ILLINOIS POLLUTION CONTROL BOARD
May 18, 2000
IN THE MATTER OF:
)
)
RCRA SUBTITLE C UPDATE, USEPA
)
R00-13
AMENDMENTS (July 1, 1999, through
)
(Identical-in-Substance
December 31, 1999)
)
Rulemaking - Land)
Adopted Rule. Final Order.
ORDER OF THE BOARD (by E.Z. Kezelis):
Under Sections 7.2 and 22.4(a) of the Environmental Protection Act (Act) (415 ILCS
5/7.2 and 22.4(a) (1998)), the Board adopts amendments to the Illinois regulations that are
“identical in substance” to 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
.
(1998)). The nominal timeframe of this docket includes federal RCRA Subtitle C amendments
that USEPA adopted in the period July 1, 1999, through December 31, 1999.
Sections 7.2 and 22.4(a) provide for quick adoption of regulations that are identical in
substance to federal regulations that USEPA adopts to implement Sections 3001 through 3005
of RCRA (42 U.S.C. §§ 6921-6925 (1998)). Section 22.4(a) also provides that Title VII of the
Act and Section 5 of the Administrative Procedure Act (APA) (5 ILCS 100/5-35 and 5-40
(1998)) do not apply to the Board’s adoption of identical-in-substance regulations. The federal
RCRA Subtitle C regulations are found at 40 C.F.R. 260 through 266, 268, 270, 271, 273,
and 279.
This order is supported by an opinion that the Board also adopts today. The Board will
wait 30 days for USEPA to review the amendments, as provided in the agreement between
USEPA and the State of Illinois relating to federal authorization of the State program
, in order to
allow USEPA an additional opportunity to review the amendments before they become effective
. We
will then file the amendments with the Secretary of State and submit Notices of Adopted
Amendments for publication in the
Illinois Register
. The complete text of the adopted
amendments follows.
2
IT IS SO ORDERED.
I, Dorothy M. Gunn, Clerk of the Illinois Pollution Control Board, do hereby certify
that the above order was adopted on the 18th day of May 2000 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
SUBPART D: APPLICATIONS
Section
703.180
Applications in General
4
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
703.221 Emergency Permits
703.220 Emergency Permits
703.221 Alternative Compliance with the Federal NESHAPS
703.222
Incinerator Conditions Prior to Trial Burn
703.223
Incinerator Conditions During Trial Burn
703.224
Incinerator Conditions After Trial Burn
703.225
Trial Burns for Existing Incinerators
703.230
Land Treatment Demonstration
703.231
Research, Development and Demonstration Permits
703.232
Permits for Boilers and Industrial Furnaces Burning Hazardous Waste
703.234
Remedial Action Plans
SUBPART F: PERMIT CONDITIONS OR DENIAL
Section
703.240
Permit Denial
703.241
Establishing Permit Conditions
5
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
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
6
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.
________, effective ______________________.
SUBPART B: PROHIBITIONS
Section 703.123
Specific Exclusions from Permit Program
The following persons are among those who that are not required to obtain a RCRA permit:
a)
Generators who that accumulate hazardous waste on-site for less than the time
periods provided in 35 Ill. Adm. Code 722.134;
b)
Farmers who that dispose of hazardous waste pesticides from their own use as
provided in 35 Ill. Adm. Code 722.170;
c)
Persons who that own or operate facilities solely for the treatment, storage or
disposal of hazardous waste excluded from regulations under this Part by 35 Ill.
Adm. Code 721.104 or 721.105 (small generator exemption);
d)
Owners or operators of totally enclosed treatment facilities as defined in 35 Ill.
Adm. Code 720.110;
e)
Owners and operators of elementary neutralization units or wastewater treatment
units as defined in 35 Ill. Adm. Code 720.110;
f)
Transporters storing manifested shipments of hazardous waste in containers
meeting the requirements of 35 Ill. Adm. Code 722.130 at a transfer facility for
a period of ten days or less;
g)
Persons adding absorbent material to waste in a container (as defined in 35 Ill.
7
Adm. Code 720.110) and persons adding waste to absorbent material in a
container, provided that these actions occur at the time waste is first placed in the
container; and 35 Ill. Adm. Code 724.117(b), 724.271 and 724.272 are
complied with; and
h)
A universal waste handler or universal waste transporter (as defined in 35 Ill.
Adm. Code 720.110) that manages the wastes listed below. Such a handler or
transporter is subject to regulation under 35 Ill. Adm. Code 733.
1)
Batteries, as described in 35 Ill. Adm. Code 733.102;
2)
Pesticides, as described in 35 Ill. Adm. Code 733.103;
3)
Thermostats, as described in 35 Ill. Adm. Code 733.104; and
4)
Mercury-containing lampsLamps, as described in 35 Ill. Adm. Code
733.107 733.105.
BOARD NOTE: Derived from 40 CFR 270.1(c)(2) (1996) (1999), as amended at 64 Fed.
Reg. 36488 (July 6, 1999). Subsection (h)(4) of this Section was added pursuant to Section
22.23a of the Act [415 ILCS 5/22.23a] (see P.A. 90-502, effective August 19, 1997).
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
SUBPART C: AUTHORIZATION BY RULE AND INTERIM STATUS
Section 703.161
Enforceable Document for Post-Closure Care
a)
An owner or operator may obtain an enforceable document containing alternative
requirements for post-closure care that imposes the requirements of 35 Ill. Adm.
Code 725.221. “Enforceable document containing alternative requirements” or
“other enforceable document,” as used in this Part and in 35 Ill. Adm. Code 724
and 725, means an order of the Board, an Agency-approved plan, or an order of
a court of competent jurisdiction that meets the requirements of subsection (b) of
this Section. An “enforceable document containing alternative requirements” or
“other enforceable document,” may also mean an order of USEPA (such as
pursuant to section 3008(h) of RCRA, 42 USC 6928(h), or under section 106 of
the federal Comprehensive Environmental Response, Compensation and Liability
Act, 42 USC 9606).
BOARD NOTE: Derived from 40 CFR 270.1(c)(7), as added at 63 Fed. Reg.
56735 (Oct. 22, 1998) (1999).
8
b)
Any alternative requirements issued under this Section or established to satisfy
the requirements of 35 Ill. Adm. Code 724.190(f), 724.210(c), 724.240(d),
725.190(f), 725.210(c), or 725.240(d) shall be embodied in a document that is
enforceable and subject to appropriate compliance orders and civil penalties
under Titles VIII and XII of the Act.
BOARD NOTE: Derived from 40 CFR 271.16(e), as added at 63 Fed. Reg.
56735 (Oct. 22, 1998) (1999).
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
SUBPART D: APPLICATIONS
Section 703.183
General Information
The following information is required in the Part B application for all HWM facilities, except as
35 Ill. Adm. Code 724.101 provides otherwise:
a)
A general description of the facility;
b)
Chemical and physical analyses of the hazardous wastes and hazardous debris to
be handled at the facility. At a minimum, these analyses must contain all the
information which must be known to treat, store, or dispose of the wastes
properly in accordance with 35 Ill. Adm. Code 724;
c)
A copy of the waste analysis plan required by 35 Ill. Adm. Code 724.113(b)
and, if applicable, 35 Ill. Adm. Code 724.113(c);
d)
A description of the security procedures and equipment required by 35 Ill. Adm.
Code 724.114, or a justification demonstrating the reasons for requesting a
waiver of this requirement;
e)
A copy of the general inspection schedule required by 35 Ill. Adm. Code
724.115(b). Include where applicable, as part of the inspection schedule,
specific requirements in 35 Ill. Adm. Code 724.274, 724.293(i), 724.295,
724.326, 724.354, 724.373, 724.403, 724.702, 724.933, 724.952, 724.953,
724.958, 724.984, 724.985, 724.986, and 724.988;
f)
A justification of any request for a waiver of the preparedness and prevention
requirements of 35 Ill. Adm. Code 724.Subpart C;
g)
A copy of the contingency plan required by 35 Ill. Adm. Code 724.Subpart D;
9
BOARD NOTE: Include, where applicable, as part of the contingency plan,
specific requirements in 35 Ill. Adm. Code 724.200 and 724.327.
Corresponding 40 CFR 270.14(b)(7) refers to the requirements of 40 CFR
264.255 (corresponding with 35 Ill. Adm. Code 724.355), marked “reserved”
by USEPA.
h)
A description of procedures, structures, or equipment used at the facility to:
1)
Prevent hazards in unloading operations (for example, ramps, or special
forklifts);
2)
Prevent runoff from hazardous waste handling areas to other areas of the
facility or environment, or to prevent flooding (for example, berms,
dikes, or trenches);
3)
Prevent contamination of water supplies;
4)
Mitigate effects of equipment failure and power outages;
5)
Prevent undue exposure of personnel to hazardous waste (for example,
protective clothing); and
6)
Prevent releases to the atmosphere;
i)
A description of precautions to prevent accidental ignition or reaction of
ignitable, reactive, or incompatible wastes, as required to demonstrate
compliance with 35 Ill. Adm. Code 724.117, including documentation
demonstrating compliance with 35 Ill. Adm. Code 724.117(c);
j)
Traffic A description of the area traffic pattern, the estimated traffic volume
(number and types of vehicles), and area traffic control (for example, show turns
across traffic lanes and stacking lanes, if appropriate); describe a description of
access road surfacing and load bearing capacity; and show the locations and
types of traffic control signals;
k)
Facility location information, as required by Section 703.184;
l)
An outline of both the introductory and continuing training programs by the
owner or operator to prepare persons to operate or maintain the HWM facility in
a safe manner, as required to demonstrate compliance with 35 Ill. Adm. Code
724.116. A brief description of how training will be designed to meet actual job
tasks in accordance with requirements in 35 Ill. Adm. Code 724.116(a)(3);
m)
A copy of the closure plan and, where applicable, the post-closure plan required
by 35 Ill. Adm. Code 724.212, 724.218, and 724.297. Include, where
10
applicable, as part of the plans, specific requirements in 35 Ill. Adm. Code
724.278, 724.297, 724.328, 724.358, 724.380, 724.410, 724.451, 724.701, and
724.703;
n)
For hazardous waste disposal units that have been closed, documentation that
notices required under 35 Ill. Adm. Code 724.219 have been filed;
o)
The most recent closure cost estimate for the facility, prepared in accordance
with 35 Ill. Adm. Code 724.242, and a copy of the documentation required to
demonstrate financial assurance under 35 Ill. Adm. Code 724.243. For a new
facility, a copy of the required documentation may be submitted 60 days prior to
the initial receipt of hazardous wastes, if it is later than the submission of the Part
B permit application;
p)
Where applicable, the most recent post-closure cost estimate for the facility,
prepared in accordance with 35 Ill. Adm. Code 724.244, plus a copy of the
documentation required to demonstrate financial assurance under 35 Ill. Adm.
Code 724.245. For a new facility, a copy of the required documentation may be
submitted 60 days prior to the initial receipt of hazardous wastes, if it is later
than the submission of the Part B permit application;
q)
Where applicable, a copy of the insurance policy or other documentation which
comprises compliance with the requirements of 35 Ill. Adm. Code 724.247. For
a new facility, documentation showing the amount of insurance meeting the
specification of 35 Ill. Adm. Code 724.247(a) and, if applicable, 35 Ill. Adm.
Code 724.247(b) that the owner or operator plans to have in effect before initial
receipt of hazardous waste for treatment, storage, or disposal. A request for an
alternative level of required coverage for a new or existing facility may be
submitted as specified in 35 Ill. Adm. Code 724.247(c);
r)
This subsection corresponds with 40 CFR 270.14(b)(18), pertaining to state
financial mechanisms that do not apply in Illinois. This statement maintains
structural parity with the federal regulations.
s)
A topographic map showing a distance of 1000 feet around the facility at a scale
of 2.5 centimeters (1 inch) equal to not more than 61.0 meters (200 feet).
Contours must be shown on the map. The contour interval must be sufficient to
clearly show the pattern of surface water flow in the vicinity of and from each
operational unit of the facility. For example, contours with an interval of 1.5
meters (5 feet), if relief is greater than 6.1 meters (20 feet), or an interval of 0.6
meters (2 feet), if relief is less than 6.1 meters (20 feet). Owners and operators
of HWM facilities located in mountainous areas shall use larger contour intervals
to adequately show topographic profiles of facilities. The map must clearly show
the following:
11
1)
Map scale and date;
2)
100-year floodplain area;
3)
Surface waters including intermittent streams;
4)
Surrounding land uses (e.g., residential, commercial, agricultural,
recreational, etc.);
5)
A wind rose (i.e., prevailing windspeed and direction);
6)
Orientation of the map (north arrow);
7)
Legal boundaries of the HWM facility site;
8)
Access control (e.g., fences, gates, etc.);
9)
Injection and withdrawal wells both on-site and off-site;
10)
Buildings; treatment, storage, or disposal operations; or other structures
(e.g., recreation areas, runoff control systems, access and internal roads,
storm, sanitary and process sewage systems, loading and unloading areas,
fire control facilities, etc.);
11)
Barriers for drainage or flood control;
12)
Location of operational units within the HWM facility site, where
hazardous waste is (or will be) treated, stored, or disposed of (include
equipment cleanup areas);
BOARD NOTE: For large HWM facilities, the Agency shall allow the use of
other scales on a case by case case-by-case basis.
t)
Applicants shall submit such information as the Agency determines is necessary
for it to determine whether to issue a permit and what conditions to impose in
any permit issued;
u)
For land disposal facilities, if a case-by-case extension has been approved under
35 Ill. Adm. Code 728.105 or if a petition has been approved under 35 Ill.
Adm. Code 728.106, a copy of the notice of approval of the extension or of
approval of the petition is required; and
v)
A summary of the pre-application meeting, along with a list of attendees and
their addresses, and copies of any written comments or materials submitted at the
meeting, as required under 35 Ill. Adm. Code 703.191(c).
12
BOARD NOTE: Derived from 40 CFR 270.14(b) (1998) (1999).
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
Section 703.205
Incinerators that Burn Hazardous Waste
For facilities that incinerate hazardous waste, except as 35 Ill. Adm. Code 724.440 provides
and subsection (e) of this Section provide otherwise, the applicant must fulfill the requirements
of subsections subsection (a), (b), or (c) below of this Section in completing the Part B
application:
a)
When seeking exemption under 35 Ill. Adm. Code 724.440(b) or (c) (ignitable,
corrosive, or reactive wastes only):
1)
Documentation that the waste is listed as a hazardous waste in 35 Ill.
Adm. Code 721.Subpart D solely because it is ignitable (Hazard Code I),
corrosive (Hazard Code C), or both; or
2)
Documentation that the waste is listed as a hazardous waste in 35 Ill.
Adm. Code 721.Subpart D solely because it is reactive (Hazard Code R)
for characteristics other than those listed in 35 Ill. Adm. Code
721.123(a)(4) and (a)(5) and will not be burned when other hazardous
wastes are present in the combustion zone; or
3)
Documentation that the waste is a hazardous waste solely because it
possesses the characteristic of ignitability or corrosivity, or both, as
determined by the tests for characteristics of hazardous wastes under 35
Ill. Adm. Code 721.Subpart C; or
4)
Documentation that the waste is a hazardous waste solely because it
possesses the reactivity characteristics listed in 35 Ill. Adm. Code
721.123(a)(1) through (a)(3) or (a)(6) through (a)(8) and that it will not be
burned when other hazardous wastes are present in the combustion zone;
or
b)
Submit a trial burn plan or the results of a trial burn, including all required
determinations, in accordance with Section 703.222 et seq.; or
13
c)
In lieu of a trial burn, the applicant may submit the following information:
1)
An analysis of each waste or mixture of wastes to be burned including:
A)
Heat value of the waste in the form and composition in which it
will be burned;
B)
Viscosity (if applicable) or description of physical form of the
waste;
C)
An identification of any hazardous organic constituents listed in 35
Ill. Adm. Code 721.Appendix H that are present in the waste to
be burned, except that the applicant need not analyze for
constituents listed in 35 Ill. Adm. Code 721.Appendix H that
would reasonably not be expected to be found in the waste. The
constituents excluded from analysis must be identified and the
basis for their exclusion stated. The waste analysis must rely on
analytical techniques specified in “Test Methods for the Evaluation
of Solid Waste, Physical/Chemical Methods”, U.S. EPA USEPA
Publication SW-846, as incorporated by reference at 35 Ill. Adm.
Code 720.111 and Section 703.110, or their equivalent;
D)
An approximate quantification of the hazardous constituents
identified in the waste, within the precision produced by the
analytical methods specified in “Test Methods for the Evaluation
of Solid Waste, Physical/Chemical Methods”, U.S. EPA USEPA
Publication SW-846, as incorporated by reference at 35 Ill. Adm.
Code 720.111 and Section 703.110; and
E)
A quantification of those hazardous constituents in the waste that
may be designated as POHCs based on data submitted from other
trial or operational burns that demonstrate compliance with the
performance standard in 35 Ill. Adm. Code 724.443;
2)
A detailed engineering description of the incinerator, including:
14
A)
Manufacturer’s name and model number of incinerator;
B)
Type of incinerator;
C)
Linear dimension of incinerator unit including cross sectional area
of combustion chamber;
D)
Description of auxiliary fuel system (type/feed);
E)
Capacity of prime mover;
F)
Description of automatic waste feed cutoff system(s) systems;
G)
Stack gas monitoring and pollution control monitoring system;
H)
Nozzle and burner design;
I)
Construction materials; and
J)
Location and description of temperature, pressure and flow
indicating devices and control devices;
3)
A description and analysis of the waste to be burned compared with the
waste for which data from operational or trial burns are provided to
support the contention that a trial burn is not needed. The data should
include those items listed in subsection (c)(1) above of this Section. This
analysis should specify the POHCs that the applicant has identified in the
waste for which a permit is sought, and any differences from the POHCs
in the waste for which burn data are provided;
4)
The design and operating conditions of the incinerator unit to be used,
compared with that for which comparative burn data are available;
5)
A description of the results submitted from any previously conducted trial
burn(s) burns including:
A)
Sampling and analysis techniques used to calculate performance
15
standards in 35 Ill. Adm. Code 724.443;
B)
Methods and results of monitoring temperatures, waste feed rates,
carbon monoxide and an appropriate indicator of combustion gas
velocity (including a statement concerning the precision and
accuracy of this measurement); and
C)
The certification and results required by subsection (b) above of
this Section;
6)
The expected incinerator operation information to demonstrate compliance
with 35 Ill. Adm. Code 724.443 and 724.445 including:
A)
Expected carbon monoxide (CO) level in the stack exhaust gas;
B)
Waste feed rate;
C)
Combustion zone temperature;
D)
Indication of combustion gas velocity;
E)
Expected stack gas volume, flow rate, and temperature;
F)
Computed residence time for waste in the combustion zone;
G)
Expected hydrochloric acid removal efficiency;
H)
Expected fugitive emissions and their control procedures; and
I)
Proposed waste feed cut-off limits based on the identified
significant operating parameters;
7)
The Agency may, pursuant to 35 Ill. Adm. Code 705.122, request such
additional information as may be necessary for the Agency to determine
whether the incinerator meets the requirements of 35 Ill. Adm. Code
724.Subpart 0 and what conditions are required by that Subpart and
Section 39(d) of the Environmental Protection Act; and
16
8)
Waste analysis data, including that submitted in subsection (c)(1) above of
this Section, sufficient to allow the Agency to specify as permit Principal
Organic Hazardous Constituents (permit POHCs) those constituents for
which destruction and removal efficiencies will be required;.
d)
The Agency shall approve a permit application without a trial burn if it finds
that:
1)
The wastes are sufficiently similar; and
2)
The incinerator units are sufficiently similar, and the data from other trial
burns are adequate to specify (under 35 Ill. Adm. Code 724.445)
operating conditions that will ensure that the performance standards in 35
Ill. Adm. Code 724.443 will be met by the incinerator.
e) When an owner or operator demonstrates compliance with the air emission
standards and limitations of the federal National Emission Standards for
Hazardous Air Pollutants (NESHAPs) in 40 CFR 63, subpart EEE, incorporated
by reference in 35 Ill. Adm. Code 720.111 (i.e., by conducting a comprehensive
performance test and submitting a Notification of Compliance), the requirements
of this Section do not apply. Nevertheless, the Agency may apply the provisions
of this Section, on a case-by-case basis, for purposes of information collection in
accordance with Sections 703.188 and 703.241(a)(2).
BOARD NOTE: Derived from 40 CFR 270.19 (1992) (1999), as amended at 58 64 Fed. Reg.
46051 (Aug. 31, 1993) 53076 (September 30, 1999).
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
Section 703.208
Boilers and Industrial Furnaces Burning Hazardous Waste
When an owner or operator of a cement or lightweight aggregate kiln demonstrates compliance
with the air emission standards and limitations of the federal National Emission Standards for
Hazardous Air Pollutants (NESHAPs) in 40 CFR 63, subpart EEE, incorporated by reference
in 35 Ill. Adm. Code 720.111 (i.e., by conducting a comprehensive performance test and
submitting a Notification of Compliance), the requirements of this Section do not apply.
Nevertheless, the Agency may apply the provisions of this Section, on a case-by-case basis, for
purposes of information collection in accordance with Sections 703.188 and 703.241(a)(2).
17
a)
Trial burns.
1)
General. Except as provided below, owners and operators that are
subject to the standards to control organic emissions provided by 35 Ill.
Adm. Code 726.204, standards to control particulate matter provided by
35 Ill. Adm. Code 726.205, standards to control metals emissions
provided by 35 Ill. Adm. Code 726.206, or standards to control
hydrogen chloride (HCl) or chlorine gas emissions provided by 35 Ill.
Adm. Code 726.207 shall conduct a trial burn to demonstrate
conformance with those standards and shall submit a trial burn plan or the
results of a trial burn, including all required determinations, in
accordance with Section 703.232.
A)
Under subsection subsections (a)(2) through (a)(5) below of this
Section and 35 Ill. Adm. Code 726.204 through 726.207, the
Agency may waive a trial burn to demonstrate conformance with
a particular emission standard; and
B)
The owner or operator may submit data in lieu of a trial burn, as
prescribed in subsection (a)(6) below of this Section.
2)
Waiver of trial burn of DRE (destruction removal efficiency).
A)
Boilers operated under special operating requirements. When
seeking to be permitted under 35 Ill. Adm. Code 726.204(a)(4)
and 726.210, which automatically waive the DRE trial burn, the
owner or operator of a boiler shall submit documentation that the
boiler operates under the special operating requirements provided
by 35 Ill. Adm. Code 726.210.
B)
Boilers and industrial furnaces burning low risk waste. When
seeking to be permitted under the provisions for low risk waste
provided by 35 Ill. Adm. Code 726.204(a)(5) and 726.209(a),
which waive the DRE trial burn, the owner or operator shall
submit:
18
i)
Documentation that the device is operated in conformance
with the requirements of 35 Ill. Adm. Code 726.209(a)(1).
ii)
Results of analyses of each waste to be burned,
documenting the concentrations of nonmetal compounds
listed in 35 Ill. Adm. Code 721.Appendix H, except for
those constituents that would reasonably not be expected to
be in the waste. The constituents excluded from analysis
must be identified and the basis for their exclusion
explained. The analysis must rely on analytical techniques
specified in Test Methods for the Evaluation of Solid
Waste, Physical/Chemical Methods, (incorporated by
reference, see in 35 Ill. Adm. Code 720.111).
iii)
Documentation of hazardous waste firing rates and
calculations of reasonable, worst-case emission rates of
each constituent identified in subsection (a)(2)(B)(ii) above
of this Section using procedures provided by 35 Ill. Adm.
Code 726.209(a)(2)(B).
iv)
Results of emissions dispersion modeling for emissions
identified in subsection (a)(2)(B)(iii) above of this Section
using modeling procedures prescribed by 35 Ill. Adm.
Code 726.206(h). The Agency shall review the emission
modeling conducted by the applicant to determine
conformance with these procedures. The Agency shall
either approve the modeling or determine that alternate or
supplementary modeling is appropriate.
v)
Documentation that the maximum annual average ground
level concentration of each constituent identified in
subsection (a)(2)(B)(ii) above of this Section quantified in
conformance with subsection (a)(2)(B)(iv) above of this
Section does not exceed the allowable ambient level
established in 35 Ill. Adm. Code 726.Appendix D or E.
The acceptable ambient concentration for emitted
constituents for which a specific reference air
19
concentration has not been established in 35 Ill. Adm.
Code 726.Appendix D or risk-specific does doses has not
been established in 35 Ill. Adm. Code 726.Appendix E is
0.1 micrograms per cubic meter, as noted in the footnote
to 35 Ill. Adm. Code 726.Appendix D.
3)
Waiver of trial burn for metals. When seeking to be permitted under the
Tier I (or adjusted Tier I) metals feed rate screening limits provided by 35
Ill. Adm. Code 726.206(b) and (e) that control metals emissions without
requiring a trial burn, the owner or operator shall submit:
A)
Documentation of the feed rate of hazardous waste, other fuels,
and industrial furnace feed stocks;
B)
Documentation of the concentration of each metal controlled by 35
Ill. Adm. Code 726.206(b) or (c) in the hazardous waste, other
fuels and industrial furnace feedstocks, and calculations of the total
feed rate of each metal;
C)
Documentation of how the applicant will ensure that the Tier I
feed rate screening limits provided by 35 Ill. Adm. Code
726.206(b) or (e) will not be exceeded during the averaging
period provided by that subsection;
D)
Documentation to support the determination of the TESH (terrain-
adjusted effective stack height), good engineering practice stack
height, terrain type, and land use as provided by 35 Ill. Adm.
Code 726.206(b)(3) through (5);
E)
Documentation of compliance with the provisions of 35 Ill. Adm.
Code 726.206(b)(6), if applicable, for facilities with multiple
stacks;
F)
Documentation that the facility does not fail the criteria provided
by 35 Ill. Adm. Code 726.206(b)(7) for eligibility to comply with
the screening limits; and
20
G)
Proposed sampling and metals analysis plan for the hazardous
waste, other fuels, and industrial furnace feed stocks.
4)
Waiver of trial burn for PM (particulate matter). When seeking to be
permitted under the low risk waste provisions of 35 Ill. Adm. Code
726.209(b), which waives the particulate standard (and trial burn to
demonstrate conformance with the particulate standard), applicants shall
submit documentation supporting conformance with subsections (a)(2)(B)
and (a)(3) above of this Section.
5)
Waiver of trial burn for HCl and chlorine gas. When seeking to be
permitted under the Tier I (or adjusted Tier I) feed rate screening limits
for total chlorine and chloride provided by 35 Ill. Adm. Code
726.207(b)(1) and (e) that control emissions by of HCl and chlorine gas
without requiring a trial burn, the owner or operator shall submit:
A)
Documentation of the feed rate of hazardous waste, other fuels,
and industrial furnace feed stocks;
B)
Documentation of the levels of total chlorine and chloride in the
hazardous waste, other fuels and industrial furnace feedstocks,
and calculations of the total feed rate of total chlorine and
chloride;
C)
Documentation of how the applicant will ensure that the Tier I (or
adjusted Tier I) feed rate screening limits provided by 35 Ill.
Adm. Code 726.207(b)(1) or (e) will not be exceeded during the
averaging period provided by that subsection;
D)
Documentation to support the determination of the TESH, good
engineering practice stack height, terrain type and land use as
provided by 35 Ill. Adm. Code 726.207(b)(3);
E)
Documentation of compliance with the provisions of 35 Ill. Adm.
Code 726.207(b)(4), if applicable, for facilities with multiple
stacks;
21
F)
Documentation that the facility does not fail the criteria provided
by 35 Ill. Adm. Code 726.207(b)(3) for eligibility to comply with
the screening limits; and
G)
Proposed sampling and analysis plan for total chlorine and
chloride for the hazardous waste, other fuels, and industrial
furnace feedstocks.
6)
Data in lieu of trial burn. The owner or operator may seek an exemption
from the trial burn requirements to demonstrate conformance with Section
703.232 and 35 Ill. Adm. Code 726.204 through 726.207 by providing
the information required by Section 703.232 from previous compliance
testing of the device in conformance with 35 Ill. Adm. Code 726.203 or
from compliance testing or trial or operational burns of similar boilers or
industrial furnaces burning similar hazardous wastes under similar
conditions. If data from a similar device is used to support a trial burn
waiver, the design and operating information required by Section
703.232 from previous compliance testing of the device in conformance
with 35 Ill. Adm. Code 726.203, or from compliance testing or trial or
operational burns of similar boilers or industrial furnaces burning similar
hazardous wastes under similar conditions. If data from a similar device
is used to support a trial burn waiver, the design and operating
information required by Section 703.232 must be provided for both the
similar device and the device to which the data is to be applied, and a
comparison of the design and operating information must be provided.
The Agency shall approve a permit application without a trial burn if the
Agency finds that the hazardous wastes are sufficiently similar, the
devices are sufficiently similar, the operating conditions are sufficiently
similar, and the data from other compliance tests, trial burns, or
operational burns are adequate to specify (under 35 Ill. Adm. Code
726.102) operating conditions that will ensure conformance with 35 Ill.
Adm. Code 726.102(c). In addition, the following information shall be
submitted:
A)
For a waiver from any trial burn:
i)
A description and analysis of the hazardous waste to be
22
burned compared with the hazardous waste for which data
from compliance testing or operational or trial burns are
provided to support the contention that a trial burn is not
needed;
ii)
The design and operating conditions of the boiler or
industrial furnace to be used, compared with that for
which comparative burn data are available; and
iii)
Such supplemental information as the Agency finds
necessary to achieve the purposes of this subsection (a).
B)
For a waiver of the DRE trial burn, the basis for selection of
POHCs (principal organic hazardous constituents) used in the
other trial or operational burns which demonstrate compliance
with the DRE performance standard in 35 Ill. Adm. Code
726.204(a). This analysis should specify the constituents in 35 Ill.
Adm. Code 721.Appendix H that the applicant has identified in
the hazardous waste for which a permit is sought and any
differences from the POHCs in the hazardous waste for which
burn data are provided.
b)
Alternative HC limit for industrial furnaces with organic matter in raw materials.
Owners and operators of industrial furnaces requesting an alternative HC limit
under 35 Ill. Adm. Code 726.204(f) shall submit the following information at a
minimum:
1)
Documentation that the furnace is designed and operated to minimize HC
emissions from fuels and raw materials;
2)
Documentation of the proposed baseline flue gas HC (and CO)
concentration, including data on HC (and CO) levels during tests when
the facility produced normal products under normal operating conditions
from normal raw materials while burning normal fuels and when not
burning hazardous waste;
3)
Test burn protocol to confirm the baseline HC (and CO) level including
23
information on the type and flow rate of all feedstreams, point of
introduction of all feedstreams, total organic carbon content (or other
appropriate measure of organic content) of all nonfuel feedstreams, and
operating conditions that affect combustion of fuel(s) fuels and destruction
of hydrocarbon emissions from nonfuel sources;
4)
Trial burn plan to:
A)
Demonstrate that flue gas HC (and CO) concentrations when
burning hazardous waste do not exceed the baseline HC (and CO)
level; and
B)
Identify, in conformance with Section 703.232(d), the types and
concentrations of organic compounds listed in 35 Ill. Adm. Code
721.Appendix H that are emitted when burning hazardous waste;
5)
Implementation plan to monitor over time changes in the operation of the
facility that could reduce the baseline HC level and procedures to
periodically confirm the baseline HC level; and
6)
Such other information as the Agency finds necessary to achieve the
purposes of this subsection (b).
c)
Alternative metals implementation approach. When seeking to be permitted
under an alternative metals implementation approach under 35 Ill. Adm. Code
726.206(f), the owner or operator shall submit documentation specifying how the
approach ensures compliance with the metals emissions standards of 35 Ill. Adm.
Code 726.106(c) or (d) and how the approach can be effectively implemented
and monitored. Further, the owner or operator shall provide such other
information that the Agency finds necessary to achieve the purposes of this
subsection (c).
d)
Automatic waste feed cutoff system. Owners and operators shall submit
information describing the automatic waste feed cutoff system, including any pre-
alarm systems that may be used.
e)
Direct transfer. Owners and operators that use direct transfer operations to feed
24
hazardous waste from transport vehicles (containers, as defined in 35 Ill. Adm.
Code 726.211) directly to the boiler or industrial furnace shall submit
information supporting conformance with the standards for direct transfer
provided by 35 Ill. Adm. Code 726.211.
f)
Residues. Owners and operators that claim that their residues are excluded from
regulation under the provisions of 35 Ill. Adm. Code 726.212 shall submit
information adequate to demonstrate conformance with those provisions.
BOARD NOTE: Derived from 40 CFR 270.22 (1992) (1999), as amended at 64 Fed. Reg.
53077 (September 30, 1999).
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
SUBPART E: SHORT TERM AND PHASED PERMITS
Section 703.221 Emergency Permits
Section 703.220 Emergency Permits
a)
Notwithstanding any other provision of this Part or 35 Ill. Adm. Code 702 or
705, in the event that the Agency finds an imminent and substantial
endangerment to human health or the environment the Agency may issue a
temporary emergency permit:
1)
To a non-permitted facility to allow treatment, storage or disposal of
hazardous waste; or
2)
To a permitted facility to allow treatment, storage or disposal of a
hazardous waste not covered by an effective permit.
b)
This emergency permit must comply with all of the following requirements:
1)
May be oral or written. If oral, it must be followed in five days by a
written emergency permit;.
2)
Shall not exceed 90 days in duration;.
3)
Shall clearly specify the hazardous wastes to be received and the manner
and location of their treatment, storage or disposal;.
4)
May be terminated by the Agency at any time without process if it
25
determines that termination is appropriate to protect human health and the
environment;.
5)
Shall be accompanied by a public notice published under 35 Ill. Adm.
Code 705.162 including:
A)
Name and address of the office granting the emergency
authorization;
B)
Name and location of the permitted HWM facility;
C)
A brief description of the wastes involved;
D)
A brief description of the action authorized and reasons for
authorizing it; and
E)
Duration of the emergency permit; and.
6)
Shall incorporate, to the extent possible and not inconsistent with the
emergency situation, all applicable requirements of this Part and 35 Ill.
Adm. Code 724.
7)
Emergency permits which that would authorize actions not in compliance
with Board rules, other than procedural requirements, require a variance
or provisional variance pursuant to Title IX of the Environmental
Protection Act and 35 Ill. Adm. Code 104.
BOARD NOTE: Derived from 40 CFR 270.61 (1996) (1999).
(Source: Section 703.221 renumbered to Section 703.220 and amended at 24 Ill. Reg.
________, effective ______________________)
Section 703.221 Alternative Compliance with the Federal NESHAPS
When an owner or operator demonstrates compliance with the air emission standards and
limitations of the federal National Emission Standards for Hazardous Air Pollutants (NESHAPs)
in 40 CFR 63, subpart EEE, incorporated by reference in 35 Ill. Adm. Code 720.111 (i.e., by
conducting a comprehensive performance test and submitting a Notification of Compliance), the
requirements of Sections 703.221 through 703.225 do not apply. Nevertheless, the Agency
may apply the provisions of Sections 703.221 through 703.225, on a case-by-case basis, for
purposes of information collection in accordance with Sections 703.188 and 703.241(a)(2).
BOARD NOTE: Derived from 40 CFR 270.62 preamble (1999), as added at 64 Fed. Reg.
53077 (September 30, 1999).
26
(Source: Old Section 703.221 renumbered to Section 703.220 and new Section 703.221 added
at 24 Ill. Reg. ________, effective ______________________)
Section 703.232
Permits for Boilers and Industrial Furnaces Burning Hazardous Waste
When an owner or operator of a cement or lightweight aggregate kiln demonstrates compliance
with the air emission standards and limitations of the federal National Emission Standards for
Hazardous Air Pollutants (NESHAPs) of in 40 CFR 63, subpart EEE, incorporated by
reference in 35 Ill. Adm. Code 720.111 (i.e., by conducting a comprehensive performance test
and submitting a Notification of Compliance), the requirements of this Section do not apply.
Nevertheless, the Agency may apply the provisions of this Section, on a case-by-case basis, for
purposes of information collection in accordance with Sections 703.188 and 703.241(a)(2).
a)
General. Owners and operators of new boilers and industrial furnaces (those not
operating under the interim status standards of 35 Ill. Adm. Code 726.203) are
subject to subsections (b) through (f) of this Section. Boilers and industrial
furnaces operating under the interim status standards of 35 Ill. Adm. Code
726.203 are subject to subsection (g) of this Section.
b)
Permit operating periods for new boilers and industrial furnaces. A permit for a
new boiler or industrial furnace must specify appropriate conditions for the
following operating periods:
1)
Pretrial burn period. For the period beginning with initial introduction of
hazardous waste and ending with initiation of the trial burn, and only for
the minimum time required to bring the boiler or industrial furnace to a
point of operation readiness to conduct a trial burn, not to exceed 720
hours operating time when burning hazardous waste, the Agency shall
establish permit conditions in the Pretrial Burn Period pretrial burn
period, including but not limited to allowable hazardous waste feed rates
and operating conditions. The Agency shall extend the duration of this
operational period once, for up to 720 additional hours, at the request of
the applicant when good cause is shown. The permit most must be
modified to reflect the extension according to Section 703.280 et seq.
A)
Applicants must submit a statement, with Part B of the permit
application, that suggests the conditions necessary to operate in
compliance with the standards of 35 Ill. Adm. Code 726.204
through 726.207 during this period. This statement should
include, at a minimum, restrictions on the applicable operating
requirements identified in 35 Ill. Adm. Code 726.202 (e).
B)
The Agency shall review this statement and any other relevant
information submitted with Part B of the permit application and
27
specify requirements for this period sufficient to meet the
performance standards of 35 Ill. Adm. Code 726.204 through
726.207 based on the Agency’s engineering judgment.
2)
Trial burn period. For the duration of the trial burn, the Agency shall
establish conditions in the permit for the purposes of determining
feasibility of compliance with the performance standards of 35 Ill. Adm.
Code 726.204 through 726.207 and determining adequate operating
conditions under 35 Ill. Adm. Code 726.202(e). Applicants shall propose
a trial burn plan, prepared under subsection (c) of this Section, to be
submitted with Part B of the permit application.
3)
Post-trial burn period.
A)
For the period immediately following completion of the trial burn,
and only for the minimum period sufficient to allow sample
analysis, data computation and submission of the trial burn results
by the applicant, and review of the trial burn results and
modification of the facility permit by the Agency to reflect the trial
burn results, the Agency shall establish the operating requirements
most likely to ensure compliance with the performance standards
of 35 Ill. Adm. Code 726.204 through 726.207 based on the
Agency’s engineering judgment.
B)
Applicants shall submit a statement, with Part B of the application,
that identifies the conditions necessary to operate during this
period in compliance with the performance standards of 35 Ill.
Adm. Code 726.204 through 726.207. This statement should
include, at a minimum, restrictions on the operating requirements
provided by 35 Ill. Adm. Code 726.202 (e).
C)
The Agency shall review this statement and any other relevant
information submitted with Part B of the permit application and
specify requirements of this period sufficient to meet the
performance standards of 35 Ill. Adm. Code 726.204 through
726.207 based on the Agency’s engineering judgment.
4)
Final permit period. For the final period of operation the Agency shall
develop operating requirements in conformance with 35 Ill. Adm. Code
726.202(e) that reflect conditions in the trial burn plan and are likely to
ensure compliance with the performance standards of 35 Ill. Adm. Code
726.204 through 726.207. Based on the trial burn results, the Agency
shall make any necessary modifications to the operating requirements to
ensure compliance with the performance standards. The permit
modification must proceed according to Section 703.280 et seq.
28
c)
Requirements for trial burn plans. The trial burn plan must include the following
information. The Agency, in reviewing the trial burn plan, shall evaluate the
sufficiency of the information provided and may require the applicant to
supplement this information, if necessary, to achieve the purposes of this
subsection (c).
1)
An analysis of each feed stream, including hazardous waste, other fuels,
and industrial furnace feed stocks, as fired, that includes:
A)
Heating value, levels of antimony, arsenic, barium, beryllium,
cadmium, chromium, lead, mercury, silver, thallium, total
chlorine/chloride, and ash; and
B)
Viscosity or description of the physical form of the feed stream.
2)
An analysis of each hazardous waste, as fired, including:
A)
An identification of any hazardous organic constituents listed in 35
Ill. Adm. Code 721.Appendix H that are present in the feed
stream, except that the applicant need not analyze for constituents
listed in 721.Appendix H that would reasonably not be expected
to be found in the hazardous waste. The constituents excluded
from analysis must be identified and the basis for this exclusion
explained. The analysis must be conducted in accordance with
analytical techniques specified in “Test Methods for the Evaluation
of Solid Waste, Physical/Chemical Methods”, USEPA Publication
SW-846, as incorporated by reference at 35 Ill. Adm. Code
720.111 and Section 703.110, or their equivalent.;
B)
An approximate quantification of the hazardous constituents
identified in the hazardous waste, within the precision produced
by the analytical methods specified in “Test Methods for the
Evaluation of Solid Waste, Physical/Chemical Methods”, USEPA
Publication SW-846, as incorporated by reference at 35 Ill. Adm.
Code 720.111 and Section 703.110, or other equivalent.; and
C)
A description of blending procedures, if applicable, prior to firing
the hazardous waste, including a detailed analysis of the hazardous
waste prior to blending, an analysis of the material with which the
hazardous waste is blended, and blending ratios.
3)
A detailed engineering description of the boiler or industrial furnace,
including:
29
A)
Manufacturer’s name and model number of the boiler or industrial
furnace;
B)
Type of boiler or industrial furnace;
C)
Maximum design capacity in appropriate units;
D)
Description of the feed system for the hazardous waste and, as
appropriate, other fuels and industrial furnace feedstocks;
E)
Capacity of hazardous waste feed system;
F)
Description of automatic hazardous waste feed cutoff system(s)
systems;
G)
Description of any pollution control system; and
H)
Description of stack gas monitoring and any pollution control
monitoring systems.
4)
A detailed description of sampling and monitoring procedures, including
sampling and monitoring locations in the system, the equipment to be
used, sampling and monitoring frequency, and sample analysis.
5)
A detailed test schedule for each hazardous waste for which the trial burn
is planned, including date(s) dates, duration, quantity of hazardous waste
to be burned, and other factors relevant to the Agency’s decision under
subsection (b)(2) of this Section.
6)
A detailed test protocol, including, for each hazardous waste identified,
the ranges of hazardous waste feed rate, and, as appropriate, the feed
rates of other fuels and industrial furnace feedstocks, and any other
relevant parameters that may affect the ability of the boiler or industrial
furnace to meet the performance standards in 35 Ill. Adm. Code 726.204
through 726.207.
7)
A description of and planned operating conditions for any emission
control equipment that will be used.
8)
Procedures for rapidly stopping the hazardous waste feed and controlling
emissions in the event of an equipment malfunction.
9)
Such other information as the Agency finds necessary to determine
whether to approve the trial burn plan in light of the purposes of this
subsection (c) and the criteria in subsection (b)(2) of this Section.
30
d)
Trial burn procedures.
1)
A trial burn must be conducted to demonstrate conformance with the
standards of 35 Ill. Adm. Code 726.104 through 726.107.
2)
The Agency shall approve a trial burn plan if the Agency finds that:
A)
The trial burn is likely to determine whether the boiler or
industrial furnace can meet the performance standards of 35 Ill.
Adm. Code 726.104 through 726.107;
B)
The trial burn itself will not present an imminent hazard to human
health and the environment;
C)
The trial burn will help the Agency to determine operating
requirements to be specified under 35 Ill. Adm. Code 726.102(e);
and
D)
The information sought in the trial burn cannot reasonably be
developed through other means.
3)
The Agency shall send a notice to all persons on the facility mailing list,
as set forth in 35 Ill. Adm. Code 705.161(a), and to the appropriate units
of State and local government, as set forth in 35 Ill. Adm. Code
705.163(a)(5), announcing the scheduled commencement and completion
dates for the trial burn. The applicant may not commence the trial burn
until after the Agency has issued such notice.
A)
This notice must be mailed within a reasonable time period before
the trial burn. An additional notice is not required if the trial burn
is delayed due to circumstances beyond the control of the facility
or the Agency.
B)
This notice must contain:
i)
The name and telephone number of applicant’s contact
person;
ii)
The name and telephone number of the Agency regional
office appropriate for the facility;
iii)
The location where the approved trial burn plan and any
supporting documents can be reviewed and copied; and
31
iv)
An expected time period for commencement and
completion of the trial burn.
4)
The applicant shall submit to the Agency a certification that the trial burn
has been carried out in accordance with the approved trial burn plan, and
submit the results of all the determinations required in subsection (c) of
this Section. The Agency shall, in the trial burn plan, require that the
submission be made within 90 days after completion of the trial burn, or
later if the Agency determines that a later date is acceptable.
5)
All data collected during any trial burn must be submitted to the Agency
following completion of the trial burn.
6)
All submissions required by this subsection (d) must be certified on behalf
of the applicant by the signature of a person authorized to sign a permit
application or a report under 35 Ill. Adm. Code 702.126.
e)
Special procedures for DRE trial burns. When a DRE trial burn is required
under 35 Ill. Adm. Code 726.104, the Agency shall specify (based on the
hazardous waste analysis data and other information in the trial burn plan) as trial
Principal Organic Hazardous Constituents (POHCs) those compounds for which
destruction and removal efficiencies must be calculated during the trial burn.
These trial POHCs will be specified by the Agency based on information
including the Agency’s estimate of the difficulty of destroying the constituents
identified in the hazardous waste analysis, their concentrations or mass in the
hazardous waste feed, and, for hazardous waste containing or derived from
wastes listed in 35 Ill. Adm. Code 721.Subpart D, the hazardous waste organic
constituent(s) constituents identified in 35 Ill. Adm. Code 721.Appendix G as the
basis for listing.
f)
Determinations based on trial burn. During each approved trial burn (or as soon
after the burn as is practicable), the applicant shall make the following
determinations:
1)
A quantitative analysis of the levels of antimony, arsenic, barium,
beryllium, cadmium, chromium, lead, mercury, thallium, silver, and
chlorine/chloride in the feed streams (hazardous waste, other fuels, and
industrial furnace feedstocks);
2)
When a DRE trial burn is required under 35 Ill. Adm. Code 726.204(a):
A)
A quantitative analysis of the trial POHCs in the hazardous waste
feed;
B)
A quantitative analysis of the stack gas for the concentration and
32
mass emissions of the trial POHCs; and
C)
A computation of destruction and removal efficiency (DRE), in
accordance with the DRE formula specified in 35 Ill. Adm. Code
726.204(a);
3)
When a trial burn for chlorinated dioxins and furans is required under 35
Ill. Adm. Code 726.204(e), a quantitative analysis of the stack gas for the
concentration and mass emission rate of the 2,3,7,8-chlorinated tetra-
through octa-congeners of chlorinated dibenzo-p-dioxins and furans, and
a computation showing conformance with the emission standard;
4)
When a trial burn for PM, metals, or HCl/Chlorine HCl and chlorine gas
is required under 35 Ill. Adm. Code 726.205, 726.206(c) or (d), or
726.207(b)(2) or (c), a quantitative analysis of the stack gas for the
concentrations and mass emissions of PM, metals, or HCl and chlorine
gas, and computations showing conformance with the applicable emission
performance standards;
5)
When a trial burn for DRE, metals, and HCl/Chlorine HCl and chlorine
gas is required under 35 Ill. Adm. Code 726.204(a), 726.206(c) or (d),
or 726.207(b)(2) or (c), a quantitative analysis of the scrubber water (if
any), ash residues, other residues, and products for the purpose of
estimating the fate of the trial POHCs, metals, and chlorine/chloride
chlorine and chloride;
6)
An identification of sources of fugitive emissions and their means of
control;
7)
A continuous measurement of carbon monoxide (CO), oxygen, and,
where required, hydrocarbons (HC), in the stack gas; and
8)
Such other information as the Agency specifies as necessary to ensure
that the trial burn will determine compliance with the performance
standards 35 Ill. Adm. Code 726.204 through 726.207 and to establish
the operating conditions required by 35 Ill. Adm. Code 726.204 through
726.207 and of determining adequate operating conditions under 35 Ill.
Adm. Code 726.203, and to establish the operating conditions required
by 35 Ill. Adm. Code 726.202(e) as necessary to meet those performance
standards.
g)
Interim status boilers and industrial furnaces. For the purpose of determining
feasibility of compliance with the performance standards of 35 Ill. Adm. Code
726.204 through 726.207 and of determining adequate operating conditions
under 35 Ill. Adm. Code 726.203, applicants owning or operating existing
33
boilers or industrial furnaces operated under the interim status standards of 35 Ill.
Adm. Code 726.203 shall either prepare and submit a trial burn plan and
perform a trial burn in accordance with the requirements of the this Section or
submit other information as specified in Section 703.208(a)(6). The Agency
shall announce its intention to approve of the trial burn plan in accordance with
the timing and distribution requirements of subsection (d)(3) of this Section. The
contents of the notice must include all of the following information: the name
and telephone number of a contact person at the facility; the name and telephone
number of the Agency regional office appropriate for the facility; the location
where the trial burn plan and any supporting documents can be reviewed and
copied; and a schedule of the activities that are required prior to permit issuance,
including the anticipated time schedule for agency approval of the plan and the
time periods during which the trial burn would be conducted. Applicants that
submit a trial burn plan and receive approval before submission of the Part B
permit application shall complete the trial burn and submit the results specified in
subsection (f) of this Section with the Part B permit application. If completion of
this process conflicts with the date set for submission of the Part B application,
the applicant shall contact the Agency to establish a later date for submission of
the Part B application or the trial burn results. If the applicant submits a trial
burn plan with Part B of the permit application, the trial burn must be conducted
and the results submitted within a time period prior to permit issuance to be
specified by the Agency.
BOARD NOTE: Derived from 40 CFR 270.66 (1996) (1999), as amended at 64 Fed. Reg.
53077 (September 30, 1999).
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
SUBPART H: REMEDIAL ACTION PLANS
Section 703.301
General Information
a)
What is a RAP?
1)
A RAP is a special form of RCRA permit that an owner or operator may
obtain, instead of a permit issued under 35 Ill. Adm. Code 702 and this
Part, to authorize the owner or operator to treat, store, or dispose of
hazardous remediation waste (as defined in 35 Ill. Adm. Code 720.110)
at a remediation waste management site. A RAP may only be issued for
the area of contamination where the remediation wastes to be managed
under the RAP originated, or areas in close proximity to the contaminated
area, except as allowed in limited circumstances under Section 703.306.
2)
The requirements in 35 Ill. Adm. Code 702 and this Part do not apply to
34
RAPs unless those requirements for traditional RCRA permits are
specifically required under this Subpart H. The definitions in 35 Ill.
Adm. Code 702.110 apply to RAPs.
3)
Notwithstanding any other provision of 35 Ill. Adm. Code 702 or this
Part, any document that meets the requirements in this Section constitutes
a RCRA permit, as defined in 35 Ill. Adm. Code 702.110.
4)
A RAP may be either of the following:
A)
A stand-alone document that includes only the information and
conditions required by this Subpart H; or
B)
A part (or parts) of another document that includes information or
conditions for other activities at the remediation waste
management site, in addition to the information and conditions
required by this Subpart H.
5)
If an owner or operator is treating, storing, or disposing of hazardous
remediation wastes as part of a cleanup compelled by authorities issued
by USEPA or the State of Illinois, a RAP does not affect the obligations
under those authorities in any way.
6)
If an owner or operator receives a RAP at a facility operating under
interim status, the RAP does not terminate the facility’s interim status.
BOARD NOTE: Derived from 40 CFR 270.80, added at 63 Fed. Reg. 65942
(Nov. 30, 1998) (1999).
b)
When does an owner or operator need a RAP?
1)
Whenever an owner or operator treats, stores, or disposes of hazardous
remediation wastes in a manner that requires a RCRA permit under
Section 703.121, an owner or operator shall obtain either of the
following:
A)
A RCRA permit according to 35 Ill. Adm. Code 702 and this
Part; or
B)
A RAP according to this Subpart H.
2)
Treatment units that use combustion of hazardous remediation wastes at a
remediation waste management site are not eligible for RAPs under this
Subpart H.
35
3)
An owner or operator may obtain a RAP for managing hazardous
remediation waste at an already permitted RCRA facility. An owner or
operator shall have the RAP approved as a modification to the owner’s or
operator’s existing permit according to the requirements of Sections
703.270 through 703.273 or Sections 703.280 through 703.283 instead
of the requirements in this Subpart H. However, when an owner or
operator submits an application for such a modification, the information
requirements in Sections 703.281(a)(1), 703.282(a)(4), and 703.283(a)(4)
do not apply. Instead, an owner or operator shall submit the information
required under Section 703.302(d). When the owner’s or operator’s
RCRA permit is modified, the RAP becomes part of the RCRA permit.
Therefore, when the owner’s or operator’s RCRA permit (including the
RAP portion) is modified, revoked and reissued, or terminated, or when
it expires, the permit will be modified, according to the applicable
requirements in Sections 703.270 through 703.273 or 703.280 through
703.283;, it will be revoked and reissued, according to the applicable
requirements in 35 Ill. Adm. Code 702.186 and Sections 703.270
through 703.273;, or it will be terminated, according to the applicable
requirements in 35 Ill. Adm. Code 702.186, or the permit will expire,
according to the applicable requirements in 35 Ill. Adm. Code 702.125
and 702.161.
BOARD NOTE: Derived from 40 CFR 270.85, added at 63 Fed. Reg. 65942
(Nov. 30, 1998) (1999).
c)
Does a RAP grant an owner or operator any rights or relieve it of any
obligations? The provisions of 35 Ill. Adm. Code 702.181 apply to RAPs.
BOARD NOTE: Derived from 40 CFR 270.90, added at 63 Fed. Reg. 65942
(Nov. 30, 1998) (1999). The corresponding federal provision includes an
explanation that 40 CFR 270.4 provides that compliance with a permit constitutes
compliance with RCRA. This is contrary to Illinois law, under which
compliance with a permit does not constitute an absolute defense to a charge of
violation of a substantive standard other than a failure to operate in accordance
with the terms of a permit. See 35 Ill. Adm. Code 702.181(a) and
accompanying Board Note.
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
Section 703.303
Getting a RAP Approved
a)
What is the process for approving or denying an application for a RAP?
1)
If the Agency tentatively finds that an owner’s or operator’s RAP
application includes all of the information required by Section 703.302(d)
36
and that the proposed remediation waste management activities meet the
regulatory standards, the Agency shall make a tentative decision to
approve the RAP application. The Agency shall then prepare a draft
RAP and provide an opportunity for public comment before making a
final decision on the RAP application, according to this Subpart H.
2)
If the Agency tentatively finds that the owner’s or operator’s RAP
application does not include all of the information required by Section
703.302(d) or that the proposed remediation waste management activities
do not meet the regulatory standards, the Agency may request additional
information from an owner or operator or ask an owner or operator to
correct deficiencies in the owner’s or operator’s application. If an owner
or operator fails or refuses to provide any additional information the
Agency requests, or to correct any deficiencies in its RAP application,
the Agency may either make a tentative decision to deny that owner’s or
operator’s RAP application or to approve that application with certain
changes, as allowed under Section 39 of the Act [415 ILCS 5/39]. After
making this tentative decision, the Agency shall prepare a notice of intent
to deny the RAP application (“notice of intent to deny”) or to approve
that application with certain changes and provide an opportunity for
public comment before making a final decision on the RAP application,
according to the requirements in this Subpart H.
BOARD NOTE: Derived from 40 CFR 270.130, added at 63 Fed. Reg. 65943
(Nov. 30, 1998) (1999).
b)
What must the Agency include in a draft RAP? If the Agency prepares a draft
RAP, the draft must include the following information:
1)
The information required under Section 703.302(d)(1) through (d)(6);
2)
The following terms and conditions:
A)
Terms and conditions necessary to ensure that the operating
requirements specified in the RAP comply with applicable
requirements of 35 Ill. Adm. Code 724, 726, and 728 (including
any recordkeeping and reporting requirements). In satisfying this
provision, the Agency may incorporate, expressly or by
reference, applicable requirements of 35 Ill. Adm. Code 724,
726, and 728 into the RAP or establish site-specific conditions, as
required or allowed by 35 Ill. Adm. Code 724, 726, and 728;
B)
The terms and conditions in Subpart F of this Part;
C)
The terms and conditions for modifying, revoking and reissuing,
37
and terminating the RAP, as provided in Section 703.304(a); and
D)
Any additional terms or conditions that the Agency determines are
necessary to protect human health and the environment, including
any terms and conditions necessary to respond to spills and leaks
during use of any units permitted under the RAP; and
3)
If the draft RAP is part of another document, as described in Section
703.301(a)(4)(B), the Agency shall clearly identify the components of that
document that constitute the draft RAP.
BOARD NOTE: Derived from 40 CFR 270.135, added at 63 Fed. Reg. 65943
(Nov. 30, 1998) (1999).
c)
What else must the Agency prepare in addition to the draft RAP or notice of
intent to deny? Once the Agency has prepared the draft RAP or notice of intent
to deny, it shall then do the following:
1)
Prepare a statement of basis that briefly describes the derivation of the
conditions of the draft RAP and the reasons for them, or the rationale for
the notice of intent to deny;
2)
Compile an administrative record, including the following information:
A)
The RAP application, and any supporting data furnished by the
applicant;
B)
The draft RAP or notice of intent to deny;
C)
The statement of basis and all documents cited therein (material
readily available at the applicable Agency office or published
material that is generally available need not be physically included
with the rest of the record, as long as it is specifically referred to
in the statement of basis); and
D)
Any other documents that support the decision to approve or deny
the RAP; and
3)
Make information contained in the administrative record available for
review by the public upon request.
BOARD NOTE: Derived from 40 CFR 270.140, added at 63 Fed. Reg. 65943
(Nov. 30, 1998) (1999).
d)
What are the procedures for public comment on the draft RAP or notice of intent
38
to deny?
1)
The Agency shall publish notice of its intent as follows:
A)
Send notice to an owner or operator of its intention to approve or
deny the owner’s or operator’s RAP application, and send an
owner or operator a copy of the statement of basis;
B)
Publish a notice of its intention to approve or deny the owner’s or
operator’s RAP application in a major local newspaper of general
circulation;
C)
Broadcast its intention to approve or deny the owner’s or
operator’s RAP application over a local radio station; and
D)
Send a notice of its intention to approve or deny the owner’s or
operator’s RAP application to each unit of local government
having jurisdiction over the area in which the owner’s or
operator’s site is located, and to each State agency having any
authority under State law with respect to any construction or
operations at the site.
2)
The notice required by subsection (d)(1) of this Section must provide an
opportunity for the public to submit written comments on the draft RAP
or notice of intent to deny within at least 45 days.
3)
The notice required by subsection (d)(1) of this Section must include the
following information:
A)
The name and address of the Agency office processing the RAP
application;
B)
The name and address of the RAP applicant, and if different, the
remediation waste management site or activity the RAP will
regulate;
C)
A brief description of the activity the RAP will regulate;
D)
The name, address, and telephone number of a person from
whom interested persons may obtain further information,
including copies of the draft RAP or notice of intent to deny,
statement of basis, and the RAP application;
E)
A brief description of the comment procedures in this Section, and
any other procedures by which the public may participate in the
39
RAP decision;
F)
If a hearing is scheduled, the date, time, location, and purpose of
the hearing;
G)
If a hearing is not scheduled, a statement of procedures to request
a hearing;
H)
The location of the administrative record, and times when it will
be open for public inspection; and
I)
Any additional information that the Agency considers necessary or
proper.
4)
If, within the comment period, the Agency receives written notice of
opposition to its intention to approve or deny the owner’s or operator’s
RAP application and a request for a hearing, the Agency shall hold an
informal public hearing to discuss issues relating to the approval or denial
of the owner’s or operator’s RAP application. The Agency may also
determine on its own initiative that an informal hearing is appropriate.
The hearing must include an opportunity for any person to present
written or oral comments. Whenever possible, the Agency shall schedule
this hearing at a location convenient to the nearest population center to the
remediation waste management site and give notice according to the
requirements in subsection (d)(1) of this Section. This notice must, at a
minimum, include the information required by subsection (d)(3) of this
Section and the following additional information:
A)
A reference to the date of any previous public notices relating to
the RAP application;
B)
The date, time, and place of the hearing; and
C)
A brief description of the nature and purpose of the hearing,
including the applicable rules and procedures.
BOARD NOTE: Derived from 40 CFR 270.145, added at 63 Fed. Reg. 65943
(Nov. 30, 1998) (1999).
e)
How must the Agency make a final decision on a RAP application?
1)
The Agency shall consider and respond to any significant comments
raised during the public comment period or during any hearing on the
draft RAP or notice of intent to deny, and the Agency may revise the
draft RAP based on those comments, as appropriate.
40
2)
If the Agency determines that the owner’s or operator’s RAP includes the
information and terms and conditions required in subsection (b) of this
Section, then it will issue a final decision approving the owner’s or
operator’s RAP and, in writing, notify the owner or operator and all
commenters on the owner’s or operator’s draft RAP that the RAP
application has been approved.
3)
If the Agency determines that the owner’s or operator’s RAP does not
include the information required in subsection (b) of this Section, then it
will issue a final decision denying the RAP and, in writing, notify the
owner or operator and all commenters on the owner’s or operator’s draft
RAP that the RAP application has been denied.
4)
If the Agency’s final decision is that the tentative decision to deny the
RAP application was incorrect, it shall withdraw the notice of intent to
deny and proceed to prepare a draft RAP, according to the requirements
in this Subpart H.
5)
When the Agency issues its final RAP decision, it shall refer to the
procedures for appealing the decision under subsection (f) of this Section.
6)
Before issuing the final RAP decision, the Agency shall compile an
administrative record. Material readily available at the applicable Agency
office or published materials that are generally available and which are
included in the administrative record need not be physically included with
the rest of the record, as long as it is specifically referred to in the
statement of basis or the response to comments. The administrative
record for the final RAP must include information in the administrative
record for the draft RAP (see subsection (c)(2) of this Section) and the
following items:
A)
All comments received during the public comment period;
B)
Tapes or transcripts of any hearings;
C)
Any written materials submitted at these hearings;
D)
The responses to comments;
E)
Any new material placed in the record since the draft RAP was
issued;
F)
Any other documents supporting the RAP; and
41
G)
A copy of the final RAP.
7)
The Agency shall make information contained in the administrative record
available for review by the public upon request.
BOARD NOTE: Derived from 40 CFR 270.150, added at 63 Fed. Reg. 65944
(Nov. 30, 1998) (1999).
f)
May the decision to approve or deny a RAP application be administratively
appealed?
1)
Any commenter on the draft RAP or notice of intent to deny, or any
participant in any public hearing on the draft RAP, may appeal the
Agency’s decision to approve or deny the owner’s or operator’s RAP
application to the Board under 35 Ill. Adm. Code 705.212. Any person
that did not file comments, or did not participate in any public hearing(s)
hearings on the draft RAP, may petition for administrative review only to
the extent of the changes from the draft to the final RAP decision.
Appeals of RAPs may be made to the same extent as for final permit
decisions under 35 Ill. Adm. Code 705.201 (or a decision under Section
703.240 to deny a permit for the active life of a RCRA hazardous waste
management facility or unit). Instead of the notice required under 35 Ill.
Adm. Code 705.Subpart D and 705.212(c), the Agency shall give public
notice of any grant of review of a RAP through the same means used to
provide notice under subsection (d) of this Section. The notice will
include the following information:
A)
The public hearing and any briefing schedule for the appeal, as
provided by the Board;
B)
A statement that any interested person may participate in the
public hearing or file public comments or an amicus brief with the
Board; and
C)
The information specified in subsection (d)(3) of this Section, as
appropriate.
2)
This appeal is a prerequisite to seeking judicial review of these Agency
actions.
BOARD NOTE: Derived from 40 CFR 270.155, added at 63 Fed. Reg. 65944
(Nov. 30, 1998) (1999).
g)
When does a RAP become effective? An A RAP becomes effective 35 days
after the Agency notifies the owner or operator and all commenters that the RAP
42
is approved, unless any of the following is true:
1)
The Agency specifies a later effective date in its decision;
2)
An owner or operator or another person has appealed the RAP under
subsection (f) of this Section (if the RAP is appealed, and the request for
review is granted under subsection (f), conditions of the RAP are stayed
according to 35 Ill. Adm. Code 705.202 through 705.204); or
3)
No commenters requested a change in the draft RAP, in which case the
RAP becomes effective immediately when it is issued.
BOARD NOTE: Derived from 40 CFR 270.160, added at 63 Fed. Reg. 65944
(Nov. 30, 1998) (1999). The corresponding federal provision provides that a
RAP is effective 30 days after the Agency notice of approval. The Board has
used 35 days to be consistent with the 35 days within which a permit appeal must
be filed under Section 40(a)(1) of the Act [415 ILCS 5/40(a)(1)].
h)
When may an owner or operator begin physical construction of new units
permitted under the RAP? An owner or operator shall not begin physical
construction of new units permitted under the RAP for treating, storing, or
disposing of hazardous remediation waste before receiving a finally final,
effective RAP.
BOARD NOTE: Derived from 40 CFR 270.165, added at 63 Fed. Reg. 65944
(Nov. 30, 1998) (1999).
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
Section 703.304
How a RAP May Be Modified, Revoked and Reissued, or Terminated
a)
After a RAP is issued, how may it be modified, revoked and reissued, or
terminated? In a RAP, the Agency shall specify, either directly or by reference,
procedures for any future modification, revocation and reissuance, or termination
of the RAP. These procedures must provide adequate opportunities for public
review and comment on any modification, revocation and reissuance, or
termination that would significantly change the owner’s or operator’s
management of its remediation waste, or that otherwise merits public review and
comment. If the RAP has been incorporated into a traditional RCRA permit, as
allowed under Section 703.301(b)(3), then the RAP will be modified according
to the applicable requirements in Sections 703.260 through 703.283, revoked
and reissued according to the applicable requirements in 35 Ill. Adm. Code
702.186 and Sections 703.270 through 703.273, or terminated according to the
applicable requirements of 35 Ill. Adm. Code 702.186.
43
BOARD NOTE: Derived from 40 CFR 270.170, added at 63 Fed. Reg. 65944
(Nov. 30, 1998) (1999).
b)
For what reasons may the Agency choose to modify a final RAP?
1)
The Agency may modify the owner’s or operator’s final RAP on its own
initiative only if one or more of the following reasons listed in this
Section exist. If one or more of these reasons do not exist, then the
Agency shall not modify a final RAP, except at the request of the owner
or operator. Reasons for modification are the following:
A)
The owner or operator made material and substantial alterations or
additions to the activity that justify applying different conditions;
B)
The Agency finds new information that was not available at the
time of RAP issuance and would have justified applying different
RAP conditions at the time of issuance;
C)
The standards or regulations on which the RAP was based have
changed because of new or amended statutes, standards, or
regulations or by judicial decision after the RAP was issued;
D)
If the RAP includes any schedules of compliance, the Agency
may find reasons to modify the owner’s or operator’s compliance
schedule, such as an act of God, strike, flood, or materials
shortage or other events over which an owner or operator has
little or no control and for which there is no reasonably available
remedy;
E)
The owner or operator is not in compliance with conditions of its
RAP;
F)
The owner or operator failed in the application or during the RAP
issuance process to disclose fully all relevant facts, or an owner or
operator misrepresented any relevant facts at the time;
G)
The Agency has determined that the activity authorized by the
owner’s or operator’s RAP endangers human health or the
environment and can only be remedied by modifying the RAP; or
H)
The owner or operator has notified the Agency (as required in the
RAP and under 35 Ill. Adm. Code 702.152(c)) of a proposed
transfer of a RAP.
2)
Notwithstanding any other provision in this Section, when the Agency
44
reviews a RAP for a land disposal facility under Section 703.304(f), it
may modify the permit as necessary to assure that the facility continues to
comply with the currently applicable requirements in 35 Ill. Adm. Code
702, 703, 705, and 720 through 726.
3)
The Agency shall not reevaluate the suitability of the facility location at
the time of RAP modification unless new information or standards
indicate that a threat to human health or the environment exists that was
unknown when the RAP was issued.
BOARD NOTE: Derived from 40 CFR 270.175, added at 63 Fed. Reg. 65944
(Nov. 30, 1998) (1999).
c)
For what reasons may the Agency choose to revoke and reissue a final RAP?
1)
The Agency may revoke and reissue a final RAP on its own initiative
only if one or more reasons for revocation and reissuance exist. If one
or more reasons do not exist, then the Agency shall not modify or revoke
and reissue a final RAP, except at the owner’s or operator’s request.
Reasons for modification or revocation and reissuance are the same as the
reasons listed for RAP modifications in subsections (b)(1)(E) through
(b)(1)(H) of this Section if the Agency determines that revocation and
reissuance of the RAP is appropriate.
2)
The Agency shall not reevaluate the suitability of the facility location at
the time of RAP revocation and reissuance, unless new information or
standards indicate that a threat to human health or the environment exists
that was unknown when the RAP was issued.
BOARD NOTE: Derived from 40 CFR 270.180, added at 63 Fed. Reg. 65945
(Nov. 30, 1998) (1999).
d)
For what reasons may the Agency choose to terminate a final RAP, or deny a
renewal application? The Agency may terminate a final RAP on its own
initiative, or deny a renewal application for the same reasons as those listed for
RAP modifications in subsections (b)(1)(E) through (b)(1)(G) of this Section if
the Agency determines that termination of the RAP or denial of the RAP
renewal application is appropriate.
BOARD NOTE: Derived from 40 CFR 270.185, added at 63 Fed. Reg. 65945
(Nov. 30, 1998) (1999).
e)
May the decision to approve or deny a modification, revocation and reissuance,
or termination of a RAP be administratively appealed?
45
1)
Any commenter on the modification, revocation and reissuance, or
termination, or any person that participated in any hearing on these
actions, may appeal the Agency’s decision to approve a modification,
revocation and reissuance, or termination of a RAP, according to Section
703.303(f). Any person that did not file comments or did not participate
in any public hearing on the modification, revocation and reissuance, or
termination may petition for administrative review only of the changes
from the draft to the final RAP decision.
2)
Any commenter on the modification, revocation and reissuance, or
termination, or any person that participated in any hearing on these
actions, may appeal the Agency’s decision to deny a request for
modification, revocation and reissuance, or termination to the Board.
Any person that did not file comments or which did not participate in any
public hearing on the modification, revocation and reissuance, or
termination may petition for administrative review only of the changes
from the draft to the final RAP decision.
3)
The procedure for appeals of RAPs is as follows:
A)
The person appealing the decision shall send a petition to the
Board pursuant to 35 Ill. Adm. Code 101 and 105. The petition
must briefly set forth the relevant facts, state the defect or fault
that serves as the basis for the appeal, and explain the basis for the
petitioner’s legal standing to pursue the appeal.
B)
The Board has 120 days after receiving the petition to act on it.
C)
If the Board does not take action on the petition within 120 days
after receiving it, the appeal shall be considered denied.
BOARD NOTE: Corresponding 40 CFR 270.190(c)(2) and
(c)(3), as added at 63 Fed. Reg. 65945 (Nov. 30, 1998) (1999)
allow 60 days for administrative review, which is too short a time
for the Board to publish the appropriate notices, conduct public
hearings, and conduct its review. Rather, the Board has
borrowed the 120 days allowed as adequate time for Board
review of permit appeals provided in Section 40(a)(2) of the Act
[415 ILCS 5/40(a)(2)].
4)
This appeal is a prerequisite to seeking judicial review of the Agency
action on the RAP.
BOARD NOTE: Derived from 40 CFR 270.190, added at 63 Fed. Reg. 65945
(Nov. 30, 1998) (1999). The corresponding federal provisions provide for
46
informal appeal of an Agency RAP decision. There is no comparable informal
procedure under Sections 39 and 40 of the Act [415 ILCS 5/39 and 40].
f)
When will a RAP expire? RAPs must be issued for a fixed term, not to exceed
10 years, although they may be renewed upon approval by the Agency in fixed
increments of no more than ten years. In addition, the Agency shall review any
RAP for hazardous waste land disposal five years after the date of issuance or
reissuance and the owner or operator or the Agency shall follow the
requirements for modifying the RAP as necessary to assure that the owner or
operator continues to comply with currently applicable requirements in the Act
and RCRA sections 3004 and 3005.
BOARD NOTE: Derived from 40 CFR 270.195, added at 63 Fed. Reg. 65945
(Nov. 30, 1998) (1999).
g)
How may an owner or operator renew a RAP that is expiring? If an owner or
operator wishes to renew an expiring RAP, the owner or operator shall follow
the process for application for and issuance of RAPs in this Subpart H.
BOARD NOTE: Derived from 40 CFR 270.200, added at 63 Fed. Reg. 65945
(Nov. 30, 1998) (1999).
h)
What happens if the owner or operator has applied correctly for a RAP renewal
but has not received approval by the time its old RAP expires? If the owner or
operator has submitted a timely and complete application for a RAP renewal, but
the Agency, through no fault of the owner or operator, has not issued a new
RAP with an effective date on or before the expiration date of the previous
RAP, the previous RAP conditions continue in force until the effective date of
the new RAP or RAP denial.
BOARD NOTE: Derived from 40 CFR 270.205, added at 63 Fed. Reg. 65945
(Nov. 30, 1998) (1999).
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
Section 703.306
Obtaining a RAP for an Off-Site Location
May an owner or operator perform remediation waste management activities under a RAP at a
location removed from the area where the remediation wastes originated?
a)
An owner or operator may request a RAP for remediation waste management
activities at a location removed from the area where the remediation wastes
originated if the owner or operator believes such a location would be more
protective than the contaminated area or areas in close proximity.
47
b)
If the Agency determines that an alternative location, removed from the area
where the remediation waste originated, is more protective than managing
remediation waste at the area of contamination or areas in close proximity, then
the Agency shall approve a RAP for this alternative location.
c)
An owner or operator shall request the RAP, and the Agency shall approve or
deny the RAP, according to the procedures and requirements in this Subpart H
of this Part.
d)
A RAP for an alternative location must also meet the following requirements,
which the Agency shall include in the RAP for such locations:
1)
The RAP for the alternative location must be issued to the person
responsible for the cleanup from which the remediation wastes originated;
2)
The RAP is subject to the expanded public participation requirements in
Sections 703.191, 703.192, and 703.193;
3)
The RAP is subject to the public notice requirements in 35 Ill. Adm.
Code 705.163;
4)
The site permitted in the RAP may not be located within 61 meters or
200 feet of a fault that has had displacement in the Holocene time. (the
The owner or operator shall demonstrate compliance with this standard
through the requirements in Section 703.183(k).) (See the definitions of
terms in 35 Ill. Adm. Code 724.118(a).).
BOARD NOTE: Sites in Illinois are assumed to be in compliance with
the requirement of subsection (d)(4) of this Section, since they are not
listed in 40 CFR 264, Appendix VI.
e)
These alternative locations are remediation waste management sites, and retain
the following benefits of remediation waste management sites:
1)
Exclusion from facility-wide corrective action under 35 Ill. Adm. Code
724.201; and
2)
Application of 35 Ill. Adm. Code 724.101(j) in lieu of 35 Ill. Adm. Code
724.Subparts B, C, and D.
BOARD NOTE: Derived from 40 CFR 270.230, added at 63 Fed. Reg. 65946 (Nov. 30,
1998) (1999).
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
48
Section 703.Appendix A
Classification of Permit Modifications
Class
Modifications
A.
General Permit Provisions
1
1.
Administrative and informational changes.
1
2.
Correction of typographical errors.
1
3.
Equipment replacement or upgrading with functionally equivalent
components (e.g., pipes, valves, pumps, conveyors, controls).
4.
Changes in the frequency of or procedures for monitoring, reporting,
sampling, or maintenance activities by the permittee:
1
a.
To provide for more frequent monitoring, reporting, or
maintenance.
2
b.
Other changes.
5.
Schedule of compliance:
1*
a.
Changes in interim compliance dates, with prior approval of the
Agency.
3
b.
Extension of final compliance date.
1*
6.
Changes in expiration date of permit to allow earlier permit
termination, with prior approval of the Agency.
1*
7.
Changes in ownership or operational control of a facility, provided the
procedures of Section 703.260(b) are followed.
1*
8. Changes to remove permit conditions that are no longer applicable
(i.e., because the standards upon which they are based are no longer
applicable to the facility).
B.
General Facility Standards
1.
Changes to waste sampling or analysis methods:
1
a.
To conform with Agency guidance or Board regulations.
49
1*
b.
To incorporate changes associated with F039 (multi-source
leachate) sampling or analysis methods.
1*
c.
To incorporate changes associated with underlying hazardous
constituents in ignitable or corrosive wastes.
2
d.
Other changes.
2.
Changes to analytical quality assurance/control quality assurance or
quality control plan:
1
a.
To conform with agency guidance or regulations.
2
b.
Other changes.
1
3.
Changes in procedures for maintaining the operating record.
2
4.
Changes in frequency or content of inspection schedules.
5.
Changes in the training plan:
2
a.
That affect the type or decrease the amount of training given to
employees.
1
b.
Other changes.
6.
Contingency plan:
2
a.
Changes in emergency procedures (i.e., spill or release
response procedures).
1
b.
Replacement with functionally equivalent equipment, upgrade,
or relocate emergency equipment listed.
2
c.
Removal of equipment from emergency equipment list.
1
d.
Changes in name, address, or phone number of coordinators or
other persons or agencies identified in the plan.
Note: When a permit modification (such as introduction of a new unit)
requires a change in facility plans or other general facility standards,
that change must be reviewed under the same procedures as the permit
modification.
7.
CQA plan:
50
1
a.
Changes that the CQA officer certifies in the operating record
will provide equivalent or better certainty that the unit
components meet the design specifications.
2
b.
Other changes.
Note: When a permit modification (such as introduction of a new unit)
requires a change in facility plans or other general facility standards,
that change shall be reviewed under the same procedures as a permit
modification.
C.
Groundwater Protection
1.
Changes to wells:
2
a.
Changes in the number, location, depth, or design of upgradient
or downgradient wells of permitted groundwater monitoring
system.
1
b.
Replacement of an existing well that has been damaged or
rendered inoperable, without change to location, design, or
depth of the well.
1*
2.
Changes in groundwater sampling or analysis procedures or
monitoring schedule, with prior approval of the Agency.
1*
3.
Changes in statistical procedure for determining whether a statistically
significant change in groundwater quality between upgradient and
downgradient wells has occurred, with prior approval of the Agency.
2*
4.
Changes in point of compliance.
5.
Changes in indicator parameters, hazardous constituents, or
concentration limits (including ACLs (Alternate Concentration Limits)):
3
a.
As specified in the groundwater protection standard.
2
b.
As specified in the detection monitoring program.
2
6.
Changes to a detection monitoring program as required by 35 Ill.
Adm. Code 724.198(j), unless otherwise specified in this Appendix.
7.
Compliance monitoring program:
51
3
a.
Addition of compliance monitoring program as required by 35
Ill. Adm. Code 724.198(h)(4) and 724.199.
2
b.
Changes to a compliance monitoring program as required by 35
Ill. Adm. Code 724.199(k), unless otherwise specified in this
Appendix.
8.
Corrective action program:
3
a.
Addition of a corrective action program as required by 35 Ill.
Adm. Code 724.199(i)(2) and 724.200.
2
b.
Changes to a corrective action program as required by 35 Ill.
Adm. Code 724.200(h), unless otherwise specified in this
Appendix.
D.
Closure
1.
Changes to the closure plan:
1*
a.
Changes in estimate of maximum extent of operations or
maximum inventory of waste on-site at any time during the
active life of the facility, with prior approval of the Agency.
1*
b.
Changes in the closure schedule for any unit, changes in the
final closure schedule for the facility or extension of the closure
period, with prior approval of the Agency.
1*
c.
Changes in the expected year of final closure, where other
permit conditions are not changed, with prior approval of the
Agency.
1*
d.
Changes in procedures for decontamination of facility
equipment or structures, with prior approval of the Agency.
2
e.
Changes in approved closure plan resulting from unexpected
events occurring during partial or final closure, unless
otherwise specified in this Appendix.
2
f.
Extension of the closure period to allow a landfill, surface
impoundment, or land treatment unit to receive non-hazardous
wastes after final receipt of hazardous wastes under 35 Ill.
Adm. Code 724.213(d) or (e).
3
2.
Creation of a new landfill unit as part of closure.
52
3.
Addition of the following new units to be used temporarily for closure
activities:
3
a.
Surface impoundments.
3
b.
Incinerators.
3
c.
Waste piles that do not comply with 35 Ill. Adm. Code
724.350(c).
2
d.
Waste piles that comply with 35 Ill. Adm. Code 724.350(c).
2
e.
Tanks or containers (other than specified in paragraph D(3)(f)
below).
1*
f.
Tanks used for neutralization, dewatering, phase separation, or
component separation, with prior approval of the Agency.
2
g.
Staging piles.
E.
Post-Closure
1
1.
Changes in name, address, or phone number of contact in post-closure
plan.
2
2.
Extension of post-closure care period.
3
3.
Reduction in the post-closure care period.
1
4.
Changes to the expected year of final closure, where other permit
conditions are not changed.
2
5.
Changes in post-closure plan necessitated by events occurring during
the active life of the facility, including partial and final closure.
F.
Containers
1.
Modification or addition of container units:
3
a.
Resulting in greater than 25 percent increase in the facility’s
container storage capacity, except as provided in F(1)(c) and
F(4)(a).
53
2
b.
Resulting in up to 25 percent increase in the facility’s container
storage capacity, except as provided in F(1)(c) and F(4)(a).
1
c.
Or Modification or addition of container units or treatment
processes necessary to treat wastes that are restricted from land
disposal to meet some or all of the applicable treatment
standards or to treat wastes to satisfy (in whole or in part) the
standard of “use of practically available technology that yields
the greatest environmental benefit” contained in 40 CFR
268.8(a)(2)(ii), incorporated by reference in 35 Ill. Adm. Code
728.108, with prior approval of the Agency. This modification
may also involve the addition of new waste codes or narrative
description of wastes. It is not applicable to dioxin-containing
wastes (F020, F021, F022, F023, F026, F027 and F028).
2.
Modification of container units without an increased capacity or
alteration of the system:
2
a.
Modification of a container unit without increasing the capacity
of the unit.
1
b.
Addition of a roof to a container unit without alteration of the
containment system.
3.
Storage of different wastes in containers, except as provided in F(4):
3
a.
That require additional or different management practices from
those authorized in the permit.
2
b.
That do not require additional or different management
practices from those authorized in the permit.
Note: See Section 703.280(g) for modification procedures to
be used for the management of newly listed or identified
wastes.
4.
Storage or treatment of different wastes in containers:
54
2
a.
That require addition of units or change in treatment process or
management standards, provided that the wastes are restricted
from land disposal and are to be treated to meet some or all of
the applicable treatment standards, or are to be treated to satisfy
(in whole or in part) the standard of “use of practically
available technology that yields the greatest environmental
benefit” contained in 40 CFR 268.8(a)(2)(ii), incorporated by
reference in 35 Ill. Adm. Code 728.108. It is not applicable to
dioxin-containing wastes (F020, F021, F022, F023, F026, F027
and F028).
1*
b.
That do not require the addition of units or a change in the
treatment process or management standards, and provided that
the units have previously received wastes of the same type
(e.g., incinerator scrubber water). This modification is not
applicable to dioxin-containing wastes (F020, F021, F022,
F023, F026, F027 and F028).
G.
Tanks
1.
3
a.
Modification or addition of tank units resulting in greater than
25 percent increase in the facility’s tank capacity, except as
provided in paragraphs G(1)(c), G(1)(d) and G(1)(e).
2
b.
Modification or addition of tank units resulting in up to 25
percent increase in the facility’s tank capacity, except as
provided in paragraphs G(1)(d) and G(1)(e).
2
c.
Addition of a new tank that will operate for more than 90 days
using any of the following physical or chemical treatment
technologies: neutralization, dewatering, phase separation, or
component separation.
1*
d.
After prior approval of the Agency, addition of a new tank that
will operate for up to 90 days using any of the following
physical or chemical treatment technologies: neutralization,
dewatering, phase separation, or component separation.
55
1*
e.
Modification or addition of tank units or treatment processes
that are necessary to treat wastes that are restricted from land
disposal to meet some or all of the applicable treatment
standards or to treat wastes to satisfy (in whole or in part) the
standard of “use of practically available technology that yields
the greatest environmental benefit” contained in 40 CFR
268.8(a)(2)(ii), incorporated by reference in 35 Ill. Adm. Code
728.108, with prior approval of the Agency. This modification
may also involve the addition of new waste codes. It is not
applicable to dioxin-containing wastes (F020, F021, F022,
F023, F026, F027 and F028).
2
2.
Modification of a tank unit or secondary containment system without
increasing the capacity of the unit.
1
3.
Replacement of a tank with a tank that meets the same design standards
and has a capacity within ± 10 percent of the replaced tank provided:
a.
The capacity difference is no more than 1500 gallons,
b.
The facility’s permitted tank capacity is not increased, and
c.
The replacement tank meets the same conditions in the permit.
2
4.
Modification of a tank management practice.
5.
Management of different wastes in tanks:
3
a.
That require additional or different management practices, tank
design, different fire protection specifications or significantly
different tank treatment process from that authorized in the
permit, except as provided in paragraph G(5)(c).
2
b.
That do not require additional or different management
practices or tank design, different fire protection specification,
or significantly different tank treatment process than authorized
in the permit, except as provided in paragraph G(5)(d).
Note: See Section 703.280(g) for modification procedures to
be used for the management of newly listed or identified
wastes.
56
1*
c.
That require addition of units or change in treatment processes
or management standards, provided that the wastes are
restricted from land disposal and are to be treated to meet some
or all of the applicable treatment standards, or that are to be
treated to satisfy (in whole or in part) the standard of “use of
practically available technology that yields the greatest
environmental benefit” contained in 40 CFR 268.8(a)(2)(ii),
incorporated by reference in 35 Ill. Adm. Code 728.108. The
modification is not applicable to dioxin-containing wastes (F020,
F021, F022, F023, F026, F027 and F028).
1
d.
That do not require the addition of units or a change in the
treatment process or management standards, and provided that
the units have previously received wastes of the same type
(e.g., incinerator scrubber water). This modification is not
applicable to dioxin-containing wastes (F020, F021, F022,
F023, F026, F027 and F028).
Note: See Section 703.280(g) for modification procedures to
be used for the management of newly listed or identified
wastes.
H.
Surface Impoundments
3
1.
Modification or addition of surface impoundment units that result in
increasing the facility’s surface impoundment storage or treatment
capacity.
3
2.
Replacement of a surface impoundment unit.
2
3.
Modification of a surface impoundment unit without increasing the
facility’s surface impoundment storage or treatment capacity and
without modifying the unit’s liner, leak detection system, or leachate
collection system.
2
4.
Modification of a surface impoundment management practice.
5.
Treatment, storage, or disposal of different wastes in surface
impoundments:
3
a.
That require additional or different management practices or
different design of the liner or leak detection system than
authorized in the permit.
57
2
b.
That do not require additional or different management
practices or different design of the liner or leak detection system
than authorized in the permit.
Note: See Section 703.280(g) for modification procedures to
be used for the management of newly listed or identified
wastes.
1
c.
That are wastes restricted from land disposal that meet the
applicable treatment standards or that are treated to satisfy the
standard of “use of practically available technology that yields
the greatest environmental benefit” contained in 40 CFR
268.8(a)(2)(ii), incorporated by reference in 35 Ill. Adm. Code
728.108, and provided that the unit meets the minimum
technological requirements stated in 40 CFR 268.5(h)(2),
incorporated by reference in 35 Ill. Adm. Code 728.105. This
modification is not applicable to dioxin-containing wastes (F020,
F021, F022, F023, F026, F027 and F028).
1
d.
That are residues from wastewater treatment or incineration,
provided the disposal occurs in a unit that meets the minimum
technological requirements stated in 40 CFR 268.5(h)(2),
incorporated by reference in 35 Ill. Adm. Code 728.105, and
provided further that the surface impoundment has previously
received wastes of the same type (for example, incinerator
scrubber water). This modification is not applicable to dioxin-
containing wastes (F020, F021, F022, F023, F026, F027 and
F028).
1*
6.
Modifications of unconstructed units to comply with 35 Ill. Adm. Code
724.321(c), 724.322, 724.323, and 724.326(d).
7.
Changes in response action plan:
3
a.
Increase in action leakage rate.
3
b.
Change in a specific response reducing its frequency or
effectiveness.
2
c.
Other changes.
Note: See Section 703.280(g) for modification procedures to be
used for the management of newly listed or identified wastes.
58
I.
Enclosed Waste Piles. For all waste piles, except those complying with 35 Ill.
Adm. Code 724.350(c), modifications are treated the same as for a landfill.
The following modifications are applicable only to waste piles complying with
35 Ill. Adm. Code 724.350(c).
1.
Modification or addition of waste pile units:
3
a.
Resulting in greater than 25 percent increase in the facility’s
waste pile storage or treatment capacity.
2
b.
Resulting in up to 25 percent increase in the facility’s waste pile
storage or treatment capacity.
2
2.
Modification of waste pile unit without increasing the capacity of the
unit.
1
3.
Replacement of a waste pile unit with another waste pile unit of the
same design and capacity and meeting all waste pile conditions in the
permit.
2
4.
Modification of a waste pile management practice.
5.
Storage or treatment of different wastes in waste piles:
3
a.
That require additional or different management practices or
different design of the unit.
2
b.
That do not require additional or different management
practices or different design of the unit.
Note: See Section 703.280(g) for modification procedures to be
used for the management of newly listed or identified wastes.
2
6.
Conversion of an enclosed waste pile to a containment building unit.
Note: See Section 703.280(g) for modification procedures to be used
for the management of newly listed or identified wastes.
J.
Landfills and Unenclosed Waste Piles
3
1.
Modification or addition of landfill units that result in increasing the
facility’s disposal capacity.
3
2.
Replacement of a landfill.
59
3
3.
Addition or modification of a liner, leachate collection system, leachate
detection system, runoff control, or final cover system.
2
4.
Modification of a landfill unit without changing a liner, leachate
collection system, leachate detection system, runoff control, or final
cover system.
2
5.
Modification of a landfill management practice.
6.
Landfill different wastes:
3
a.
That require additional or different management practices,
different design of the liner, leachate collection system, or
leachate detection system.
2
b.
That do not require additional or different management
practices, different design of the liner, leachate collection
system, or leachate detection system.
Note: See Section 703.280(g) for modification procedures to be
used for the management of newly listed or identified wastes.
1
c.
That are wastes restricted from land disposal that meet the
applicable treatment standards or that are treated to satisfy the
standard of “use of practically available technology that yields
the greatest environmental benefit” contained in 40 CFR
268.8(a)(2)(ii), incorporated by reference in 35 Ill. Adm. Code
728.108, and provided that the landfill unit meets the minimum
technological requirements stated in 40 CFR 268.5(h)(2),
incorporated by reference in 35 Ill. Adm. Code 728.105. This
modification is not applicable to dioxin-containing wastes (F020,
F021, F022, F023, F026, F027 and F028).
1
d.
That are residues from wastewater treatment or incineration,
provided the disposal occurs in a landfill unit that meets the
minimum technological requirements stated in 40 CFR
268.5(h)(2), incorporated by reference in 35 Ill. Adm. Code
728.105, and provided further that the landfill has previously
received wastes of the same type (for example, incinerator ash).
This modification is not applicable to dioxin-containing wastes
(F020, F021, F022, F023, F026, F027 and F028).
1*
7.
Modification of unconstructed units to comply with 35 Ill. Adm. Code
724.351(c), 724.352, 724.353, 724.354(c), 724.401(c), 724.402,
724.403(c), and 724.404.
60
8.
Changes in response action plan:
3
a.
Increase in action leakage rate.
3
b.
Change in a specific response reducing its frequency or
effectiveness.
2
c.
Other changes.
Note: See Section 703.280(g) for modification procedures to be
used for the management of newly listed or identified wastes.
K.
Land Treatment
3
1.
Lateral expansion of or other modification of a land treatment unit to
increase area extent.
2
2.
Modification of runon control system.
3
3.
Modify runoff control system.
2
4.
Other modification of land treatment unit component specifications or
standards required in permit.
5.
Management of different wastes in land treatment units:
3
a.
That require a change in permit operating conditions or unit
design specifications.
2
b.
That do not require a change in permit operating conditions or
unit design specifications.
Note: See Section 703.280(g) for modification procedures to be
used for the management of newly listed or identified wastes.
6.
Modification of a land treatment unit management practice to:
3
a.
Increase rate or change method of waste application.
1
b.
Decrease rate of waste application.
2
7.
Modification of a land treatment unit management practice to change
measures of pH or moisture content or to enhance microbial or
chemical reactions.
61
3
8.
Modification of a land treatment unit management practice to grow
food chain crops, to add to or replace existing permitted crops with
different food chain crops or to modify operating plans for distribution
of animal feeds resulting from such crops.
3
9.
Modification of operating practice due to detection of releases from the
land treatment unit pursuant to 35 Ill. Adm. Code 724.378(g)(2).
3
10.
Changes in the unsaturated zone monitoring system that result in a
change to the location, depth, or number of sampling points or which
replace unsaturated zone monitoring devices or components of devices
with devices or components that have specifications different from
permit requirements.
2
11.
Changes in the unsaturated zone monitoring system that do not result in
a change to the location, depth, or number of sampling points or which
replace unsaturated zone monitoring devices or components of devices
with devices or components having specifications different from permit
requirements.
2
12.
Changes in background values for hazardous constituents in soil and
soil-pore liquid.
2
13.
Changes in sampling, analysis, or statistical procedure.
2
14.
Changes in land treatment demonstration program prior to or during
the demonstration.
1*
15.
Changes in any condition specified in the permit for a land treatment
unit to reflect results of the land treatment demonstration, provided
performance standards are met, and the Agency’s prior approval has
been received.
1*
16.
Changes to allow a second land treatment demonstration to be
conducted when the results of the first demonstration have not shown
the conditions under which the wastes can be treated completely,
provided the conditions for the second demonstration are substantially
the same as the conditions for the first demonstration and have received
the prior approval of the Agency.
62
3
17.
Changes to allow a second land treatment demonstration to be
conducted when the results of the first demonstration have not shown
the conditions under which the wastes can be treated completely,
where the conditions for the second demonstration are not substantially
the same as the conditions for the first demonstration.
2
18.
Changes in vegetative cover requirements for closure.
L.
Incinerators, Boilers and Industrial Furnaces
3
1.
Changes to increase by more than 25 percent any of the following
limits authorized in the permit: A thermal feed rate limit, a feedstream
feed rate limit, a chlorine/chloride feed rate limit, a metal feed rate
limit, or an ash feed rate limit. The Agency shall require a new trial
burn to substantiate compliance with the regulatory performance
standards unless this demonstration can be made through other means.
2
2.
Changes to increase by up to 25 percent any of the following limits
authorized in the permit: A thermal feed rate limit, a feedstream feed
rate limit, a chlorine/chloride feed rate limit, a metal feed rate limit, or
an ash feed rate limit. The Agency shall require a new trial burn to
substantiate compliance with the regulatory performance standards
unless this demonstration can be made through other means.
3
3.
Modification of an incinerator, boiler, or industrial furnace unit by
changing the internal size or geometry of the primary or secondary
combustion units; by adding a primary or secondary combustion unit;
by substantially changing the design of any component used to remove
HCl/Cl
2
, metals, or particulate from the combustion gases; or by
changing other features of the incinerator, boiler, or industrial furnace
that could affect its capability to meet the regulatory performance
standards. The Agency shall require a new trial burn to substantiate
compliance with the regulatory performance standards, unless this
demonstration can be made through other means.
2
4.
Modification of an incinerator, boiler, or industrial furnace unit in a
manner that will not likely affect the capability of the unit to meet the
regulatory performance standards but which will change the operating
conditions or monitoring requirements specified in the permit. The
Agency may require a new trial burn to demonstrate compliance with
the regulatory performance standards.
5.
Operating requirements:
63
3
a.
Modification of the limits specified in the permit for minimum
or maximum combustion gas temperature, minimum combustion
gas residence time, oxygen concentration in the secondary
combustion chamber, flue gas carbon monoxide or hydrocarbon
concentration, maximum temperature at the inlet to the PM
emission control system, or operating parameters for the air
pollution control system. The Agency shall require a new trial
burn to substantiate compliance with the regulatory performance
standards unless this demonstration can be made through other
means.
3
b.
Modification of any stack gas emission limits specified in the
permit, or modification of any conditions in the permit
concerning emergency shutdown or automatic waste feed cutoff
procedures or controls.
2
c.
Modification of any other operating condition or any inspection
or recordkeeping requirement specified in the permit.
6.
Burning different wastes:
3
a.
If the waste contains a POHC that is more difficult to burn than
authorized by the permit or if burning of the waste requires
compliance with different regulatory performance standards
than specified in the permit, the Agency shall require a new
trial burn to substantiate compliance with the regulatory
performance standards, unless this demonstration can be made
through other means.
2
b.
If the waste does not contain a POHC that is more difficult to
burn than authorized by the permit and if burning of the waste
does not require compliance with different regulatory
performance standards than specified in the permit.
Note: See Section 703.280(g) for modification procedures to be
used for the management of newly listed or identified wastes.
7.
Shakedown and trial burn:
2
a.
Modification of the trial burn plan or any of the permit
conditions applicable during the shakedown period for
determining operational readiness after construction, the trial
burn period or the period immediately following the trial burn.
64
1*
b.
Authorization of up to an additional 720 hours of waste burning
during the shakedown period for determining operational
readiness after construction, with the prior approval of the
Agency.
1*
c.
Changes in the operating requirements set in the permit for
conducting a trial burn, provided the change is minor and has
received the prior approval of the Agency.
1*
d.
Changes in the ranges of the operating requirements set in the
permit to reflect the results of the trial burn, provided the
change is minor and has received the prior approval of the
Agency.
1
8.
Substitution of an alternate alternative type of non-hazardous waste fuel
that is not specified in the permit.
1*
9.
Technology changes needed to meet standards under federal 40 CFR
63 (Subpart subpart EEE--National Emission Standards for Hazardous
Air Pollutants From Hazardous Waste Combustors), provided the
procedures of Section 703.280(j) are followed.
M.
Containment Buildings.
1.
Modification or addition of containment building units:
3
a.
Resulting in greater than 25 percent increase in the facility’s
containment building storage or treatment capacity.
2
b.
Resulting in up to 25 percent increase in the facility’s
containment building storage or treatment capacity.
2
2.
Modification of a containment building unit or secondary containment
system without increasing the capacity of the unit.
3.
Replacement of a containment building with a containment building that
meets the same design standards provided:
1
a.
The unit capacity is not increased.
1
b.
The replacement containment building meets the same
conditions in the permit.
2
4.
Modification of a containment building management practice.
65
5.
Storage or treatment of different wastes in containment buildings:
3
a.
That require additional or different management practices.
2
b.
That do not require additional or different management
practices.
N.
Corrective Action.
3
1.
Approval of a corrective action management unit pursuant to 35 Ill.
Adm. Code 724.652.
2
2.
Approval of a temporary unit or time extension pursuant to 35 Ill.
Adm. Code 724.653.
2
3.
Approval of a staging pile or staging pile operating term extension
pursuant to 35 Ill. Adm. Code 724.654.
Note:* indicates modifications requiring prior Agency approval.
BOARD NOTE: Derived from 40 CFR 270.42, Appendix I (1998) (1999), as amended at 63
64 Fed. Reg. 65941 (Nov. 30, 1998) 53077 (September 30, 1999).
(Source: Amended at 24 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
Section
720.110
Definitions
720.111
References
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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
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;
67
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. ________, effective
______________________.
SUBPART B: DEFINITIONS
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:
“Aboveground tank” means a device meeting the definition of “tank” 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 U.S. 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 tank(s) 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.
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“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.
“Boiler” means an enclosed device using controlled flame combustion and having
the following characteristics:
Physical 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 section(s) sections must be of integral design. To
be of integral design, the combustion chamber and the primary
energy recovery section(s) 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 section(s) 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 be given for recovered heat used
69
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.
“Closed portion” means that portion of a facility which 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 which 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
70
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,
WhichOf which any of the following is true:
Has The facility has received a RCRA permit (or interim status)
pursuant to 35 Ill. Adm. Code 702, 703 and 705;
Has The facility has received a RCRA permit from USEPA
pursuant to 40 CFR 124 and 270 (1992) (1999);
Has The facility has received a RCRA permit from a state
authorized by USEPA pursuant to 40 CFR 271 (1992) (1999); or
Is The facility is regulated under 35 Ill. Adm. Code 721.106(c)(2)
or 266.Subpart F; and
Which 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, which 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-
71
chlorinated dibenzo dioxins and furans.
“Director” means the Director of the Illinois Environmental Protection Agency.
“Discharge” or “hazardous waste discharge” means the accidental or intentional
spilling, leaking, pumping, pouring, emitting, emptying, or dumping of
hazardous waste into or on any land or water.
“Disposal” means the discharge, deposit, injection, dumping, spilling, leaking, or
placing of any solid waste or hazardous waste into or on any land or water so
that such solid waste or hazardous waste or any constituent thereof may enter the
environment or be emitted into the air or discharged into any waters, including
groundwaters.
“Disposal facility” means a facility or part of a facility at which hazardous waste
is intentionally placed into or on any land or water and at which waste will
remain after closure. The term disposal facility does not include a corrective
action management unit (CAMU) into which remediation wastes are placed.
“Drip pad” means an engineered structure consisting of a curbed, free-draining
base, constructed of non-earthen materials and designed to convey preservative
kick-back or drippage from treated wood, precipitation and surface water runon
to an associated collection system at wood preserving plants.
“Electric lamp” means the bulb or tube portion of a lighting device specifically
designed to produce radiant energy, most often in the ultraviolet, visible, and
infrared regions of the electromagnetic spectrum.
BOARD NOTE: The definition of “electric lamp” was added pursuant to
Section 22.23a of the Act [415 ILCS 5/22.23a] (see P.A. 90-502, effective
August 19, 1997).
“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.
72
“EPA identification number” or “USEPA identification number” means the
number assigned by USEPA pursuant to 35 Ill. Adm. Code 722 through 725 to
each generator; transporter; and treatment, storage, or disposal facility.
“EPA region” or “USEPA region” means the states and territories found in any
one of the following ten regions:
Region I: Maine, Vermont, New Hampshire, Massachusetts,
Connecticut, and Rhode Island
Region II: New York, New Jersey, Commonwealth of Puerto Rico, and
the U.S. Virgin Islands
Region III: Pennsylvania, Delaware, Maryland, West Virginia, Virginia,
and the District of Columbia
Region IV: Kentucky, Tennessee, North Carolina, Mississippi, Alabama,
Georgia, South Carolina, and Florida
Region V: Minnesota, Wisconsin, Illinois, Michigan, Indiana, and Ohio
Region VI: New Mexico, Oklahoma, Arkansas, Louisiana, and Texas
Region VII: Nebraska, Kansas, Missouri, and Iowa
Region VIII: Montana, Wyoming, North Dakota, South Dakota, Utah,
and Colorado
Region IX: California, Nevada, Arizona, Hawaii, Guam, American
Samoa, and Commonwealth of the Northern Mariana Islands
Region X: Washington, Oregon, Idaho, and Alaska
“Equivalent method” means any testing or analytical method approved by the
Board pursuant to Section 720.120.
“Existing hazardous waste management (HWM) facility” or “existing facility”
means a facility which 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 State, and
local approvals or permits necessary to begin physical construction and either:
A continuous on-site, physical construction program had begun; or
73
The owner or operator had entered into contractual obligations, which
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 is was in operation or for which installation has was commenced on or
prior to July 14, 1986. Installation will be considered to have commenced if the
owner or operator has obtained all federal, State, and local approvals or permits
necessary to begin physical construction of the site or installation of the tank
system and if either of the following is true:
A continuous on-site physical construction or installation program has
begun; or
The owner or operator has entered into contractual obligations, which
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
74
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 U.S. United States Department
of Defense (U.S. DODUSDOD) emergency explosive ordnance disposal (EOD),
technical escort unit (TEU), and U.S. DODUSDOD-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:
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 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 State, and local approvals or permits necessary to begin physical
construction” means permits and approvals required under federal, state 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
75
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 produce produces
hazardous waste identified or listed in 35 Ill. Adm. Code 721 or whose act first
causes a hazardous waste to become subject to regulation.
“Groundwater” means water below the land surface in a zone of saturation.
“Hazardous waste” means a hazardous waste as defined in 35 Ill. Adm. Code
721.103.
“Hazardous waste constituent” means a constituent which 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 that of which the following is true:
Uses 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
76
Meets The facility meets the definition of infrared incinerator or plasma
arc incinerator.
“Incompatible waste” means a hazardous waste which 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, 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;
77
Halogen acid furnaces (HAFs) for the production of acid from
halogenated hazardous waste generated by chemical production facilities
where the furnace is located on the site of a chemical production facility,
the acid product has a halogen acid content of at least three percent, the
acid product is used in a manufacturing process, and, except for
hazardous waste burned as fuel, hazardous waste fed to the furnace has a
minimum halogen content of 20 percent, as generated; and
Any other such device as the Agency determines to be an “Industrial
Furnace” 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 which 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.
78
“In operation” refers to a facility which that is treating, storing, or disposing of
hazardous waste.
“Injection well” means a well into which fluids are being injected. (See also
“underground injection”.)
“Inner liner” means a continuous layer of material placed inside a tank or
container which 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 which 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.
79
“Liner” means a continuous layer of natural or manmade materials beneath or on
the sides of a surface impoundment, landfill, or landfill cell, which that restricts
the downward or lateral escape of hazardous waste, hazardous waste
constituents, or leachate.
“Leak-detection system” means a system capable of detecting the failure of either
the primary or secondary containment structure or the presence of a release of
hazardous waste or accumulated liquid in the secondary containment structure.
Such a system must employ operational controls (e.g., daily visual inspections for
releases into the secondary containment system of aboveground tanks) or consist
of an interstitial monitoring device designed to detect continuously and
automatically the failure of the primary or secondary containment structure or the
presence of a release of hazardous waste into the secondary containment
structure.
“Management” or “hazardous waste management” means the systematic control
of the collection, source separation, storage, transportation, processing,
treatment, recovery, and disposal of hazardous waste.
“Manifest” means the shipping document originated and signed by the generator
which 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.
“Mercury-containing lamp” means an electric lamp into which mercury is
purposely introduced by the manufacturer for the operation of the lamp.
Mercury-containing lamps include, but are not limited to, fluorescent lamps and
high-intensity discharge lamps.
BOARD NOTE: The definition of “mercury-containing lamp” was added
pursuant to Section 22.23a of the Act [415 ILCS 5/22.23a] (see P.A. 90-502,
effective August 19, 1997).
“Military munitions” means all ammunition products and components produced
or used by or for the U.S. United States Department of Defense or the U.S.
United States Armed Services for national defense and security, including
military munitions under the control of the U.S. United States Department of
Defense, the U.S. United States Coast Guard, the U.S. United States
Department of Energy (U.S. DOE 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 U.S. DOD USDOD components, including bulk
explosives and chemical warfare agents, chemical munitions, rockets, guided and
80
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 U.S. DOE 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.
“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 that hazardous waste that is transported to a facility in an
individual vehicle.
“New hazardous waste management facility” or “new facility” means a facility
which 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 commences 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
81
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.
(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 which 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
82
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 subsections
paragraphs of this definition.
BOARD NOTE: The second exception of corresponding 40 CFR
260.10 reads as follows: “Is an animal drug that has been determined by
regulation of the Secretary of Health and Human Services not to be a
new animal drug”. This is very similar to the language of section 2(u) of
the Federal Insecticide, Fungicide, and Rodenticide Act (FIFRA; 7 USC
136(u)). The three exceptions, taken together, appear intended not to
include as “pesticide” any material within the scope of federal Food and
Drug Administration regulation. The Board codified this provision with
the intent of retaining the same meaning as its federal counterpart while
adding the definiteness required under Illinois law.
“Pile” means any noncontainerized accumulation of solid, non-flowing hazardous
waste that is used for treatment or storage, and that is not a containment building.
“Plasma arc incinerator” means any enclosed device which 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
83
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 listed hazardous wastes or which themselves exhibit a hazardous waste
characteristic which 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) which 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
84
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 which 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.
“Small Quantity Generator quantity generator” means a generator which 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
which that is a natural topographic depression, manmade excavation, or diked
85
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.
“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 which
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 which 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,
86
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.;
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 such the waste, so as to recover
energy or material resources from the waste, or so as to render such 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
87
entire surface area is totally below the surface of and covered by the ground.
“Unfit-for-use tank system” means a tank system that has been determined,
through an integrity assessment or other inspection, to be no longer capable of
storing or treating hazardous waste without posing a threat of release of
hazardous waste to the environment.
“United States” means the 50 states, the District of Columbia, the
Commonwealth of Puerto Rico, the U.S. Virgin Islands, Guam, American
Samoa, and the Commonwealth of the Northern Mariana Islands.
“Universal waste” means any of the following hazardous wastes that are
managed under the universal waste requirements of 35 Ill. Adm. Code 733:
Batteries, as described in 35 Ill. Adm. Code 733.102;
Pesticides, as described in 35 Ill. Adm. Code 733.103;
Thermostats, as described in 35 Ill. Adm. Code 733.104; and
Mercury-containing lampsLamps, as described in 35 Ill. Adm. Code
733.107 733.105.
BOARD NOTE: Mercury-containing lamps were added as universal
waste pursuant to Section 22.23a of the Act [415 ILCS 5/22.23a] (see
P.A. 90-502, effective August 19, 1997).
“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.
88
“Universal waste transporter” means a person engaged in the off-site
transportation of universal waste by air, rail, highway, or water.
“Unsaturated zone” or “zone of aeration” means the zone between the land
surface and the water table.
“Uppermost aquifer” means the geologic formation nearest the natural ground
surface that is an aquifer, as well as lower aquifers that are hydraulically
interconnected with this aquifer within the facility’s property boundary.
“USDOT” or “Department of Transportation” means the United States
Department of Transportation.
“Used oil” means any oil that has been refined from crude oil, or any synthetic
oil, that has been used and as a result of such use is contaminated by physical or
chemical impurities.
“USEPA” or “EPA” or “U.S. EPA” means the United States Environmental
Protection Agency.
“Vessel” includes every description of watercraft, used or capable of being used
as a means of transportation on the water.
“Wastewater treatment unit” means a device of which the following is true:
Is It is part of a wastewater treatment facility which 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
Receives It receives and treats or stores an influent wastewater which 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
Meets It meets the definition of tank or tank system in this Section.
“Water (bulk shipment)” means the bulk transportation of hazardous waste which
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.
89
“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 24 Ill. Reg. ________, effective ______________________)
Section 720.111
References
The following documents are incorporated by reference for the purposes of this Part and 35 Ill.
Adm. Code 703 through 705, 721 through 726, 728, 730, 733, 738, and 739:
a)
The following publications 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: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.
90
“Installation of Underground Petroleum Storage Systems”, API
Recommended Practice 1615, Fourth Edition, November, 1987.
APTI. Available from the Air and Waste Management Association, Box
2861, Pittsburgh, PA 15230, 412-232-3444:
APTI Course 415: Control of Gaseous Emissions, USEPA
Publication EPA-450/2-81-005, December, 1981.
ASME. Available from the American Society of Mechanical Engineers,
345 East 47th Street, New York, NY 10017, 212-705-7722:
“Chemical Plant and Petroleum Refinery Piping”, ASME/ANSI
B31.3-1987, as supplemented by B31.3a-1988 and B31.3b-1988.
Also available from ANSI.
“Liquid Transportation Systems for Hydrocarbons, Liquid
Petroleum Gas, Anhydrous Ammonia, and Alcohols”,
ASME/ANSI B31.4-1986, as supplemented by B31.4a-1987.
Also available from ANSI.
ASTM. Available from American Society for Testing and Materials,
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
91
of Hydrocarbon Fuels by Bomb Calorimeter (High Precision
Method), approved October 31, 1988.
ASTM D 2879-92, Standard Test Method for Vapor Pressure-
Temperature Relationship and Initial Decomposition Temperature
of Liquids by Isoteniscope, approved 1992.
ASTM D 3828-87, Standard Test Methods for Flash Point of
Liquids by Setaflash Closed Tester, approved December 14,
1988.
ASTM E 168-88, Standard Practices for General Techniques of
Infrared Quantitative Analysis, approved May 27, 1988.
ASTM E 169-87, Standard Practices for General Techniques of
Ultraviolet-Visible Quantitative Analysis, approved February 1,
1987.
ASTM E 260-85, Standard Practice for Packed Column Gas
Chromatography, approved June 28, 1985.
ASTM Method G 21-70 (1984a), — Standard Practice for
Determining Resistance of Synthetic Polymer Materials to Fungi.
ASTM Method G 22-76 (1984b), — Standard Practice for
Determining Resistance of Plastics to Bacteria.
MICE. Methods Information Communication Exchange Service, 703-
821-4690:
“Test Methods for Evaluating Solid Waste, Physical/Chemical
Methods”, USEPA Publication number SW-846, Update IIIA
(April 1998).
GPO. Available from the Superintendent of Documents, U.S.
Government Printing Office, Washington, D.C. 20402,202-512-1800:
Standard Industrial Classification Manual (1972), and 1977
Supplement, republished in 1983.
“Test Methods for Evaluating Solid Waste, Physical/Chemical
Methods”, USEPA Publication number SW-846 (Third Edition,
November, 1986), as amended by Updates I (July, 1992), II
(September, 1994), IIA (August, 1993), IIB (January, 1995), and
III (December, 1996) (Document Number 955-001-00000-1).
92
NACE. Available from the National Association of Corrosion
Engineers, 1400 South Creek Dr., Houston, TX 77084, 713-492-0535:
“Control of External Corrosion on Metallic Buried, Partially
Buried, or Submerged Liquid Storage Systems”, NACE
Recommended Practice RP-02-85, approved March, 1985.
NFPA. Available from the National Fire Protection Association,
Batterymarch Park, Boston, MA 02269, 617-770-3000 or 800-344-3555:
“Flammable and Combustible Liquids Code” NFPA 30, issued
July 17, 1987. Also available from ANSI.
NTIS. Available from the U.S. Department of Commerce, National
Technical Information Service, 5285 Port Royal Road, Springfield, VA
22161, 703-605-6000 or 800-553-6847:
APTI Course 415: Control of Gaseous Emissions, USEPA
Publication EPA-450/2-81-005, December, 1981.
“Generic Quality Assurance Project Plan for Land Disposal
Restrictions Program”, EPA/530-SW-87-011, March 15, 1987
(Document document number PB 88-170766).
“Guideline on Air Quality Models”, Revised 1986. (Document
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 (document number PB99-121949).
“Methods for Chemical Analysis of Water and Wastes”, Third
Edition, March, 1983 (Document document number PB 84-
128677).
“Methods Manual for Compliance with BIF Regulations”,
December, 1990 (Document document number PB91-120-006).
“Petitions to Delist Hazardous Wastes — A Guidance Manual,
Second Edition”, EPA/530-R-93-007, March, 1993 (Document
Number document number PB 93-169 365).
93
“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
document number 955-001-00000-1).
OECD. Organisation for Economic Co-operation and Development,
Environment Directorate, 2 rue Andre Pascal, 75775 Paris Cedex 16,
France):
OECD Guideline for Testing of Chemicals, Method 301B: “CO
2
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).
U.S. DODUSDOD. Available from the United States Department of
Defense:
“DOD Ammunition and Explosive Safety Standards” (DOD
6055.9-STD), as in effect on November 8, 1995.
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.
94
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:
“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 22203 (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).
U.S. GSA. 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:
95
10 CFR 20, Appendix B (19981999)
40 CFR 51.100(ii) (19981999)
40 CFR 51, Appendix W (19981999)
40 CFR 52.741, Appendix B (19981999)
40 CFR 60 (19981999)
40 CFR 61, Subpart V (19981999)
40 CFR 63 (19981999)
40 CFR 136 (19981999), as corrected at 63 Fed. Reg. 38756 (July 20,
1998) and 63 Fed. Reg. 44146 (Aug. 18, 1998) and amended at 63 Fed.
Reg. 50387 (Sep. 21, 1998), 64 Fed. Reg. 4975 (Feb. 2, 1999), 64 Fed.
Reg. 26315 (May 14, 1999), and 64 Fed. Reg. 30417 73414 (June
8December 30, 1999)
40 CFR 142 (19981999)
40 CFR 220 (19981999)
40 CFR 232.2 (19981999)
40 CFR 260.20 (19981999)
40 CFR 264 (19981999)
40 CFR 268.41 (1990)
40 CFR 268.Appendix IX (19981999)
40 CFR 270.5 (19981999)
40 CFR 302.4, 302.5, and 302.6 (19981999)
40 CFR 761 (19981999)
49 CFR 171 (19981999)
49 CFR 173 (19981999)
49 CFR 178 (19981999)
96
c)
Federal Statutes
Section 3004 of the Resource Conservation and Recovery Act (42 USC
6901 et seq.), as amended through December 31, 1987.
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 24 Ill. Reg. ________, effective ______________________)
TITLE 35: ENVIRONMENTAL PROTECTION
SUBTITLE G: WASTE DISPOSAL
CHAPTER I: POLLUTION CONTROL BOARD
SUBCHAPTER c: HAZARDOUS WASTE OPERATING REQUIREMENTS
PART 721
IDENTIFICATION AND LISTING OF HAZARDOUS WASTE
SUBPART A: GENERAL PROVISIONS
Section
721.101
Purpose and Scope
721.102
Definition of Solid Waste
721.103
Definition of Hazardous Waste
721.104
Exclusions
721.105
Special Requirements for Hazardous Waste Generated by Small Quantity
Generators
721.106
Requirements for Recyclable Materials
721.107
Residues of Hazardous Waste in Empty Containers
721.108
PCB Wastes Regulated under TSCA
721.109
Requirements for Universal Waste
SUBPART B: CRITERIA FOR IDENTIFYING THE CHARACTERISTICS
OF HAZARDOUS WASTE AND FOR LISTING HAZARDOUS WASTES
Section
721.110
Criteria for Identifying the Characteristics of Hazardous Waste
721.111
Criteria for Listing Hazardous Waste
97
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)
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.
98
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. ________, effective ______________________.
SUBPART A: GENERAL PROVISIONS
Section 721.109
Requirements for Universal Waste
The wastes listed in this Section are exempt from regulation under 35 Ill. Adm. Code 702
through 705, 722 through 726, and 728, except as specified in 35 Ill. Adm. Code 733, and are
therefore not fully regulated as hazardous waste. The wastes listed in this Section are subject to
regulation under 35 Ill. Adm. Code 733:
a)
Batteries, as described in 35 Ill. Adm. Code 733.102;
b)
Pesticides, as described in 35 Ill. Adm. Code 733.103;
c)
Thermostats, as described in 35 Ill. Adm. Code 733.104; and
99
d)
Mercury-containing lampsLamps, as described in 35 Ill. Adm. Code 733.107
733.105.
BOARD NOTE: Subsection (d) of this Section was added pursuant to Section
22.23a of the Act [415 ILCS 5/22.23a] (see P.A. 90-502, effective August 19,
1997).
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
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)
100
K007
Wastewater treatment sludge from the production of iron blue
pigments.
(T)
K008
Oven residue from the production of chrome oxide green
pigments.
(T)
Organic Chemicals:
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)
101
K023
Distillation light ends from the production of phthalic anhydride
from naphthalene.
(T)
K024
Distillation bottoms from the production of phthalic anhydride
from naphthalene.
(T)
K093
Distillation light ends from the production of phthalic anhydride
from ortho-xylene.
(T)
K094
Distillation bottoms from the production of phthalic anhydride
from ortho-xylene.
(T)
K025
Distillation bottoms from the production of nitrobenzene by the
nitration of benzene.
(T)
K026
Stripping still tails from the production of methyl ethyl pyridines.
(T)
K027
Centrifuge and distillation residues from toluene diisocyanate
production.
(R,T)
K028
Spent catalyst from the hydrochlorinator reactor in the
production of 1,1,1-trichloroethane.
(T)
K029
Waste from the product stream stripper in the production of
1,1,1-trichloroethane.
(T)
K095
Distillation bottoms from the production of 1,1,1-trichloroethane.
(T)
K096
Heavy ends from the heavy ends column from the production of
1,1,1-trichloroethane.
(T)
K030
Column bottoms or heavy ends from the combined production of
trichloroethylene and perchloroethylene.
(T)
K083
Distillation bottoms from aniline production.
(T)
K103
Process residues from aniline extraction from the production of
aniline.
(T)
K104
Combined wastewater streams generated from
nitrobenzene/aniline production.
(T)
K085
Distillation or fractionation column bottoms
from the production of chlorobenzenes.
(T)
102
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)
K115
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 toluenedi-
amine.
(T)
K117
Wastewater from the reactor vent gas scrubber in the production
of ethylene dibromide via bromination of ethene.
(T)
103
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)
K140
Floor sweepings, off-specification product and spent filter media
from the production of 2,4,6-tribromophenol.
(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
Bag house 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)
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)
104
K106
Wastewater treatment sludge from the mercury cell process in
chlorine production.
(T)
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 cyclopenta-
diene 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)
105
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)
K051
API separator sludge from the petroleum refining industry.
(T)
106
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 Copper:
K064
Acid plant blowdown slurry or sludge resulting from the
thickening of blowdown slurry from primary copper production.
(T)
Primary Lead:
K065
Surface impoundment solids contained in and dredged from
surface impoundments at primary lead smelting facilities.
(T)
Primary Zinc:
K066
Sludge from treatment of process wastewater or acid plant
blowdown from primary zinc production.
(T)
BOARD NOTE: This waste listing is the subject of a judicial remand in American Mining
Congress v. EPA, 907 F.2d 1179 (D.D.C. 1990). The Board intends that this listing not
become enforceable in Illinois until the first date upon which the Board RCRA program
becomes “not equivalent to the Federal program”, within the meaning of section 3006(b) of the
107
RCRA Act, 42 USC 6926(b), the Board RCRA rules become “less stringent” than the
USEPA rules, as this phrase is used in section 3009, 42 USC 6929, or the Board RCRA rules
are not “identical in substance” with the federal rules as that term is intended by 415 ILCS
5/7.2 and 22.4 as a result of some action by USEPA with regard to this listing in response to
the American Mining Congress remand.
Primary Aluminum:
K088
Spent potliners from primary aluminum reduction.
(T)
Ferroalloys:
K090
Emission control dust or sludge from ferrochromiumsilicon
production.
(T)
K091
Emission control dust or sludge from ferrochromium production.
(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)
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)
108
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)
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)
109
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 24 Ill. Reg. ________, effective ______________________)
Section 721.133
Discarded Commercial Chemical Products, Off-Specification Species,
Container Residues, and Spill Residues Thereof
The following materials or items are hazardous wastes if and when they are discarded or
intended to be discarded as described in Section 721.102(a)(2)(A), when they are mixed with
waste oil or used oil or other material and applied to the land for dust suppression or road
treatment, when they are otherwise applied to the land in lieu of their original intended use or
when they are contained in products that are applied to land in lieu of their original intended
use, or when, in lieu of their original intended use, they are produced for use as (or as a
component of) a fuel, distributed for use as a fuel, or burned as a fuel.
a)
Any commercial chemical product, or manufacturing chemical intermediate
having the generic name listed in subsection (e) or (f) of this Section.
b)
Any off-specification commercial chemical product or manufacturing chemical
intermediate which that, if it met specifications, would have the generic name
listed in subsection (e) or (f) of this Section.
c)
Any residue remaining in a container or inner liner removed from a container
that has held any commercial chemical product or manufacturing chemical
intermediate having the generic name listed in subsection (e) or (f) of this
Section, unless the container is empty, as defined in Section 721.107(b)(3).
BOARD NOTE: Unless the residue is being beneficially used or reused,; or
legitimately recycled or reclaimed,; or being accumulated, stored, transported, or
treated prior to such use, reuse, recycling, or reclamation, the Board considers
the residue to be intended for discard, and thus a hazardous waste. An example
of a legitimate reuse of the residue would be where the residue remains in the
container and the container is used to hold the same commercial chemical
product or manufacturing chemical intermediate it previously held. An example
of the discard of the residue would be where the drum is sent to a drum
110
reconditioner that reconditions the drum but discards the residue.
d)
Any residue or contaminated soil, water, or other debris resulting from the
cleanup of a spill into or on any land or water of any commercial chemical
product or manufacturing chemical intermediate having the generic name listed in
subsection (e) or (f) of this Section, or any residue or contaminated soil, water,
or other debris resulting from the cleanup of a spill into or on any land or water,
of any off-specification chemical product or manufacturing chemical intermediate
which that, if it met specifications, would have the generic name listed in
subsection (e) or (f) of this Section.
BOARD NOTE: The phrase “commercial chemical product or manufacturing
chemical intermediate having the generic name listed in ...” refers to a chemical
substance that is manufactured or formulated for commercial or manufacturing
use which consists of the commercially pure grade of the chemical, any technical
grades of the chemical that are produced or marketed, and all formulations in
which the chemical is the sole active ingredient. It does not refer to a material,
such as a manufacturing process waste, that contains any of the substances listed
in subsection (e) or (f) of this Section. Where a manufacturing process waste is
deemed to be a hazardous waste because it contains a substance listed in
subsection (e) or (f) of this Section, such waste will be listed in either Sections
721.131 or 721.132 or will be identified as a hazardous waste by the
characteristics set forth in Subpart C of this Part.
e)
The commercial chemical products, manufacturing chemical intermediates, or
off-specification commercial chemical products or manufacturing chemical
intermediates referred to in subsections (a) through (d) of this Section, are
identified as acute hazardous waste (H) and are subject to the small quantity
exclusion defined in Section 721.105(e). These wastes and their corresponding
USEPA Hazardous Waste Numbers are the following:
BOARD NOTE: For the convenience of the regulated community, the primary
hazardous properties of these materials have been indicated by the letters T
(Toxicity), and R (Reactivity). The absence of a letter indicates that the
compound only is only listed for acute toxicity.
USEPA
Hazardous
Waste No.
Chemical
Abstracts No.
(CAS No.)
Substance
P023
107-20-0
Acetaldehyde, chloro-
P002
591-08-2
Acetamide, N-(aminothioxomethyl)
P057
640-19-7
Acetamide, 2-fluoro-
P058
62-74-8
Acetic acid, fluoro-, sodium salt
P002
591-08-2
1-Acetyl-2-thiourea
111
P003
107-02-8
Acrolein
P070
116-06-3
Aldicarb
P203
1646-88-4
Aldicarb sulfone
P004
309-00-2
Aldrin
P005
107-18-6
Allyl alcohol
P006
20859-73-8
Aluminum phosphide (R,T)
P007
2763-96-4
5-(Aminomethyl)-3-isoxazolol
P008
504-24-5
4-Aminopyridine
P009
131-74-8
Ammonium picrate (R)
P119
7803-55-6
Ammonium vanadate
P099
506-61-6
Argentate(1-), bis(cyano-C)-, potassium
P010
7778-39-4
Arsenic acid H
3
AsO
4
P012
1327-53-3
Arsenic oxide As
2
O
3
P011
1303-28-2
Arsenic oxide As
2
O
5
P011
1303-28-2
Arsenic pentoxide
P012
1327-53-3
Arsenic trioxide
P038
692-42-2
Arsine, diethyl-
P036
696-28-6
Arsonous dichloride, phenyl-
P054
151-56-4
Aziridine
P067
75-55-8
Aziridine, 2-methyl
P013
542-62-1
Barium cyanide
P024
106-47-8
Benzenamine, 4-chloro-
P077
100-01-6
Benzenamine, 4-nitro-
P028
100-44-7
Benzene, (chloromethyl)-
P042
51-43-4
1,2-Benzenediol, 4-[1-hydroxy-2-(methylamino)-
ethyl]-, (R)-
P046
122-09-8
Benzeneethanamine,
α
,
α
-dimethyl-
P014
108-98-5
Benzenethiol
P127
1563-66-2
7-Benzofuranol, 2,3-dihydro-2,2-dimethyl-,
methylcarbamate
P188
57-64-7
Benzoic acid, 2-hydroxy-, compound with (3aS-
cis)-1,2,3,3a,8,8a-hexahydro-1,3a,8-trimethyl-
pyrrolo[2,3-b]indol-5-yl methylcarbamate ester
(1:1)
P001
81-81-2
*
2H-1-Benzopyran-2-one, 4-hydroxy-3-(3-oxo-1-
phenylbutyl)-, and salts, when present at
concentrations greater than 0.3 percent
P028
100-44-7
Benzyl chloride
P015
7440-41-7
Beryllium powder
P017
598-31-2
Bromoacetone
P018
357-57-3
Brucine
P045
39196-18-6
2-Butanone,3,3-dimethyl-1-(methylthio)-, O-
[methylamino)carbonyl] oxime
P021
592-01-8
Calcium cyanide
P021
592-01-8
Calcium cyanide Ca(CN)
2
112
P189
55285-14-8
Carbamic acid, [(dibutylamino)- thio]methyl-,
2,3-dihydro-2,2-dimethyl-7-benzofuranyl ester
P191
644-64-4
Carbamic acid, dimethyl-, 1-[(dimethyl-amino)-
carbonyl]-5-methyl-1H-pyrazol-3-yl ester
P192
119-38-0
Carbamic acid, dimethyl-, 3-methyl-1-(1-methyl-
ethyl)-1H-pyrazol-5-yl ester
P190
1129-41-5
Carbamic acid, methyl-, 3-methylphenyl ester
P127
1563-66-2
Carbofuran
P022
75-15-0
Carbon disulfide
P095
75-44-5
Carbonic dichloride
P189
55285-14-8
Carbosulfan
P023
107-20-0
Chloroacetaldehyde
P024
106-47-8
p-Chloroaniline
P026
5344-82-1
1-(o-Chlorophenyl)thiourea
P027
542-76-7
3-Chloropropionitrile
P029
544-92-3
Copper cyanide
P029
544-92-3
Copper cyanide CuCN
P202
64-00-6
m-Cumenyl methylcarbamate
P030
Cyanides (soluble cyanide salts), not otherwise
specified
P031
460-19-5
Cyanogen
P033
506-77-4
Cyanogen chloride
P033
506-77-4
Cyanogen chloride CNCl
P034
131-89-5
2-Cyclohexyl-4,6-dinitrophenol
P016
542-88-1
Dichloromethyl ether
P036
696-28-6
Dichlorophenylarsine
P037
60-57-1
Dieldrin
P038
692-42-2
Diethylarsine
P041
311-45-5
Diethyl-p-nitrophenyl phosphate
P040
297-97-2
O,O-Diethyl O-pyrazinyl phosphorothioate
P043
55-91-4
Diisopropylfluorophosphate (DFP)
P191
644-64-4
Dimetilan
P004
309-00-2
1,4,5,8-Dimethanonaphthalene, 1,2,3,4,10,10-
hexachloro-1,4,4a,5,8,8a-hexahydro-,
(1
α
,4
α
,4a
β
,5
α
,8
α
,8a
β
)-
P060
465-73-6
1,4,5,8-Dimethanonaphthalene, 1,2,3,4,10,10-
hexachloro-1,4,4a,5,8,8a-hexahydro-,
(1
α
,4
α
,4a
β
,5
β
,8
β
,8a
β
)-
P037
60-57-1
2,7:3,6-Dimethanonaphth[2,3-b]oxirene,
3,4,5,6,9,9-hexachloro-1a,2,2a,3,6,6a,7,7a-
octahydro-, (1a
α
,2
β
,2a
α
,3
β
,6
β
,6a
α
,7
β
,7a
α
)-
P051
72-20-8
*
2,7:3,6-Dimethanonaphth[2,3-b]oxirene,
3,4,5,6,9,9-hexachloro-1a,2,2a,3,6,6a,7,7a-
octahydro-, (1a
α
,2
β
,2a
β
,3
α
,6
α
,6a
β
,7
β
,7a
α
)-,
and metabolites
113
P044
60-51-5
Dimethoate
P046
122-09-8
α
,
α
-Dimethylphenethylamine
P047
534-52-1
*
4,6-Dinitro-o-cresol and salts
P048
51-28-5
2,4-Dinitrophenol
P020
88-85-7
Dinoseb
P085
152-16-9
Diphosphoramide, octamethyl-
P111
107-49-3
Diphosphoric acid, tetraethyl ester
P039
298-04-4
Disulfoton
P049
541-53-7
Dithiobiuret
P185
26419-73-8
1,3-Dithiolane-2-carboxaldehyde, 2,4-dimethyl-,
O-[(methylamino)- carbonyl]oxime
P050
115-29-7
Endosulfan
P088
145-73-3
Endothall
P051
72-20-8
Endrin
P051
72-20-8
Endrin, and metabolites
P042
51-43-4
Epinephrine
P031
460-19-5
Ethanedinitrile
P194
23135-22-0
Ethanimidothioc acid, 2-(dimethylamino)-N-
[[(methylamino)carbonyl]oxy]-2-oxo-, methyl
ester
P066
16752-77-5
Ethanimidothioic acid, N-[[(methylamino)-
carbonyl]oxy]-, methyl ester
P101
107-12-0
Ethyl cyanide
P054
151-56-4
Ethylenimine
P097
52-85-7
Famphur
P056
7782-41-4
Fluorine
P057
640-19-7
Fluoroacetamide
P058
62-74-8
Fluoroacetic acid, sodium salt
P198
23422-53-9
Formetanate hydrochloride
P197
17702-57-7
Formparanate
P065
628-86-4
Fulminic acid, mercury (2+) salt (R,T)
P059
76-44-8
Heptachlor
P062
757-58-4
Hexaethyl tetraphosphate
P116
79-19-6
Hydrazinecarbothioamide
P068
60-34-4
Hydrazine, methyl-
P063
74-90-8
Hydrocyanic acid
P063
74-90-8
Hydrogen cyanide
P096
7803-51-2
Hydrogen phosphide
P060
465-73-6
Isodrin
P192
119-38-0
Isolan
P202
64-00-6
3-Isopropylphenyl-N-methylcarbamate
P007
2763-96-4
3(2H)-Isoxazolone, 5-(aminomethyl)-
P196
15339-36-3
Manganese, bis(dimethylcarbamodithioato-S,S’)-
P196
15339-36-3
Manganese dimethyldithiocarbamate
P092
62-38-4
Mercury, (acetato-O)phenyl-
114
P065
628-86-4
Mercury fulminate (R,T)
P082
62-75-9
Methanamine, N-methyl-N-nitroso-
P064
624-83-9
Methane, isocyanato-
P016
542-88-1
Methane, oxybis[chloro-
P112
509-14-8
Methane, tetranitro- (R)
P118
75-70-7
Methanethiol, trichloro-
P198
23422-53-9
Methanimidamide, N,N-dimethyl-N’-[3-
[[(methylamino)-carbonyl]oxy]phenyl]-,
monohydrochloride
P197
17702-57-7
Methanimidamide, N,N-dimethyl-N’-[2-methyl-
4-[[(methylamino)carbonyl]oxy]phenyl]-
P199
2032-65-7
Methiocarb
P050
115-29-7
6,9-Methano-2,4,3-benzodioxathiepen,
6,7,8,9,10,10-hexachloro-1,5,5a,6,9,9a-hexa-
hydro-, 3-oxide
P059
76-44-8
4,7-Methano-1H-indene, 1,4,5,6,7,8,8-hepta-
chloro-3a,4,7,7a-tetrahydro-
P066
16752-77-5
Methomyl
P068
60-34-4
Methyl hydrazine
P064
624-83-9
Methyl isocyanate
P069
75-86-5
2-Methyllactonitrile
P071
298-00-0
Methyl parathion
P190
1129-41-5
Metolcarb
P129
315-8-4
Mexacarbate
P072
86-88-4
α
-Naphthylthiourea
P073
13463-39-3
Nickel carbonyl
P073
13463-39-3
Nickel carbonyl Ni(CO)
4
, (T-4)-
P074
557-19-7
Nickel cyanide
P074
557-19-7
Nickel cyanide Ni(CN)
2
P075
54-11-5
*
Nicotine, and salts
P076
10102-43-9
Nitric oxide
P077
100-01-6
p-Nitroaniline
P078
10102-44-0
Nitrogen dioxide
P076
10102-43-9
Nitrogen oxide NO
P078
10102-44-0
Nitrogen oxide NO
2
P081
55-63-0
Nitroglycerine (R)
P082
62-75-9
N-Nitrosodimethylamine
P084
4549-40-0
N-Nitrosomethylvinylamine
P085
152-16-9
Octamethylpyrophosphoramide
P087
20816-12-0
Osmium oxide OsO
4
, (T-4)-
P087
20816-12-0
Osmium tetroxide
P088
145-73-3
7-Oxabicyclo[2.2.1]heptane-2,3-dicarboxylic
acid
P194
23135-22-0
Oxamyl
P089
56-38-2
Parathion
115
P034
131-89-5
Phenol, 2-cyclohexyl-4,6-dinitro-
P128
315-18-4
Phenol, 4-(dimethylamino)-3,5-dimethyl-,
methylcarbamate (ester)
P199
2032-65-7
Phenol, (3,5-dimethyl-4-(methylthio)-, methyl-
carbamate
P048
51-28-5
Phenol, 2,4-dinitro-
P047
534-52-1
*
Phenol, 2-methyl-4,6-dinitro-, and salts
P202
64-00-6
Phenol, 3-(1-methylethyl)-, methyl carbamate
P201
2631-37-0
Phenol, 3-methyl-5-(1-methylethyl)-, methyl
carbamate
P020
88-85-7
Phenol, 2-(1-methylpropyl)-4,6-dinitro-
P009
131-74-8
Phenol, 2,4,6-trinitro-, ammonium salt (R)
P092
62-38-4
Phenylmercury acetate
P093
103-85-5
Phenylthiourea
P094
298-02-2
Phorate
P095
75-44-5
Phosgene
P096
7803-51-2
Phosphine
P041
311-45-5
Phosphoric acid, diethyl 4-nitrophenyl ester
P039
298-04-4
Phosphorodithioic acid, O,O-diethyl S-[2-(ethyl-
thio)ethyl] ester
P094
298-02-2
Phosphorodithioic acid, O,O-diethyl S-[(ethyl-
thio)methyl] ester
P044
60-51-5
Phosphorodithioic acid, O,O-dimethyl S-[2-
(methylamino)-2-oxoethyl]ester
P043
55-91-4
Phosphorofluoridic acid, bis(1-methylethyl)ester
P089
56-38-2
Phosphorothioic acid, O,O-diethyl O-(4-
nitrophenyl) ester
P040
297-97-2
Phosphorothioic acid, O,O-diethyl O-pyrazinyl
ester
P097
52-85-7
Phosphorothioic acid, O-[4-[(dimethylamino)-
sulfonyl)]phenyl] O,O-dimethyl ester
P071
298-00-0
Phosphorothioic acid, O,O-dimethyl O-(4-
nitrophenyl) ester
P204
57-47-6
Physostigmine
P188
57-64-7
Physostigmine salicylate
P110
78-00-2
Plumbane, tetraethyl-
P098
151-50-8
Potassium cyanide
P098
151-50-8
Potassium cyanide KCN
P099
506-61-6
Potassium silver cyanide
P201
2631-37-0
Promecarb
P203
1646-88-4
Propanal, 2-methyl-2-(methyl-sulfonyl)-, O-
[(methylamino)carbonyl] oxime
P070
116-06-3
Propanal, 2-methyl-2-(methylthio)-, O-[(methyl-
amino)carbonyl]oxime
P101
107-12-0
Propanenitrile
116
P027
542-76-7
Propanenitrile, 3-chloro-
P069
75-86-5
Propanenitrile, 2-hydroxy-2-methyl-
P081
55-63-0
1,2,3-Propanetriol, trinitrate- (R)
P017
598-31-2
2-Propanone, 1-bromo-
P102
107-19-7
Propargyl alcohol
P003
107-02-8
2-Propenal
P005
107-18-6
2-Propen-1-ol
P067
75-55-8
1,2-Propylenimine
P102
107-19-7
2-Propyn-1-ol
P008
504-24-5
4-Pyridinamine
P075
54-11-5
*
Pyridine, 3-(1-methyl-2-pyrrolidinyl)-, (S)- and
salts
P204
57-47-6
Pyrrolo[2,3-b]indol-5-ol, 1,2,3,3a,8,8a-hexa-
hydro-1,3a,8-trimethyl-, methylcarbamate
(ester), (3aS-cis)-
P114
12039-52-0
Selenious acid, dithallium (1+) salt
P103
630-10-4
Selenourea
P104
506-64-9
Silver cyanide
P104
506-64-9
Silver cyanide AgCN
P105
26628-22-8
Sodium azide
P106
143-33-9
Sodium cyanide
P106
143-33-9
Sodium cyanide NaCN
P108
57-24-9
*
Strychnidin-10-one, and salts
P018
357-57-3
Strychnidin-10-one, 2,3-dimethoxy-
P108
57-24-9
*
Strychnine and salts
P115
7446-18-6
Sulfuric acid, dithallium (1+) salt
P109
3689-24-5
Tetraethyldithiopyrophosphate
P110
78-00-2
Tetraethyl lead
P111
107-49-3
Tetraethylpyrophosphate
P112
509-14-8
Tetranitromethane (R)
P062
757-58-4
Tetraphosphoric acid, hexaethyl ester
P113
1314-32-5
Thallic oxide
P113
1314-32-5
Thallium oxide Tl
2
O
3
P114
12039-52-0
Thallium (I) selenite
P115
7446-18-6
Thallium (I) sulfate
P109
3689-24-5
Thiodiphosphoric acid, tetraethyl ester
P045
39196-18-4
Thiofanox
P049
541-53-7
Thioimidodicarbonic diamide [(H
2
N)C(S)]
2
NH
P014
108-98-5
Thiophenol
P116
79-19-6
Thiosemicarbazide
P026
5344-82-1
Thiourea, (2-chlorophenyl)-
P072
86-88-4
Thiourea, 1-naphthalenyl-
P093
103-85-5
Thiourea, phenyl-
P123
8001-35-2
Toxaphene
P185
26419-73-8
Tirpate
117
P118
75-70-7
Trichloromethanethiol
P119
7803-55-6
Vanadic acid, ammonium salt
P120
1314-62-1
Vanadium oxide V
2
O
5
P120
1314-62-1
Vanadium pentoxide
P084
4549-40-0
Vinylamine, N-methyl-N-nitroso-
P001
81-81-2
*
Warfarin, and salts, when present at
concentrations greater than 0.3 percent
P121
557-21-1
Zinc cyanide
P121
557-21-1
Zinc cyanide Zn(CN)
2
P205
137-30-4
Zinc, bis(dimethylcarbamodithioato-S,S’)-
P122
1314-84-7
Zinc phosphide Zn
3
P
2
, when present at
concentrations greater than 10 percent (R,T)
P205
137-30-4
Ziram
BOARD NOTE: An asterisk (*) following the CAS number indicates that the
CAS number is given for the parent compound only.
f)
The commercial chemical products, manufacturing chemical intermediates, or
off-specification commercial chemical products referred to in subsections (a)
through (d) of this Section, are identified as toxic wastes (T) unless otherwise
designated and are subject to the small quantity exclusion defined in Section
721.105(a) and (g). These wastes and their corresponding USEPA Hazardous
Waste Numbers are the following:
BOARD NOTE: For the convenience of the regulated community, the primary
hazardous properties of these materials have been indicated by the letters T
(Toxicity), R (Reactivity), I (Ignitability), and C (Corrosivity). The absence of a
letter indicates that the compound is only listed for toxicity.
USEPA
Hazardous
Waste No.
Chemical
Abstracts No.
(CAS No.)
Substance
U394
30558-43-1
A2213
U001
75-07-0
Acetaldehyde (I)
U034
75-87-6
Acetaldehyde, trichloro-
U187
62-44-2
Acetamide, N-(4-ethoxyphenyl)-
U005
53-96-3
Acetamide, N-9H-fluoren-2-yl-
U240
P 94-75-7
Acetic acid, (2,4-dichlorophenoxy)-, salts and
esters
U112
141-78-6
Acetic acid, ethyl ester (I)
U144
301-04-2
Acetic acid, lead (2+) salt
U214
563-68-8
Acetic acid, thallium (1+) salt
See F027
93-76-5
Acetic acid, (2,4,5-trichlorophenoxy)-
U002
67-64-1
Acetone (I)
118
U003
75-05-8
Acetonitrile (I,T)
U004
98-86-2
Acetophenone
U005
53-96-3
2-Acetylaminofluorene
U006
75-36-5
Acetyl chloride (C,R,T)
U007
79-06-1
Acrylamide
U008
79-10-7
Acrylic acid (I)
U009
107-13-1
Acrylonitrile
U011
61-82-5
Amitrole
U012
62-53-3
Aniline (I,T)
U136
75-60-5
Arsinic acid, dimethyl-
U014
492-80-8
Auramine
U015
115-02-6
Azaserine
U010
50-07-7
Azirino[2',3':3,4]pyrrolo[1,2-a]indole-4,7-dione,
6-amino-8-[[(aminocarbonyl)oxy]methyl]-
1,1a,2,8,8a,8b-hexahydro-8a-methoxy-5-methyl-
, [1a-S-(1a
α
,8
β
,8a
α
,8b
α
)]-
U280
101-27-9
Barban
U278
22781-23-3
Bendiocarb
U364
22961-82-6
Bendiocarb phenol
U271
17804-35-2
Benomyl
U157
56-49-5
Benz[j]aceanthrylene, 1,2-dihydro-3-methyl-
U016
225-51-4
Benz(c)acridine
U017
98-87-3
Benzal chloride
U192
23950-58-5
Benzamide, 3,5-dichloro-N-(1,1-dimethyl-2-
propynyl)-
U018
56-55-3
Benz[a]anthracene
U094
57-97-6
Benz[a]anthracene, 7,12-dimethyl-
U012
62-53-3
Benzenamine (I,T)
U014
492-80-8
Benzenamine, 4,4'-carbonimidoylbis[N,N-di-
methyl-
U049
3165-93-3
Benzenamine, 4-chloro-2-methyl-, hydrochloride
U093
60-11-7
Benzenamine, N,N-dimethyl-4-(phenylazo)-
U328
95-53-4
Benzenamine, 2-methyl-
U353
106-49-0
Benzenamine, 4-methyl-
U158
101-14-4
Benzenamine, 4,4'-methylenebis[2-chloro-
U222
636-21-5
Benzenamine, 2-methyl-, hydrochloride
U181
99-55-8
Benzenamine, 2-methyl-5-nitro-
U019
71-43-2
Benzene (I,T)
U038
510-15-6
Benzeneacetic acid, 4-chloro-
α
-(4-chloro-
phenyl)-
α
-hydroxy-, ethyl ester
U030
101-55-3
Benzene, 1-bromo-4-phenoxy-
U035
305-03-3
Benzenebutanoic acid, 4-[bis(2-chloroethyl)-
amino]-
U037
108-90-7
Benzene, chloro-
U221
25376-45-8
Benzenediamine, ar-methyl-
119
U028
117-81-7
1,2-Benzenedicarboxylic acid, bis(2-ethylhexyl)
ester
U069
84-74-2
1,2-Benzenedicarboxylic acid, dibutyl ester
U088
84-66-2
1,2-Benzenedicarboxylic acid, diethyl ester
U102
131-11-3
1,2-Benzenedicarboxylic acid, dimethyl ester
U107
117-84-0
1,2-Benzenedicarboxylic acid, dioctyl ester
U070
95-50-1
Benzene, 1,2-dichloro-
U071
541-73-1
Benzene, 1,3-dichloro-
U072
106-46-7
Benzene, 1,4-dichloro-
U060
72-54-8
Benzene, 1,1'-(2,2-dichloroethylidene)bis[4-
chloro-
U017
98-87-3
Benzene, (dichloromethyl)-
U223
26471-62-5
Benzene, 1,3-diisocyanatomethyl- (R,T)
U239
1330-20-7
Benzene, dimethyl- (I,T)
U201
108-46-3
1,3-Benzenediol
U127
118-74-1
Benzene, hexachloro-
U056
110-82-7
Benzene, hexahydro- (I)
U220
108-88-3
Benzene, methyl-
U105
121-14-2
Benzene, 1-methyl-2,4-dinitro-
U106
606-20-2
Benzene, 2-methyl-1,3-dinitro-
U055
98-82-8
Benzene, (1-methylethyl)- (I)
U169
98-95-3
Benzene, nitro-
U183
608-93-5
Benzene, pentachloro-
U185
82-68-8
Benzene, pentachloronitro-
U020
98-09-9
Benzenesulfonic acid chloride (C,R)
U020
98-09-9
Benzenesulfonyl chloride (C,R)
U207
95-94-3
Benzene, 1,2,4,5-tetrachloro-
U061
50-29-3
Benzene, 1,1'-(2,2,2-trichloroethylidene)bis[4-
chloro-
U247
72-43-5
Benzene, 1,1'-(2,2,2-trichloroethylidene)bis[4-
methoxy-
U023
98-07-7
Benzene, (trichloromethyl)-
U234
99-35-4
Benzene, 1,3,5-trinitro-
U021
92-87-5
Benzidene
U202
P 81-07-2
1,2-Benzisothiazol-3(2H)-one, 1,1-dioxide, and
salts
U203
94-59-7
1,3-Benzodioxole, 5-(2-propenyl)-
U141
120-58-1
1,3-Benzodioxole, 5-(1-propenyl)-
U090
94-58-6
1,3-Benzodioxole, 5-propyl-
U278
22781-23-3
1,3-Benzodioxol-4-ol, 2,2-dimethyl-, methyl
carbamate
U364
22961-82-6
1,3-Benzodioxol-4-ol, 2,2-dimethyl-
U367
1563-38-8
7-Benzofuranol, 2,3-dihydro-2,2-dimethyl-
U064
189-55-9
Benzo[rst]pentaphene
120
U248
P 81-81-2
2H-1-Benzopyran-2-one, 4-hydroxy-3-(3-oxo-1-
phenylbutyl)-, and salts, when present at
concentrations of 0.3 percent or less
U022
50-32-8
Benzo[a]pyrene
U197
106-51-4
p-Benzoquinone
U023
98-07-7
Benzotrichloride (C,R,T)
U085
1464-53-5
2,2'-Bioxirane
U021
92-87-5
[1,1'-Biphenyl]-4,4'-diamine
U073
91-94-1
[1,1'-Biphenyl]-4,4'-diamine, 3,3'-dichloro-
U091
119-90-4
[1,1'-Biphenyl]-4,4'-diamine, 3,3'-dimethoxy-
U095
119-93-7
[1,1'-Biphenyl]-4,4'-diamine, 3,3'-dimethyl-
U225
75-25-2
Bromoform
U030
101-55-3
4-Bromophenyl phenyl ether
U128
87-68-3
1,3-Butadiene, 1,1,2,3,4,4-hexachloro-
U172
924-16-3
1-Butanamine, N-butyl-N-nitroso-
U031
71-36-3
1-Butanol (I)
U159
78-93-3
2-Butanone (I,T)
U160
1338-23-4
2-Butanone, peroxide (R,T)
U053
4170-30-3
2-Butenal
U074
764-41-0
2-Butene, 1,4-dichloro- (I,T)
U143
303-34-4
2-Butenoic acid, 2-methyl-, 7-[[2,3-dihydroxy-2-
(1-methoxyethyl)-3-methyl-1-oxobutoxy]methyl]-
2,3,5,7a-tetrahydro-1H-pyrrolizin-1-yl ester,
[1S-[1
α
(Z), 7(2S*,3R*), 7a
α
]]-
U031
71-36-3
n-Butyl alcohol (I)
U136
75-60-5
Cacodylic acid
U032
13765-19-0
Calcium chromate
U372
10605-21-7
Carbamic acid, 1H-benzimidazol-2-yl, methyl
ester
U271
17804-35-2
Carbamic acid, [1-[(butylamino)carbonyl]-1H-
benzimidazol-2-yl]-, methyl ester
U280
101-27-9
Carbamic acid, (3-chlorophenyl)-, 4-chloro-2-
butynyl ester
U238
51-79-6
Carbamic acid, ethyl ester
U178
615-53-2
Carbamic acid, methylnitroso-, ethyl ester
U373
122-42-9
Carbamic acid, phenyl-, 1-methylethyl ester
U409
23564-05-8
Carbamic acid, [1,2-phenylenebis(iminocarbono-
thioyl)]bis-, dimethyl ester
U097
79-44-7
Carbamic chloride, dimethyl-
U114
P 111-54-6
Carbamodithioic acid, 1,2-ethanediylbis-, salts
and esters
U062
2303-16-4
Carbamothioic acid, bis(1-methylethyl)-, S-(2,3-
dichloro-2-propenyl) ester
U389
2303-17-5
Carbamothioic acid, bis(1-methylethyl)-, S-
(2,3,3-trichloro-2-propenyl) ester
121
U387
52888-80-9
Carbamothioic acid, dipropyl-, S-(phenylmethyl)
ester
U279
63-25-2
Carbaryl
U372
10605-21-7
Carbendazim
U367
1563-38-8
Carbofuran phenol
U215
6533-73-9
Carbonic acid, dithallium (1+) salt
U033
353-50-4
Carbonic difluoride
U156
79-22-1
Carbonochloridic acid, methyl ester (I,T)
U033
353-50-4
Carbon oxyfluoride (R,T)
U211
56-23-5
Carbon tetrachloride
U034
75-87-6
Chloral
U035
305-03-3
Chlorambucil
U036
57-74-9
Chlordane,
α
and
γ
isomers
U026
494-03-1
Chlornaphazin
U037
108-90-7
Chlorobenzene
U038
510-15-6
Chlorobenzilate
U039
59-50-7
p-Chloro-m-cresol
U042
110-75-8
2-Chloroethyl vinyl ether
U044
67-66-3
Chloroform
U046
107-30-2
Chloromethyl methyl ether
U047
91-58-7
β
-Chloronaphthalene
U048
95-57-8
o-Chlorophenol
U049
3165-93-3
4-Chloro-o-toluidine, hydrochloride
U032
13765-19-0
Chromic acid H
2
CrO
4
, calcium salt
U050
218-01-9
Chrysene
U051
Creosote
U052
1319-77-3
Cresol (Cresylic acid)
U053
4170-30-3
Crotonaldehyde
U055
98-82-8
Cumeme (I)
U246
506-68-3
Cyanogen bromide CNBr
U197
106-51-4
2,5-Cyclohexadiene-1,4-dione
U056
110-82-7
Cyclohexane (I)
U129
58-89-9
Cyclohexane, 1,2,3,4,5,6-hexachloro-,
(1
α
,2
α
,3
β
,4
α
,5
α
,6
β
)-
U057
108-94-1
Cyclohexanone (I)
U130
77-47-4
1,3-Cyclopentadiene, 1,2,3,4,5,5-hexachloro-
U058
50-18-0
Cyclophosphamide
U240
P 94-75-7
2,4-D, salts and esters
U059
20830-81-3
Daunomycin
U060
72-54-8
DDD
U061
50-29-3
DDT
U062
2303-16-4
Diallate
U063
53-70-3
Dibenz[a,h]anthracene
U064
189-55-9
Dibenzo[a,i]pyrene
U066
96-12-8
1,2-Dibromo-3-chloropropane
122
U069
84-74-2
Dibutyl phthalate
U070
95-50-1
o-Dichlorobenzene
U071
541-73-1
m-Dichlorobenzene
U072
106-46-7
p-Dichlorobenzene
U073
91-94-1
3,3'-Dichlorobenzidine
U074
764-41-0
1,4-Dichloro-2-butene (I,T)
U075
75-71-8
Dichlorodifluoromethane
U078
75-35-4
1,1-Dichloroethylene
U079
156-60-5
1,2-Dichloroethylene
U025
111-44-4
Dichloroethyl ether
U027
108-60-1
Dichloroisopropyl ether
U024
111-91-1
Dichloromethoxy ethane
U081
120-83-2
2,4-Dichlorophenol
U082
87-65-0
2,6-Dichlorophenol
U084
542-75-6
1,3-Dichloropropene
U085
1464-53-5
1,2:3,4-Diepoxybutane (I,T)
U395
5952-26-1
Diethylene glycol, dicarbamate
U108
123-91-1
1,4-Diethyleneoxide
U028
117-81-7
Diethylhexyl phthalate
U086
1615-80-1
N,N’-Diethylhydrazine
U087
3288-58-2
O,O-Diethyl S-methyl dithiophosphate
U088
84-66-2
Diethyl phthalate
U089
56-53-1
Diethylstilbestrol
U090
94-58-6
Dihydrosafrole
U091
119-90-4
3,3'-Dimethoxybenzidine
U092
124-40-3
Dimethylamine (I)
U093
60-11-7
p-Dimethylaminoazobenzene
U094
57-97-6
7,12-Dimethylbenz[a]anthracene
U095
119-93-7
3,3'-Dimethylbenzidine
U096
80-15-9
α
,
α
-Dimethylbenzylhydroperoxide (R)
U097
79-44-7
Dimethylcarbamoyl chloride
U098
57-14-7
1,1-Dimethylhydrazine
U099
540-73-8
1,2-Dimethylhydrazine
U101
105-67-9
2,4-Dimethylphenol
U102
131-11-3
Dimethyl phthalate
U103
77-78-1
Dimethyl sulfate
U105
121-14-2
2,4-Dinitrotoluene
U106
606-20-2
2,6-Dinitrotoluene
U107
117-84-0
Di-n-octyl phthalate
U108
123-91-1
1,4-Dioxane
U109
122-66-7
1,2-Diphenylhydrazine
U110
142-84-7
Dipropylamine (I)
U111
621-64-7
Di-n-propylnitrosamine
U041
106-89-8
Epichlorohydrin
U001
75-07-0
Ethanal (I)
123
U404
121-44-8
Ethanamine, N,N-diethyl-
U174
55-18-5
Ethanamine, N-ethyl-N-nitroso-
U155
91-80-5
1,2-Ethanediamine, N,N-dimethyl-N’-2-
pyridinyl-N’-(2-thienylmethyl)-
U067
106-93-4
Ethane, 1,2-dibromo-
U076
75-34-3
Ethane, 1,1-dichloro-
U077
107-06-2
Ethane, 1,2-dichloro-
U131
67-72-1
Ethane, hexachloro-
U024
111-91-1
Ethane, 1,1'-[methylenebis(oxy)]bis[2-chloro-
U117
60-29-7
Ethane, 1,1'-oxybis- (I)
U025
111-44-4
Ethane, 1,1'-oxybis[2-chloro-
U184
76-01-7
Ethane, pentachloro-
U208
630-20-6
Ethane, 1,1,1,2-tetrachloro-
U209
79-34-5
Ethane, 1,1,2,2-tetrachloro-
U218
62-55-5
Ethanethioamide
U226
71-55-6
Ethane, 1,1,1-trichloro-
U227
79-00-5
Ethane, 1,1,2-trichloro-
U410
59669-26-0
Ethanimidothioic acid, N,N’- [thiobis[(methyl-
imino)carbonyloxy]]bis-, dimethyl ester
U394
30558-43-1
Ethanimidothioic acid, 2-(dimethylamino)-N-
hydroxy-2-oxo-, methyl ester
U359
110-80-5
Ethanol, 2-ethoxy-
U173
1116-54-7
Ethanol, 2,2'-(nitrosoimino)bis-
U395
5952-26-1
Ethanol, 2,2'-oxybis-, dicarbamate
U004
98-86-2
Ethanone, 1-phenyl-
U043
75-01-4
Ethene, chloro-
U042
110-75-8
Ethene, (2-chloroethoxy)-
U078
75-35-4
Ethene, 1,1-dichloro-
U079
156-60-5
Ethene, 1,2-dichloro-, (E)-
U210
127-18-4
Ethene, tetrachloro-
U228
79-01-6
Ethene, trichloro-
U112
141-78-6
Ethyl acetate (I)
U113
140-88-5
Ethyl acrylate (I)
U238
51-79-6
Ethyl carbamate (urethane)
U117
60-29-7
Ethyl ether
U114
P 111-54-6
Ethylenebisdithiocarbamic acid, salts and esters
U067
106-93-4
Ethylene dibromide
U077
107-06-2
Ethylene dichloride
U359
110-80-5
Ethylene glycol monoethyl ether
U115
75-21-8
Ethylene oxide (I,T)
U116
96-45-7
Ethylenethiourea
U076
75-34-3
Ethylidene dichloride
U118
97-63-2
Ethyl methacrylate
U119
62-50-0
Ethyl methanesulfonate
U120
206-44-0
Fluoranthene
124
U122
50-00-0
Formaldehyde
U123
64-18-6
Formic acid (C,T)
U124
110-00-9
Furan (I)
U125
98-01-1
2-Furancarboxaldehyde (I)
U147
108-31-6
2,5-Furandione
U213
109-99-9
Furan, tetrahydro- (I)
U125
98-01-1
Furfural (I)
U124
110-00-9
Furfuran (I)
U206
18883-66-4
Glucopyranose, 2-deoxy-2-(3-methyl-3-nitroso-
ureido)-, D-
U206
18883-66-4
D-Glucose, 2-deoxy-2-[[(methylnitrosoamino)-
carbonyl]amino]-
U126
765-34-4
Glycidylaldehyde
U163
70-25-7
Guanidine, N-methyl-N’-nitro-N-nitroso-
U127
118-74-1
Hexachlorobenzene
U128
87-68-3
Hexachlorobutadiene
U130
77-47-4
Hexachlorocyclopentadiene
U131
67-72-1
Hexachloroethane
U132
70-30-4
Hexachlorophene
U243
1888-71-7
Hexachloropropene
U133
302-01-2
Hydrazine (R,T)
U086
1615-80-1
Hydrazine, 1,2-diethyl-
U098
57-14-7
Hydrazine, 1,1-dimethyl-
U099
540-73-8
Hydrazine, 1,2-dimethyl-
U109
122-66-7
Hydrazine, 1,2-diphenyl-
U134
7664-39-3
Hydrofluoric acid (C,T)
U134
7664-39-3
Hydrogen fluoride (C,T)
U135
7783-06-4
Hydrogen sulfide
U135
7783-06-4
Hydrogen sulfide H
2
S
U096
80-15-9
Hydroperoxide, 1-methyl-1-phenylethyl- (R)
U116
96-45-7
2-Imidazolidinethione
U137
193-39-5
Indeno[1,2,3-cd]pyrene
U190
85-44-9
1,3-Isobenzofurandione
U140
78-83-1
Isobutyl alcohol (I,T)
U141
120-58-1
Isosafrole
U142
143-50-0
Kepone
U143
303-34-4
Lasiocarpene
U144
301-04-2
Lead acetate
U146
1335-32-6
Lead, bis(acetato-O)tetrahydroxytri-
U145
7446-27-7
Lead phosphate
U146
1335-32-6
Lead subacetate
U129
58-89-9
Lindane
U163
70-25-7
MNNG
U147
108-31-6
Maleic anhydride
U148
123-33-1
Maleic hydrazide
125
U149
109-77-3
Malononitrile
U150
148-82-3
Melphalan
U151
7439-97-6
Mercury
U152
126-98-7
Methacrylonitrile (I,T)
U092
124-40-3
Methanamine, N-methyl- (I)
U029
74-83-9
Methane, bromo-
U045
74-87-3
Methane, chloro- (I,T)
U046
107-30-2
Methane, chloromethoxy-
U068
74-95-3
Methane, dibromo-
U080
75-09-2
Methane, dichloro-
U075
75-71-8
Methane, dichlorodifluoro-
U138
74-88-4
Methane, iodo-
U119
62-50-0
Methanesulfonic acid, ethyl ester
U211
56-23-5
Methane, tetrachloro-
U153
74-93-1
Methanethiol (I,T)
U225
75-25-2
Methane, tribromo-
U044
67-66-3
Methane, trichloro-
U121
75-69-4
Methane, trichlorofluoro-
U036
57-74-9
4,7-Methano-1H-indene, 1,2,4,5,6,7,8,8-
octachloro-2,3,3a,4,7,7a-hexahydro-
U154
67-56-1
Methanol (I)
U155
91-80-5
Methapyrilene
U142
143-50-0
1,3,4-Metheno-2H-cyclobuta[cd]pentalen-2-one,
1,1a,3,3a,4,5,5,5a,5b,6-decachlorooctahydro-
U247
72-43-5
Methoxychlor
U154
67-56-1
Methyl alcohol (I)
U029
74-83-9
Methyl bromide
U186
504-60-9
1-Methylbutadiene (I)
U045
74-87-3
Methyl chloride (I,T)
U156
79-22-1
Methyl chlorocarbonate (I,T)
U226
71-55-6
Methylchloroform
U157
56-49-5
3-Methylcholanthrene
U158
101-14-4
4,4'-Methylenebis(2-chloroaniline)
U068
74-95-3
Methylene bromide
U080
75-09-2
Methylene chloride
U159
78-93-3
Methyl ethyl ketone (MEK) (I,T)
U160
1338-23-4
Methyl ethyl ketone peroxide (R,T)
U138
74-88-4
Methyl iodide
U161
108-10-1
Methyl isobutyl ketone (I)
U162
80-62-6
Methyl methacrylate (I,T)
U161
108-10-1
4-Methyl-2-pentanone (I)
U164
56-04-2
Methylthiouracil
U010
50-07-7
Mitomycin C
126
U059
20830-81-3
5,12-Naphthacenedione, 8-acetyl-10-[(3-amino-
2,3,6-trideoxy)-
α
-L-lyxo-hexapyranosyl)oxyl]-
7,8,9,10-tetrahydro-6,8,11-trihydroxy-1-
methoxy-, (8S-cis)-
U167
134-32-7
1-Naphthalenamine
U168
91-59-8
2-Naphthalenamine
U026
494-03-1
Naphthaleneamine, N,N’-bis(2-chloroethyl)-
U165
91-20-3
Naphthalene
U047
91-58-7
Naphthalene, 2-chloro-
U166
130-15-4
1,4-Naphthalenedione
U236
72-57-1
2,7-Naphthalenedisulfonic acid, 3,3'-[(3,3'-di-
methyl-[1,1'-biphenyl]-4,4'-diyl)bis(azo)bis[5-
amino-4-hydroxy]-, tetrasodium salt
U279
63-25-2
1-Naphthalenol, methylcarbamate
U166
130-15-4
1,4-Naphthoquinone
U167
134-32-7
α
-Naphthylamine
U168
91-59-8
β
-Naphthylamine
U217
10102-45-1
Nitric acid, thallium (1+) salt
U169
98-95-3
Nitrobenzene (I,T)
U170
100-02-7
p-Nitrophenol
U171
79-46-9
2-Nitropropane (I,T)
U172
924-16-3
N-Nitrosodi-n-butylamine
U173
1116-54-7
N-Nitrosodiethanolamine
U174
55-18-5
N-Nitrosodiethylamine
U176
759-73-9
N-Nitroso-N-ethylurea
U177
684-93-5
N-Nitroso-N-methylurea
U178
615-53-2
N-Nitroso-N-methylurethane
U179
100-75-4
N-Nitrosopiperidine
U180
930-55-2
N-Nitrosopyrrolidine
U181
99-55-8
5-Nitro-o-toluidine
U193
1120-71-4
1,2-Oxathiolane, 2,2-dioxide
U058
50-18-0
2H-1,3,2-Oxazaphosphorin-2-amine, N,N-bis(2-
chloroethyl)tetrahydro-, 2-oxide
U115
75-21-8
Oxirane (I,T)
U126
765-34-4
Oxiranecarboxyaldehyde
U041
106-89-8
Oxirane, (chloromethyl)-
U182
123-63-7
Paraldehyde
U183
608-93-5
Pentachlorobenzene
U184
76-01-7
Pentachloroethane
U185
82-68-8
Pentachloronitrobenzene (PCNB)
See F027
87-86-5
Pentachlorophenol
U161
108-10-1
Pentanol, 4-methyl-
U186
504-60-9
1,3-Pentadiene (I)
U187
62-44-2
Phenacetin
U188
108-95-2
Phenol
127
U048
95-57-8
Phenol, 2-chloro-
U039
59-50-7
Phenol, 4-chloro-3-methyl-
U081
120-83-2
Phenol, 2,4-dichloro-
U082
87-65-0
Phenol, 2,6-dichloro-
U089
56-53-1
Phenol, 4,4'-(1,2-diethyl-1,2-ethenediyl)bis-,
(E)-
U101
105-67-9
Phenol, 2,4-dimethyl-
U052
1319-77-3
Phenol, methyl-
U132
70-30-4
Phenol, 2,2'-methylenebis[3,4,6-trichloro-
U411
114-26-1
Phenol, 2-(1-methylethoxy)-, methylcarbamate
U170
100-02-7
Phenol, 4-nitro-
See F027
87-86-5
Phenol, pentachloro-
See F027
58-90-2
Phenol, 2,3,4,6-tetrachloro-
See F027
95-95-4
Phenol, 2,4,5-trichloro-
See F027
88-06-2
Phenol, 2,4,6-trichloro-
U150
148-82-3
L-Phenylalanine, 4-[bis(2-chloroethyl)amino]-
U145
7446-27-7
Phosphoric acid, lead (2+) salt (2:3)
U087
3288-58-2
Phosphorodithioic acid, O,O-diethyl S-methyl
ester
U189
1314-80-3
Phosphorus sulfide (R)
U190
85-44-9
Phthalic anhydride
U191
109-06-8
2-Picoline
U179
100-75-4
Piperidine, 1-nitroso-
U192
23950-58-5
Pronamide
U194
107-10-8
1-Propanamine (I,T)
U111
621-64-7
1-Propanamine, N-nitroso-N-propyl-
U110
142-84-7
1-Propanamine, N-propyl- (I)
U066
96-12-8
Propane, 1,2-dibromo-3-chloro-
U083
78-87-5
Propane, 1,2-dichloro-
U149
109-77-3
Propanedinitrile
U171
79-46-9
Propane, 2-nitro- (I,T)
U027
108-60-1
Propane, 2,2'-oxybis[2-chloro-
See F027
93-72-1
Propanoic acid, 2-(2,4,5-trichlorophenoxy)-
U193
1120-71-4
1,3-Propane sultone
U235
126-72-7
1-Propanol, 2,3-dibromo-, phosphate (3:1)
U140
78-83-1
1-Propanol, 2-methyl- (I,T)
U002
67-64-1
2-Propanone (I)
U007
79-06-1
2-Propenamide
U084
542-75-6
1-Propene, 1,3-dichloro-
U243
1888-71-7
1-Propene, 1,1,2,3,3,3-hexachloro-
U009
107-13-1
2-Propenenitrile
U152
126-98-7
2-Propenenitrile, 2-methyl- (I,T)
U008
79-10-7
2-Propenoic acid (I)
U113
140-88-5
2-Propenoic acid, ethyl ester (I)
U118
97-63-2
2-Propenoic acid, 2-methyl-, ethyl ester
128
U162
80-62-6
2-Propenoic acid, 2-methyl-, methyl ester (I,T)
U373
122-42-9
Propham
U411
114-26-1
Propoxur
See F027
93-72-1
Propionic acid, 2-(2,4,5-trichlorophenoxy)-
U194
107-10-8
n-Propylamine (I,T)
U083
78-87-5
Propylene dichloride
U387
52888-80-9
Prosulfocarb
U148
123-33-1
3,6-Pyridazinedione, 1,2-dihydro-
U196
110-86-1
Pyridine
U191
109-06-8
Pyridine, 2-methyl-
U237
66-75-1
2,4-(1H,3H)-Pyrimidinedione, 5-[bis(2-chloro-
ethyl)amino]-
U164
58-04-2
4(1H)-Pyrimidinone, 2,3-dihydro-6-methyl-2-
thioxo-
U180
930-55-2
Pyrrolidine, 1-nitroso-
U200
50-55-5
Reserpine
U201
108-46-3
Resorcinol
U202
P 81-07-2
Saccharin and salts
U203
94-59-7
Safrole
U204
7783-00-8
Selenious acid
U204
7783-00-8
Selenium dioxide
U205
7488-56-4
Selenium sulfide
U205
7488-56-4
Selenium sulfide SeS
2
(R,T)
U015
115-02-6
L-Serine, diazoacetate (ester)
See F027
93-72-1
Silvex (2,4,5-TP)
U206
18883-66-4
Streptozotocin
U103
77-78-1
Sulfuric acid, dimethyl ester
U189
1314-80-3
Sulfur phosphide (R)
See F027
93-76-5
2,4,5-T
U207
95-94-3
1,2,4,5-Tetrachlorobenzene
U208
630-20-6
1,1,1,2-Tetrachloroethane
U209
79-34-5
1,1,2,2-Tetrachloroethane
U210
127-18-4
Tetrachloroethylene
See F027
58-90-2
2,3,4,6-Tetrachlorophenol
U213
109-99-9
Tetrahydrofuran (I)
U214
563-68-8
Thallium (I) acetate
U215
6533-73-9
Thallium (I) carbonate
U216
7791-12-0
Thallium (I) chloride
U216
7791-12-0
Thallium chloride TlCl
U217
10102-45-1
Thallium (I) nitrate
U218
62-55-5
Thioacetamide
U410
59669-26-0
Thiodicarb
U153
74-93-1
Thiomethanol (I,T)
U244
137-26-8
Thioperoxydicarbonic diamide [(H
2
N)C(S)]
2
S
2
,
tetramethyl-
129
U409
23564-05-8
Thiophanate-methyl
U219
62-56-6
Thiourea
U244
137-26-8
Thiram
U220
108-88-3
Toluene
U221
25376-45-8
Toluenediamine
U223
26471-62-5
Toluene diisocyanate (R,T)
U328
95-53-4
o-Toluidine
U353
106-49-0
p-Toluidine
U222
636-21-5
o-Toluidine hydrochloride
U389
2303-17-5
Triallate
U011
61-82-5
1H-1,2,4-Triazol-3-amine
U408
118-79-6
2,4,6-Tribromophenol
U227
79-00-5
1,1,2-Trichloroethane
U228
79-01-6
Trichloroethylene
U121
75-69-4
Trichloromonofluoromethane
See F027
95-95-4
2,4,5-Trichlorophenol
See F027
88-06-2
2,4,6-Trichlorophenol
U404
121-44-8
Triethylamine
U234
99-35-4
1,3,5-Trinitrobenzene (R,T)
U182
123-63-7
1,3,5-Trioxane, 2,4,6-trimethyl-
U235
126-72-7
Tris(2,3-dibromopropyl) phosphate
U236
72-57-1
Trypan blue
U237
66-75-1
Uracil mustard
U176
759-73-9
Urea, N-ethyl-N-nitroso-
U177
684-93-5
Urea, N-methyl-N-nitroso-
U043
75-01-4
Vinyl chloride
U248
P 81-81-2
Warfarin, and salts, when present at
concentrations of 0.3 percent or less
U239
1330-20-7
Xylene (I)
U200
50-55-5
Yohimban-16-carboxylic acid, 11,17-dimethoxy-
18-[(3,4,5-trimethoxybenzoyl)oxy]-, methyl
ester, (3
β
,16
β
,17
α
,18
β
,20
α
)-
U249
1314-84-7
Zinc phosphide Zn
3
P
2
, when present at
concentrations of 10 percent or less
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
Section 721.138
Comparable or Syngas Fuel Exclusion
Wastes that meet the following comparable or syngas fuel requirements are not solid wastes:
a)
Comparable fuel specifications.
1)
Physical specifications.
130
A)
Heating value. The heating value must exceed 5,000 Btu/lb
(11,500 J/g).
B)
Viscosity. The viscosity must not exceed: 50 cs, as-fired.
2)
Constituent specifications. For the compounds listed, the constituent
specification levels and minimum required detection limits (where non-
detect is the constituent specification) are set forth in the table at
subsection (d) of this Section.
b)
Synthesis gas fuel specification. Synthesis gas fuel (i.e., syngas fuel) that is
generated from hazardous waste must fulfill the following requirements:
1)
It must have a minimum Btu value of 100 Btu/Scf;
2)
It must contain less than 1 ppmv of total halogen;
3)
It must contain less than 300 ppmv of total nitrogen other than diatomic
nitrogen (N
2
);
4)
It must contain less than 200 ppmv of hydrogen sulfide; and
5)
It must contain less than 1 ppmv of each hazardous constituent in the
target list of Appendix H constituents.
c)
Implementation. Waste that meets the comparable or syngas fuel specifications
provided by subsection (a) or (b) of this Section (these constituent levels must be
achieved by the comparable fuel when generated, or as a result of treatment or
blending, as provided in subsection (c)(3) or (c)(4) of this Section) is excluded
from the definition of solid waste provided that the following requirements are
met:
1)
Notices. For purposes of this Section, the person claiming and qualifying
for the exclusion is called the comparable or syngas fuel generator and
the person burning the comparable or syngas fuel is called the
comparable or syngas burner. The person that generates the comparable
fuel or syngas fuel must claim and certify to the exclusion.
A)
Notice to the Agency.
i)
The generator must submit a one-time notice to the
Agency, certifying compliance with the conditions of the
exclusion and providing documentation as required by
subsection (c)(1)(A)(iii) of this Section;
131
ii)
If the generator is a company that generates comparable or
syngas fuel at more than one facility, the generator shall
specify at which sites the comparable or syngas fuel will
be generated;
iii)
A comparable or syngas fuel generator’s notification to the
Agency must contain the items listed in subsection
(c)(1)(C) of this Section.
B)
Public notice. Prior to burning an excluded comparable or syngas
fuel, the burner must publish in a major newspaper of general
circulation, local to the site where the fuel will be burned, a notice
entitled “Notification of Burning a Comparable or Syngas Fuel
Excluded Under the Resource Conservation and Recovery Act”
containing the following information:
i)
The name, address, and USEPA identification number of
the generating facility;
ii)
The name and address of the unit(s) units that will burn the
comparable or syngas fuel;
iii)
A brief, general description of the manufacturing,
treatment, or other process generating the comparable or
syngas fuel;
iv)
An estimate of the average and maximum monthly and
annual quantity of the waste claimed to be excluded; and
v)
The name and mailing address of the Agency office, to
which the claim was submitted.
C)
Required content of comparable or syngas notification to the
Agency.
i)
The name, address, and USEPA identification number of
the person or facility claiming the exclusion;
ii)
The applicable USEPA hazardous waste code(s) codes for
the hazardous waste;
iii)
The name and address of the units that meet the
requirements of subsection (c)(2) of this Section which that
will burn the comparable or syngas fuel; and
132
iv)
The following statement, signed and submitted by the
person claiming the exclusion or its authorized
representative:
Under penalty of criminal and civil prosecution for
making or submitting false statements,
representations, or omissions, I certify that the
requirements of 35 Ill. Adm. Code 721.138 have
been met for all waste identified in this
notification. Copies of the records and information
required by 35 Ill. Adm. Code 721.138(c)(10) are
available at the comparable or syngas fuel
generator’s facility. Based on my inquiry of the
individuals immediately responsible for obtaining
the information, the information is, to the best of
my knowledge and belief, true, accurate, and
complete. I am aware that there are significant
penalties for submitting false information, including
the possibility of fine and imprisonment for
knowing violations.
BOARD NOTE: Subsections (c)(1)(C)(i) through (c)(1)(C)(iv)
are derived from 40 CFR 261.138(c)(1)(i)(C)(
1
) and
(c)(1)(i)(C)(
4
), which the Board has codified here to comport with
Illinois Administrative Code format requirements.
2)
Burning. The comparable or syngas fuel exclusion for fuels that meet the
requirements of subsection subsections (a) or (b) and (c)(1) of this Section
applies only if the fuel is burned in the following units that also shall be
subject to federal, State, and local air emission requirements, including all
applicable federal Clean Air Act (CAA) maximum achievable control
technology (MACT) requirements:
A)
Industrial furnaces, as defined in 35 Ill. Adm. Code 720.110;
B)
Boilers, as defined in 35 Ill. Adm. Code 720.110, that are further
defined as follows:
i)
Industrial boilers located on the site of a facility engaged in
a manufacturing process where substances are transformed
into new products, including the component parts of
products, by mechanical or chemical processes; or
ii)
Utility boilers used to produce electric power, steam,
heated or cooled air, or other gases or fluids for sale;
133
C)
Hazardous waste incinerators subject to regulation under 35 Ill.
Adm. Code 724.Subpart O or 35 Ill. Adm. Code 725.Subpart O
or applicable CAA MACT standards.
3)
Blending to meet the viscosity specification. A hazardous waste blended
to meet the viscosity specification must fulfill the following requirements:
A)
As generated and prior to any blending, manipulation, or
processing, the waste must meet the constituent and heating value
specifications of subsections (a)(1)(A) and (a)(2) of this Section;
B)
The waste must be blended at a facility that is subject to the
applicable requirements of 35 Ill. Adm. Code 724 and 725 or 35
Ill. Adm. Code 722.134; and
C)
The waste must not violate the dilution prohibition of subsection
(c)(6) of this Section.
4)
Treatment to meet the comparable fuel exclusion specifications.
A)
A hazardous waste may be treated to meet the exclusion
specifications of subsections (a)(1) and (a)(2) of this Section
provided the treatment fulfills the following requirements:
i)
The treatment destroys or removes the constituent listed in
the specification or raises the heating value by removing or
destroying hazardous constituents or materials;
ii)
The treatment is performed at a facility that is subject to
the applicable requirements of 35 Ill. Adm. Code 724 and
725 or 35 Ill. Adm. Code 722.134; and
iii)
The treatment does not violate the dilution prohibition of
subsection (c)(6) of this Section.
B)
Residuals resulting from the treatment of a hazardous waste listed
in Subpart D of this Part to generate a comparable fuel remain a
hazardous waste.
5)
Generation of a syngas fuel.
A)
A syngas fuel can be generated from the processing of hazardous
wastes to meet the exclusion specifications of subsection (b) of this
Section provided the processing fulfills the following
134
requirements:
i)
The processing destroys or removes the constituent listed
in the specification or raises the heating value by removing
or destroying constituents or materials;
ii)
The processing is performed at a facility that is subject to
the applicable requirements of 35 Ill. Adm. Code 724 and
725 or 35 Ill. Adm. Code 722.134 or is an exempt
recycling unit pursuant to Section 721.106(c); and
iii)
The processing does not violate the dilution prohibition of
subsection (c)(6) of this Section.
B)
Residuals resulting from the treatment of a hazardous waste listed
in Subpart D of this Part to generate a syngas fuel remain a
hazardous waste.
6)
Dilution prohibition for comparable and syngas fuels. No generator,
transporter, handler, or owner or operator of a treatment, storage, or
disposal facility shall in any way dilute a hazardous waste to meet the
exclusion specifications of subsection (a)(1)(A), (a)(2) or (b) of this
Section.
7)
Waste analysis plans. The generator of a comparable or syngas fuel shall
develop and follow a written waste analysis plan which that describes the
procedures for sampling and analysis of the hazardous waste to be
excluded. The waste analysis plan shall be developed in accordance with
the applicable sections of the “Test Methods for Evaluating Solid Waste,
Physical/Chemical Methods” (SW-846). The plan shall be followed and
retained at the facility excluding the waste.
A)
At a minimum, the plan must specify the following:
i)
The parameters for which each hazardous waste will be
analyzed and the rationale for the selection of those
parameters;
ii)
The test methods which that will be used to test for these
parameters;
iii)
The sampling method which that will be used to obtain a
representative sample of the waste to be analyzed;
iv)
The frequency with which the initial analysis of the waste
135
will be reviewed or repeated to ensure that the analysis is
accurate and up to date; and
v)
If process knowledge is used in the waste determination,
any information prepared by the generator in making such
determination.
B)
The waste analysis plan must also contain records of the
following:
i)
The dates and times waste samples were obtained, and the
dates the samples were analyzed;
ii)
The names and qualifications of the person(s) persons who
obtained the samples;
iii)
A description of the temporal and spatial locations of the
samples;
iv)
The name and address of the laboratory facility at which
analyses of the samples were performed;
v)
A description of the analytical methods used, including any
clean-up and sample preparation methods;
vi)
All quantitation limits achieved and all other quality control
results for the analysis (including method blanks, duplicate
analyses, matrix spikes, etc.), laboratory quality assurance
data, and description of any deviations from analytical
methods written in the plan or from any other activity
written in the plan which occurred;
vii)
All laboratory results demonstrating that the exclusion
specifications have been met for the waste; and
viii)
All laboratory documentation that supports the analytical
results, unless a contract between the claimant and the
laboratory provides for the documentation to be maintained
by the laboratory for the period specified in subsection
(c)(11) of this Section and also provides for the availability
of the documentation to the claimant upon request.
C)
Syngas fuel generators shall submit for approval, prior to
performing sampling, analysis, or any management of a syngas
fuel as an excluded waste, a waste analysis plan containing the
136
elements of subsection (c)(7)(A) of this Section to the Agency.
The approval of waste analysis plans must be stated in writing and
received by the facility prior to sampling and analysis to
demonstrate the exclusion of a syngas. The approval of the waste
analysis plan may contain such provisions and conditions as the
regulatory authority deems appropriate.
8)
Comparable fuel sampling and analysis.
A)
General. For each waste for which an exclusion is claimed, the
generator of the hazardous waste must test for all the constituents
on Appendix H of this Part, except those that the generator
determines, based on testing or knowledge, should not be present
in the waste. The generator is required to document the basis of
each determination that a constituent should not be present. The
generator may not determine that any of the following categories
of constituents should not be present:
i)
A constituent that triggered the toxicity characteristic for
the waste constituents that were the basis of the listing of
the waste stream, or constituents for which there is a
treatment standard for the waste code in 35 Ill. Adm. Code
728.140;
ii)
A constituent detected in previous analysis of the waste;
iii)
Constituents introduced into the process that generates the
waste; or
iv)
Constituents that are byproducts or side reactions to the
process that generates the waste.
Note to subsection (c)(8): Any claim under this Section must be valid
and accurate for all hazardous constituents; a determination not to test for
a hazardous constituent will not shield a generator from liability should
that constituent later be found in the waste above the exclusion
specifications.
B)
For each waste for which the exclusion is claimed where the
generator of the comparable or syngas fuel is not the original
generator of the hazardous waste, the generator of the comparable
or syngas fuel may not use process knowledge pursuant to
subsection (c)(8)(A) of this Section and must test to determine that
all of the constituent specifications of subsections (a)(2) and (b) of
this Section have been met.
137
C)
The comparable or syngas fuel generator may use any reliable
analytical method to demonstrate that no constituent of concern is
present at concentrations above the specification levels. It is the
responsibility of the generator to ensure that the sampling and
analysis are unbiased, precise, and representative of the waste.
For the waste to be eligible for exclusion, a generator must
demonstrate the following:
i)
That each constituent of concern is not present in the waste
above the specification level at the 95 percent upper
confidence limit around the mean; and
ii)
That the analysis could have detected the presence of the
constituent at or below the specification level at the 95
percent upper confidence limit around the mean.
D)
Nothing in this subsection (c)(8) preempts, overrides or otherwise
negates the provision in 35 Ill. Adm. Code 722.111 that requires
any person which generates a solid waste to determine if that
waste is a hazardous waste.
E)
In an enforcement action, the burden of proof to establish
conformance with the exclusion specification shall be on the
generator claiming the exclusion.
F)
The generator must conduct sampling and analysis in accordance
with its waste analysis plan developed under subsection (c)(7) of
this Section.
G)
Syngas fuel and comparable fuel that has not been blended in
order to meet the kinematic viscosity specifications must be
analyzed as generated.
H)
If a comparable fuel is blended in order to meet the kinematic
viscosity specifications, the generator shall undertake the following
actions:
i)
Analyze the fuel as generated to ensure that it meets the
constituent and heating value specifications; and
ii)
After blending, analyze the fuel again to ensure that the
blended fuel continues to meet all comparable or syngas
fuel specifications.
138
I)
Excluded comparable or syngas fuel must be re-tested retested, at
a minimum, annually and must be retested after a process change
that could change the chemical or physical properties of the waste.
Note to subsection (c)(8): Any claim under this Section must be valid
and accurate for all hazardous constituents; a determination not to test for
a hazardous constituent will not shield a generator from liability should
that constituent later be found in the waste above the exclusion
specifications.
9)
Speculative accumulation. Any persons handling a comparable or syngas
fuel are subject to the speculative accumulation test under Section
721.102(c)(4).
10)
Records. The generator must maintain records of the following
information on-site:
A)
All information required to be submitted to the implementing
authority as part of the notification of the claim:
i)
The owner or operator name, address, and RCRA facility
USEPA identification number of the person claiming the
exclusion;
ii)
The applicable USEPA hazardous waste codes for each
hazardous waste excluded as a fuel; and
iii)
The certification signed by the person claiming the
exclusion or his authorized representative.;
B)
A brief description of the process that generated the hazardous
waste and process that generated the excluded fuel, if not the
same;
C)
An estimate of the average and maximum monthly and annual
quantities of each waste claimed to be excluded;
D)
Documentation for any claim that a constituent is not present in
the hazardous waste as required under subsection (c)(8)(A) of this
Section;
E)
The results of all analyses and all detection limits achieved as
required under subsection (c)(8) of this Section;
F)
If the excluded waste was generated through treatment or
139
blending, documentation as required under subsection (c)(3) or
(c)(4) of this Section;
G)
If the waste is to be shipped off-site, a certification from the
burner as required under subsection (c)(12) of this Section;
H)
A waste analysis plan and the results of the sampling and analysis
that includes include the following:
i)
The dates and times waste samples were obtained, and the
dates the samples were analyzed;
ii)
The names and qualifications of the person(s) persons that
obtained the samples;
iii)
A description of the temporal and spatial locations of the
samples;
iv)
The name and address of the laboratory facility at which
analyses of the samples were performed;
v)
A description of the analytical methods used, including any
clean-up and sample preparation methods;
vi)
All quantitation limits achieved and all other quality control
results for the analysis (including method blanks, duplicate
analyses, matrix spikes, etc.), laboratory quality assurance
data, and description of any deviations from analytical
methods written in the plan or from any other activity
written in the plan which that occurred;
vii)
All laboratory analytical results demonstrating that the
exclusion specifications have been met for the waste; and
viii)
All laboratory documentation that supports the analytical
results, unless a contract between the claimant and the
laboratory provides for the documentation to be maintained
by the laboratory for the period specified in subsection
(c)(11) of this Section and also provides for the availability
of the documentation to the claimant upon request; and
I)
If the generator ships comparable or syngas fuel off-site for
burning, the generator shall retain for each shipment the following
information on-site:
140
i)
The name and address of the facility receiving the
comparable or syngas fuel for burning;
ii)
The quantity of comparable or syngas fuel shipped and
delivered;
iii)
The date of shipment or delivery;
iv)
A cross-reference to the record of comparable or syngas
fuel analysis or other information used to make the
determination that the comparable or syngas fuel meets the
specifications as required under subsection (c)(8) of this
Section; and
v)
A one-time certification by the burner as required under
subsection (c)(12) of this Section.
11)
Records retention. Records must be maintained for the period of three
years. A generator shall maintain a current waste analysis plan during
that three year period.
12)
Burner certification. Prior to submitting a notification to the Agency, a
comparable or syngas fuel generator that intends to ship their its fuel off-
site for burning must obtain a one-time written, signed statement from the
burner that includes the following:
A)
A certification that the comparable or syngas fuel will only be
burned in an industrial furnace or boiler, utility boiler, or
hazardous waste incinerator, as required under subsection (c)(2)
of this Section;
B)
Identification of the name and address of the units that will burn
the comparable or syngas fuel; and
C)
A certification that the state in which the burner is located is
authorized to exclude wastes as comparable or syngas fuel under
the provisions of this Section.
13)
Ineligible waste codes. Wastes that are listed because of presence of
dioxins or furans, as set out in Appendix G of this Part, are not eligible
for this exclusion, and any fuel produced from or otherwise containing
these wastes remains a hazardous waste subject to full RCRA hazardous
waste management requirements.
d)
Table Y of this Part sets forth the table of detection and detection limit values for
141
comparable fuel specification:.
Chemical name
CAS No
Concentration
limit (mg/kg at
10,000 Btu/lb)
Minimum re-
quired detection
limit (mg/kg)
Total Nitrogen as N
na
4900
Total Halogens as Cl
na
540
Total Organic Halogens as
Cl
na
25 or individual
halogenated
organics listed
below.
Polychlorinated biphenyls,
total [Arocolors, total]
a
1336-36-3
Non-detect
1.4
Cyanide, total
57-12-5
Non-detect
1.0
Metals:
Antimony, total
7440-36-0
7.9
Arsenic, total
7440-38-2
0.23
Barium, total
7440-39-3
23
Beryllium, total
7440-41-7
1.2
Cadmium, total
7440-43-9
1.2
Chromium, total
7440-47-3
2.3
Cobalt
7440-48-4
4.6
Lead, total
7439-92-1
31
Manganese
7439-96-5
1.2
Mercury, total
7439-97-6
0.24
Nickel, total
7440-02-0
58
Selenium, total
7782-49-2
0.15
Silver, total
7440-22-4
2.3
Thallium, total
7440-28-0
23
Hydrocarbons:
Benzo[a]anthracene
56-55-3
1100
Benzene
71-43-2
4100
Benzo[b]fluoranthene
205-99-2
960
Benzo[k]fluoranthene
207-08-9
1900
Benzo[a]pyrene
50-32-8
960
Chrysene
218-01-9
1400
Dibenzo[a,h]anthracene
53-70-3
960
7,12-Dimethylbenz[a]-
anthracene
57-97-6
1900
Fluoranthene
206-44-0
1900
Indeno(1,2,3-cd)pyrene
193-39-5
960
3-Methylcholanthrene
56-49-5
1900
Naphthalene
91-20-3
3200
142
Toluene
108-88-3
36000
Oxygetes:
Acetophenone
98-86-2
1900
Acrolein
107-02-8
37
Allyl alcohol
107-18-6
30
Bis(2-ethylhexyl)-
phthalate [Di-2-ethyl-
hexyl phthalate]
117-81-7
1900
Butyl benzyl phthalate
85-68-7
1900
o-Cresol [2-Methyl
phenol]
95-48-7
220
m-Cresol [3-Methyl
phenol]
108-39-4
220
p-Cresol [4-Methyl
phenol]
106-44-5
220
Di-n-butyl phthalate
84-74-2
1900
Diethyl phthalate
84-66-2
1900
2,4-Dimethylphenol
105-67-9
1900
Dimethyl phthalate
131-11-3
1900
Di-n-octyl phthalate
117-84-0
960
Endothall
145-73-3
100
Ethyl methacrylate
97-63-2
37
2-Ethoxyethanol
[Ethylene glycol
monoethyl ether].
110-80-5
100
Isobutyl alcohol
78-83-1
37
Isosafrole
120-58-1
1900
Methyl ethyl ketone [2-
Butanone]
78-93-3
37.
Methyl methacrylate
80-62-6
37.
1,4-Naphthoquinone
130-15-4
1900.
Phenol
108-95-2
1900.
Propargyl alcohol [2-
Propyn-l-ol]
107-19-7
30.
Safrole
94-59-7
1900.
Sulfonated Organics:
Carbon disulfide
75-15-0
Non-detect
37
Disulfoton
298-04-4
Non-detect
1900
Ethyl methanesulfonate
62-50-0
Non-detect
1900
Methyl methane-
sulfonate
66-27-3
Non-detect
1900
Phorate
298-02-2
Non-detect
1900
1,3-Propane sultone
1120-71-4
Non-detect
100
143
Tetraethyldithiopyro-
phosphate [Sulfotepp]
3689-24-5
Non-detect
1900
Thiophenol [Benzene-
thiol]
108-98-5
Non-detect
30
O,O,O-Triethyl
phosphorothioate
126-68-1
Non-detect
1900
Nitrogenated Organics:
Acetonitrile [Methyl
cyanide]
75-05-8
Non-detect
37
2-Acetylaminofluorene
[2-AAF]
53-96-3
Non-detect
1900
Acrylonitrile
107-13-1
Non-detect
37
4-Aminobiphenyl
92-67-1
Non-detect
1900
4-Aminopyridine
504-24-5
Non-detect
100
Aniline
62-53-3
Non-detect
1900
Benzidine
92-87-5
Non-detect
1900
Dibenz[a,j]acridine
224-42-0
Non-detect
1900
O,O-Diethyl O-
pyrazinyl phophoro-
thioate [Thionazin].
297-97-2
Non-detect
1900
Dimethoate
60-51-5
Non-detect
1900
p-(Dimethylamino)azo-
benzene [4-Dimethyl-
aminoazobenzene].
60-11-7
Non-detect
1900
3,3'-Dimethylbenzidine
119-93-7
Non-detect
1900
a,a-Dimethylphenethyl-
amine.
122-09-8
Non-detect
1900
3,3'-Dimethoxy-
benzidine
119-90-4
Non-detect
100
1,3-Dinitrobenzene [m-
Dinitrobenzene]
99-65-0
Non-detect
1900
4,6-Dinitro-o-cresol
534-52-1
Non-detect
1900
2,4-Dinitrophenol
51-28-5
Non-detect
1900
2,4-Dinitrotoluene
121-14-2
Non-detect
1900
2,6-Dinitrotoluene
606-20-2
Non-detect
1900
Dinoseb [2-sec-Butyl-
4,6-dinitrophenol]
88-85-7
Non-detect
1900
Diphenylamine
122-39-4
Non-detect
1900
Ethyl carbamate
[Urethane]
51-79-6
Non-detect
100
Ethylenethiourea (2-
Imidazolidinethione)
96-45-7
Non-detect
110
Famphur
52-85-7
Non-detect
1900
144
Methacrylonitrile
126-98-7
Non-detect
37
Methapyrilene
91-80-5
Non-detect
1900
Methomyl
16752-77-5
Non-detect
57
2-Methyllactonitrile
[Acetone cyanohydrin].
75-86-5
Non-detect
100
Methyl parathion
298-00-0
Non-detect
1900
MNNG (N-Metyl-N-
nitroso-N’-nitro-
guanidine)
70-25-7
Non-detect
110
1-Naphthylamine, [
α
-
Naphthylamine]
134-32-7
Non-detect
1900
2-Naphthylamine, [
β
-
Naphthylamine]
91-59-8
Non-detect
1900
Nicotine
54-11-5
Non-detect
100
4-Nitroaniline, [p-
Nitroaniline]
100-01-6
Non-detect
1900
Nitrobenzene
98-95-3
Non-detect
1900
p-Nitrophenol, [p-
Nitrophenol]
100-02-7
Non-detect
1900
5-Nitro-o-toluidine
99-55-8
Non-detect
1900
N-Nitrosodi-n-butyl-
amine
924-16-3
Non-detect
1900
N-Nitrosodiethylamine
55-18-5
Non-detect
1900
N-Nitrosodiphenyl-
amine, [Diphenylnitros-
amine]
86-30-6
Non-detect
1900
N-Nitroso-N-methyl-
ethylamine
10595-95-6
Non-detect
1900
N-Nitrosomorpholine
59-89-2
Non-detect
1900
N-Nitrosopiperidine
100-75-4
Non-detect
1900
N-Nitrosopyrrolidine
930-55-2
Non-detect
1900
2-Nitropropane
79-46-9
Non-detect
30
Parathion
56-38-2
Non-detect
1900
Phenacetin
62-44-2
Non-detect
1900
1,4-Phenylene diamine,
[p-Phenylenediamine]
106-50-3
Non-detect
1900
N-Phenylthiourea
103-85-5
Non-detect
57
2-Picoline [alpha-
Picoline]
109-06-8
Non-detect
1900
Propythioracil [6-
Propyl-2-thiouracil]
51-52-5
Non-detect
100
Pyridine
110-86-1
Non-detect
1900
Strychnine
57-24-9
Non-detect
100
145
Thioacetamide
62-55-5
Non-detect
57
Thiofanox
39196-18-4
Non-detect
100
Thiourea
62-56-6
Non-detect
57
Toluene-2,4-diamine
[2,4-Diaminotoluene]
95-80-7
Non-detect
57
Toluene-2,6-diamine
[2,6-Diaminotoluene]
823-40-5
Non-detect
57
o-Toluidine
95-53-4
Non-detect
2200
p-Toluidine
106-49-0
Non-detect
100
1,3,5-Trinitrobenzne,
[sym-Trinitobenzene]
99-35-4
Non-detect
2000
Halogenated Organics
b
:
Allyl chloride
107-05-1
Non-detect
37
Aramite
104-57-8
Non-detect
1900
Benzal chloride [Di-
chloromethyl benzene]
98-87-3
Non-detect
100
Benzyl chloride
100-44-77
Non-detect
100
Bis(2-chloroethyl)ether
[Dichloroethyl ether]
111-44-4
Non-detect
1900
Bromoform [Tribromo-
methane]
75-25-2
Non-detect
37
Bromomethane [Methyl
bromide]
74-83-9
Non-detect
37
4-Bromophenyl phenyl
ether [p-Bromodiphenyl
ether]
101-55-3
Non-detect
1900
Carbon tetrachloride
56-23-5
Non-detect
37
Chlordane
57-74-9
Non-detect
14
p-Chloroaniline
106-47-8
Non-detect
1900
Chlorobenzene
108-90-7
Non-detect
37
Chlorobenzilate
510-15-6
Non-detect
1900
p-Chloro-m-cresol
59-50-7
Non-detect
1900
2-Chloroethyl vinyl
ether
110-75-8
Non-detect
37
Chloroform
67-66-3
Non-detect
37
Chloromethane [Methyl
chloride]
74-87-3
Non-detect
37
2-Chlorophthalene
[beta-Chlorophthalene]
91-58-7
Non-detect
1900
2-Chlorophenol [o-
Chlorophenol]
95-57-8
Non-detect
1900
Chloroprene [2-Chloro-
1,3-butadiene]
1126-99-8
Non-detect
37
146
2,4-D [2,4-Dichloro-
phenoxyacetic acid]
94-75-7
Non-detect
7.0
Diallate
2303-16-4
Non-detect
1900
1,2-Dibromo-3-chloro-
propane
96-12-8
Non-detect
37
1,2-Dichlorobenzene
[o-Dichlorobenzene]
95-50-1
Non-detect
1900
1,3-Dichlorobenzene
[m-Dichlorobenzene]
541-73-1
Non-detect
1900
1,4-Dichlorobenzene
[p-Dichlorobenzene]
106-46-7
Non-detect
1900
3,3'-Dichlorobenzidine
91-94-1
Non-detect
1900
Dichlorodifluoro-
methane [CFC-12]
75-71-8
Non-detect
37
1,2-Dichloroethane
[Ethylene dichloride]
107-06-2
Non-detect
37
1,1-Dichloroethylene
[Vinylidene chloride]
75-35-4
Non-detect
37
Dichloromethoxy
ethane [Bis(2-chloro-
ethoxy)methane
111-91-1
Non-detect
1900
2,4-Dichlorophenol
120-83-2
Non-detect
1900
2,6-Dichlorophenol
87-65-0
Non-detect
1900
1,2-Dichloropropane
[Propylene dichloride]
78-87-5
Non-detect
37
cis-1,3-Dichloro-
propylene
10061-01-5
Non-detect
37
trans-1,3-Dichloro-
propylene
10061-02-6
Non-detect
37
1,3-Dichloro-2-
propanol
96-23-1
Non-detect
30
Endosulfan I
959-98-8
Non-detect
1.4
Endosulfan II
33213-65-9
Non-detect
1.4
Endrin
72-20-8
Non-detect
1.4
Endrin aldehyde
7421-93-4
Non-detect
1.4
Endrin Ketone
53494-70-5
Non-detect
1.4
Epichlorohydrin [1-
Chloro-2,3-epoxy
propane]
106-89-8
Non-detect
30
Ethylidene dichloride
[1,1-Dichloroethane]
75-34-3
Non-detect
37
2-Fluoroacetamide
640-19-7
Non-detect
100
Heptachlor
76-44-8
Non-detect
1.4
Heptachlor epoxide
1024-57-3
Non-detect
2.8
147
Hexachlorobenzene
118-74-1
Non-detect
1900
Hexachloro-1,3-buta-
diene [Hexachlorobuta-
diene]
87-68-3
Non-detect
1900
Hexachlorocyclopenta-
diene
77-47-4
Non-detect
1900
Hexachloroethane
67-72-1
Non-detect
1900
Hexachlorophene
70-30-4
Non-detect
1000
Hexachloropropene
[Hexachloropropylene]
1888-71-7
Non-detect
1900
Isodrin
465-73-6
Non-detect
1900
Kepone [Chlordecone]
143-50-0
Non-detect
3600
Lindane [gamma-Hexa-
chlorocyclohexane]
[gamma-BHC]
58-89-9
non-detect
1.4
Methylene chloride
[Dichloromethane]
75-09-2
non-detect
37
4,4'-methylene-bis(2-
chloroaniline)
101-14-4
non-detect
100
Methyl iodide [Iodo-
methane]
74-88-4
non-detect
37
Pentachlorobenzene
608-93-5
non-detect
1900
Pentachloroethane
76-01-7
non-detect
37
Pentachloronitro-
benzene [PCNB]
[Quintobenzene]
[Quintozene]
82-68-8
non-detect
1900
Pentachlorophenol
87-86-5
non-detect
1900
Pronamide
23950-58-5
non-detect
1900
Silvex [2,4,5-Trichloro-
phenoxypropionic acid]
93-72-1
non-detect
7.0
2,3,7,8-Tetrachloro-
dibenzo-p-dioxin
[2,3,7,8-TCDD]
1746-01-6
non-detect
30
1,2,4,5-Tetrachloro-
benzene
95-94-3
non-detect
1900
1,1,2,2-Tetrachloro-
ethane
79-34-5
non-detect
37
Tetrachloroethylene
[Perchloroethylene]
127-18-4
non-detect
37
2,3,4,6-Tetrachloro-
phenol
58-90-2
non-detect
1900
1,2,4-Trichlorobenzene
120-82-1
non-detect
1900
148
1,1,1-Trichloroethane
[Methyl chloroform]
71-55-6
non-detect
37
1,1,2-Trichloroethane
[Vinyl trichloride]
79-00-5
non-detect
37
Trichloroethylene
79-01-6
non-detect
37
Trichlorofluoromethane
[Trichloromonofluoro-
methane]
75-69-4
non-detect
37
2,4,5-Trichlorophenol
95-95-4
non-detect
1900
2,4,6-Trichlorophenol
88-06-2
non-detect
1900
1,2,3-Trichloropropane
96-18-4
non-detect
37
Vinyl Chloride
75-01-4
non-detect
37
a
Absence of PCBs can also be demonstrated by using appropriate screening
methods, e.g., immunoassay kit for PCB in oils (Method 4020) or colorimetric
analysis for PCBs in oil (Method 9079).
b
Some minimum required detection limits are above the total halogen limit of
540 ppm. The detection limits reflect what was achieved during USEPA testing
and analysis and also analytical complexity associated with measuring all halogen
compounds on Appendix H of this Part at low levels. USEPA stated that it
recognizes that in practice the presence of these compounds will be functionally
limited by the molecular weight and the total halogen limit of 540 ppm.
(Source: Amended at 24 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.
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).
149
F012
Cyanide (complexed).
F019
Hexavalent chromium, cyanide (complexed).
F020
Tetra- and pentachlorodibenzo-p-dioxins; tetra- and
pentachlorodibenzofurans; tri- and tetrachlorophenols and their
clorophenoxy derivative acids, esters, ethers, amines and other salts.
F021
Penta- and hexachlorodibenzo-p-dioxins; penta- and
hexachlorodibenzofurans; pentachlorophenol and its derivatives.
F022
Tetra-, penta- and hexachlorodibenzo-p-dioxins; tetra-, penta- and
hexachlorodibenzofurans.
F023
Tetra- and pentachlorodibenzo-p-dioxins; tetra- and
pentachlorodibenzofurans; tri- and tetra- chlorophenols and their
chlorophenoxy derivative acids, esters, ethers, amines and other salts.
F024
Chloromethane, dichloromethane, trichloromethane, carbon tetrachloride,
chloroethylene, 1,1-dichloroethane, 1,2-dichloroethane, trans-1,2-
dichloroethylene, 1,1-dichloroethylene, 1,1,1-trichloroethane, 1,1,2-
trichloroethane, trichloroethylene, 1,1,1,2-tetrachloroethane, 1,1,2,2-
tetrachloroethane, tetrachloroethylene, pentachloroethane, hexachloroethane,
allyl chloride (3-chloropropene), dichloropropane, dichloropropene, 2-
chloro-1,3-butadiene, hexachloro-1,3-butadiene, hexachlorochylopentadiene,
hexachlorocylohexane, benzene, chlorobenzene, dichlorobenzenes, 1,2,4-
trichlorobenzene, tetrachlorobenzenes, pentachlorobenzene,
hexachlorobenzene, toluene, naphthalene.
F025
Chloromethane, dicloromethane, trichloromethane; carbon tetrachloride;
chloroethylene; 1,1-dichloroethane; 1,2-dichloroethane; trans-1,2-
dichloroethylene; 1,1-dichloroethylene; 1,1,1-trichloroethane; 1,1,2-
trichloroethane; trichloroethylene; 1,1,1,2-tetrachloroethane; 1,1,2,2-
tetrachloroethane; tetrachloroethylene; pentachloroethane; hexachloroethane;
allyl chloride (3-chloropropene); dichloropropane; dichloropropene; 2-
chloro-1,3-butadiene; hexachloro-1,3-butadiene; hexachlorocyclopentadiene;
benzene; chlorobenzene; dichlorobenzene; 1,2,4-trichlorobenzene;
tetrachlorobenzene; pentachlorobenzene; hexachlorobenzene; toluene;
naphthalene.
F026
Tetra-, penta-, and hexachlorodibenzo-p-dioxins; tetra-, penta-, and
hexachlorodibenzofurans.
F027
Tetra-, penta, and hexachlorodibenzo-p-dioxins; tetra-, penta-, and
hexachlorodibenzofurans; tri-, tetra-, and pentachlorophenols and their
chlorophenoxy derivative acids, esters, ethers, amine 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, amine 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-,
heptachlorordibenzo-p-dioxins, tetra-, penta-, hexa-,
heptachlorodibenzofurans.
150
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, chrysene, naphthalene, fluoranthene,
benzo(b)fluoranthene, benzo(a)pyrene, indeno(1,2,3-cd)pyrene, benz(a)
anthracene, dibenz(a)anthracene, acenaphthalene.
K002
Hexavalent chromium, lead.
K003
Hexavalent chromium, lead.
K004
Hexavalent chromium.
K005
Hexavalent chromium, lead.
K006
Hexavalent chromium.
K007
Cyanide (complexed), hexavalent chromium.
K008
Hexavalent chromium.
K009
Chloroform, formaldehyde, methylene chloride, methyl chloride,
paraldehyde, formic acid.
K010
Chloroform, formaldehyde, methylene chloride, methyl chloride,
paraldehyde, formic acid, chloroacetaldehyde.
K011
Acrylonitrile, acetonitrile, hydrocyanic acid.
K013
Hydrocyanic acid, acrylonitrile, acetonitrile.
K014
Acetonitrile, acrylamide.
K015
Benzyl chloride, chlorobenzene, toluene, benzotrichloride.
K016
Hexachlorobenzene, hexachlorobutadiene, carbon tetrachloride,
hexachloroethane, perchloroethylene.
K017
Epichlorohydrin, chloroethers [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).
151
K023
Phthalic anhydride, maleic anhydride.
K024
Phthalic anhydride, 1,4-naphthoguinone.
K025
Meta-dinitrobenzene, 2,4-dinitrotoluene.
K026
Paraldehyde, pyridines, 2-picoline.
K027
Toluene diisocyanate, toluene-2,4-diamine.
K028
1,1,1-trichloroethane, vinyl chloride.
K029
1,2-dichloroethane, 1,1,1-trichloroethane, vinyl chloride, vinylidene
chloride, chloroform.
K030
Hexachlorobenzene, hexachlorobutadiene, hexachloroethane, 1,1,1,2-
tetrachloroethane, 1,1,2,2-tetrachloroethane, ethylene dichloride.
K031
Arsenic.
K032
Hexachlorocyclopentadiene.
K033
Hexachlorocyclopentadiene.
K034
Hexachlorocyclopentadiene.
K035
Creosote, chrysene, naphthalene, fluoranthene, benzo(b) fluoranthene,
benzo(a)-pyrene, indeno(1,2,3-cd) pyrene, benzo(a)anthracene,
dibenzo(a)anthracene, acenaphthalene.
K036
Toluene, phosphorodithioic and phosphorothioic acid esters.
K037
Toluene, phosphorodithioic and phosphorothioic acid esters.
K038
Phorate, formaldehyde, phosphorodithioic and phosphorothioic acid esters.
K039
Phosphorodithioic and phosphorothioic acid esters.
K040
Phorate, formaldehyde, phosphorodithioic and phosphorothioic acid esters.
K041
Toxaphene.
K042
Hexachlorobenzene, ortho-dichlorobenzene.
K043
2,4-dichlorophenol, 2,6-dichlorophenol, 2,4,6-trichlorophenol.
K044
N.A.
K045
N.A.
K046
Lead.
K047
N.A.
K048
Hexavalent chromium, lead.
K049
Hexavalent chromium, lead.
K050
Hexavalent chromium.
K051
Hexavalent chromium, lead.
K052
Lead.
K060
Cyanide, naphthalene, phenolic compounds, arsenic.
K061
Hexavalent chromium, lead, cadmium.
K062
Hexavalent chromium, lead.
K064
Lead, cadmium.
K065
Lead, cadmium.
K066
Lead, cadmium.
K069
Hexavalent chromium, lead, cadmium.
K071
Mercury.
K073
Chloroform, carbon tetrachloride, hexachloroethane, trichloroethane,
tetrachloroethylene, dichloroethylene, 1,1,2,2-tetrachloroethane.
K083
Aniline, diphenylamine, nitrobenzene, phenylenediamine.
152
K084
Arsenic.
K085
Benzene, dichlorobenzenes, trichlorobenzenes, tetrachlorobenzenes,
pentachlorobenzene, hexachlorobenzene, benzyl chloride.
K086
Lead, hexavalent chromium.
K087
Phenol, naphthalene.
K088
Cyanide (complexes).
K090
Chromium.
K091
Chromium.
K093
Phthalic anhydride, maleic anhydride.
K094
Phthalic anhydride.
K095
1,1,2-trichloroethane, 1,1,1,2-tetrachloroethane, 1,1,2,2-tetrachloroethane.
K096
1,2-dichloroethane, 1,1,1-trichloroethane, 1,1,2-trichloroethane.
K097
Chlordane, heptachlor.
K098
Toxaphene.
K099
2,4-dichlorophenol, 2,4,6-trichlorophenol.
K100
Hexavalent chromium, lead, cadmium.
K101
Arsenic.
K102
Arsenic.
K103
Aniline, nitrobenzene, phenylenediamine.
K104
Aniline, benzene, diphenylamine, nitrobenzene, phynylenediamine.
K105
Benzene, monochlorobenzene, dichlorobenzenes, 2,4,6-trichlorophenol.
K106
Mercury.
K111
2,4-Dinitrotoluene.
K112
2,4-Toluenediamine, o-toluidine, p-toluidine, aniline.
K113
2,4-Toluenediamine, o-toluidine, p-toluidine, aniline.
K114
2,4-Toluenediamine, o-toluidine, p-toluidine.
K115
2,4-Toluenediamine.
K116
Carbon tetrachloride, tetrachloroethylene, chloroform, phosgene.
K117
Ethylene dibromide.
K118
Ethylene dibromide.
K123
Ethylene thiourea.
K124
Ethylene thiourea.
K125
Ethylene thiourea.
K126
Ethylene thiourea.
K131
Dimethyl sulfate, methyl bromide.
K132
Methyl bromide.
K136
Ethylene dibromide.
K140
2,4,6-Tribromophenol.
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.
153
K145
Benzene, benz(a)anthracene, benzo(a)pyrene, dibenz(a,h)anthracene,
naphthalene.
K147
Benzene, benz(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene,
benzo(k)fluoranthene, dibenz(a,h)anthracene, indeno(1,2,3-cd)pyrene.
K148
Benz(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene,
benzo(k)fluoranthene, dibenz(a,h)anthracene, indeno(1,2,3-cd)pyrene.
K149
Benzotrichloride, benzyl chloride, chloroform, chloromethane,
chlorobenzene, 1,4-dichlorobenzene, hexachlorobenzene,
pentachlorobenzene, 1,2,4,5-tetrachlorobenzene, toluene.
K150
Carbon tetrachloride, chloroform, chloromethane, 1,4-dichlorobenzene,
hexachlorobenzene, pentachlorobenzene, 1,2,4,5-tetrachlorobenzene,
1,1,2,2-tetrachloroethane, tetrachloroethylene, 1,2,4-trichlorobenzene.
K151
Benzene, carbon tetrachloride, chloroform, hexachlorobenzene,
pentachlorobenzene, toluene, 1,2,4,5-tetrachlorobenzene,
tetrachloroethylene.
K156
Benomyl, carbaryl, carbendazim, carbofuran, carbosulfan, formaldehyde,
methylene chloride, triethylamine.
K157
Carbon tetrachloride, formaldehyde, methyl chloride, methylene chloride,
pyridine, triethylamine.
K158
Benomyl, carbendazim, carbofuran, carbosulfan, chloroform, methylene
chloride.
K159
Benzene, butylate, EPTC, molinate, pebulate, vernolate.
K161
Antimony, arsenic, metam-sodium, ziram.
K169
Benzene.
K170
Benzo(a)pyrene, dibenz(a,h)anthracene, benzo (a) anthracene,
benzo(b)fluoranthene, benzo(k)fluoranthene, 3-methylcholanthrene, 7,12-
dimethylbenz(a)anthracene.
K171
Benzene, arsenic.
K172
Benzene, arsenic.
N.A.--Waste is hazardous because it fails the test for the characteristic of ignitability,
corrosivity, or reactivity.
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
Section 721.Appendix H
Hazardous Constituents
Common Name
Chemical Abstracts Name
Chemical
Abstracts
Number
(CAS No.)
USEPA
Hazard-
ous Waste
Number
A2213
Ethanimidothioic acid, 2-
(dimethylamino)-N-hydroxy-2-
oxo-, methyl ester
30558-43-1
U394
154
Acetonitrile
Same
75-05-8
U003
Acetophenone
Ethanone, 1-phenyl-
98-86-2
U004
2-Acetylaminofluorene
Acetamide, N-9H-fluoren-2-yl-
53-96-3
U005
Acetyl chloride
Same
75-36-5
U006
1-Acetyl-2-thiourea
Acetamide, N-
(aminothioxomethyl)-
591-08-2
P002
Acrolein
2-Propenal
107-02-8
P003
Acrylamide
2-Propenamide
79-06-1
U007
Acrylonitrile
2-Propenenitrile
107-13-1
U009
Aflatoxins
Same
1402-68-2
Aldicarb
Propanal, 2-methyl-2-
(methylthio)-, O-
[(methylamino)carbonyl]oxime
116-06-3
P070
Aldicarb sulfone
Propanal, 2-methyl-2- (methyl-
sulfonyl)-, O-[(methylamino)-
carbonyl]oxime
1646-88-4
P203
Aldrin
1,4,5,8-Dimethanonaphthalene,
1,2,3,4,10,10-hexachloro-
1,4,4a,5,8,8a-hexahydro-, (1-
α
,4-
α
,4a-
β
,5-
α
,8-
α
,8a-
β
)-
309-00-2
P004
Allyl alcohol
2-Propen-1-ol
107-18-6
P005
Allyl chloride
1-Propene, 3-chloro-
107-18-6
Aluminum phosphide
Same
20859-73-8
P006
4-Aminobiphenyl
[1,1'-Biphenyl]-4-amine
92-67-1
5-(Aminomethyl)-3-isoxazolol
3(2H)-Isoxazolone, 5-(amino-
methyl)-
2763-96-4
P007
4-Aminopyridine
4-Pyridinamine
504-24-5
P008
Amitrole
1H-1,2,4-Triazol-3-amine
61-82-5
U011
Ammonium vanadate
Vanadic acid, ammonium salt
7803-55-6
U119
Aniline
Benzenamine
62-53-3
U012
Antimony
Same
7440-36-0
Antimony compounds, N.O.S.
(not otherwise specified)
Aramite
Sulfurous acid, 2-chloroethyl-,
2-[4-(1,1-dimethylethyl)-
phenoxy]-1-methylethyl ester
140-57-8
Arsenic
Arsenic
7440-38-2
Arsenic compounds, N.O.S.
Arsenic acid
Arsenic acid H
3
AsO
4
7778-39-4
P010
Arsenic pentoxide
Arsenic oxide As
2
O
5
1303-28-2
P011
Arsenic trioxide
Arsenic oxide As
2
O
3
1327-53-3
P012
Auramine
Benzenamine, 4,4'-carbon-
imidoylbis[N, N-dimethyl-
492-80-8
U014
Azaserine
L-Serine, diazoacetate (ester)
115-02-6
U015
155
Barban
Carbamic acid, (3-chloro-
phenyl)-, 4-chloro-2-butynyl
ester
101-27-9
U280
Barium
Same
7440-39-3
Barium compounds, N.O.S.
Barium cyanide
Same
542-62-1
P013
Bendiocarb
1,3-Benzodioxol-4-ol-2,2-
dimethyl-, methyl carbamate
22781-23-3
U278
Bendiocarb phenol
1,3-Benzodioxol-4-ol-2,2-
dimethyl-,
22961-82-6
U364
Benomyl
Carbamic acid, [1- [(butyl-
amino)carbonyl]-1H-benz-
imidazol-2-yl]-, methyl ester
17804-35-2
U271
Benz[c]acridine
Same
225-51-4
U016
Benz[a]anthracene
Same
56-55-3
U018
Benzal chloride
Benzene, (dichloromethyl)-
98-87-3
U017
Benzene
Same
71-43-2
U018
Benzenearsonic acid
Arsonic acid, phenyl-
98-05-5
Benzidine
[1,1'-Biphenyl]-4,4'-diamine
92-87-5
U021
Benzo[b]fluoranthene
Benz[e]acephenanthrylene
205-99-2
Benzo[j]fluoranthene
Same
205-82-3
Benzo(k)fluoranthene
Same
207-08-9
Benzo[a]pyrene
Same
50-32-8
U022
p-Benzoquinone
2,5-Cyclohexadiene-1,4-dione
106-51-4
U197
Benzotrichloride
Benzene, (trichloromethyl)-
98-07-7
U023
Benzyl chloride
Benzene, (chloromethyl)-
100-44-7
P028
Beryllium powder
Same
7440-41-7
P015
Beryllium compounds, N.O.S.
Bis(pentamethylene)thiuram
tetrasulfide
Piperidine, 1,1'-(tetrathio-
dicarbonothioyl)-bis-
120-54-7
Bromoacetone
2-Propanone, 1-bromo-
598-31-2
P017
Bromoform
Methane, tribromo-
75-25-2
U225
4-Bromophenyl phenyl ether
Benzene, 1-bromo-4-phenoxy-
101-55-3
U030
Brucine
Strychnidin-10-one, 2,3-
dimethoxy-
357-57-3
P018
Butylate
Carbamothioic acid, bis(2-
methylpropyl)-, S-ethyl ester
2008-41-5
Butyl benzyl phthalate
1,2-Benzenedicarboxylic acid,
butyl phenylmethyl ester
85-68-7
Cacodylic acid
Arsenic acid, dimethyl-
75-60-5
U136
Cadmium
Same
7440-43-9
Cadmium compounds, N.O.S.
Calcium chromate
Chromic acid H
2
CrO
4
, calcium
salt
13765-19-0
U032
Calcium cyanide
Calcium cyanide Ca(CN)
2
592-01-8
P021
156
Carbaryl
1-Naphthalenol, methyl-
carbamate
63-25-2
U279
Carbendazim
Carbamic acid, 1H-benz-
imidazol-2-yl, methyl ester
10605-21-7
U372
Carbofuran
7-Benzofuranol, 2,3-dihydro-
2,2-dimethyl-, methylcarbamate
1563-66-2
P127
Carbofuran phenol
7-Benzofuranol, 2,3-dihydro-
2,2-dimethyl-
1563-38-8
U367
Carbosulfan
Carbamic acid, [(dibutylamino)-
thio] methyl-, 2,3-dihydro-2,2-
dimethyl-7-benzofuranyl ester
55285-14-8
P189
Carbon disulfide
Same
75-15-0
P022
Carbon oxyfluoride
Carbonic difuoride
353-50-4
U033
Carbon tetrachloride
Methane, tetrachloro-
56-23-5
U211
Chloral
Acetaldehyde, trichloro-
75-87-6
U034
Chlorambucil
Benzenebutanoic acid, 4[bis-(2-
chloroethyl)amino]-
305-03-3
U035
Chlordane
4,7-Methano-1H-indene,
1,2,4,5,6,7,8,8-octachloro-
2,3,3a,4,7,7a-hexahydro-
57-74-9
U036
Chlordane,
α
and
γ
isomers
U036
Chlorinated benzenes, N.O.S.
Chlorinated ethane, N.O.S.
Chlorinated fluorocarbons,
N.O.S.
Chlorinated naphthalene, N.O.S.
Chlorinated phenol, N.O.S.
Chlornaphazine
Naphthalenamine, N,N’-bis(2-
chloroethyl)-
494-03-1
U026
Chloroacetaldehyde
Acetaldehyde, chloro-
107-20-0
P023
Chloroalkyl ethers, N.O.S.
p-Chloroaniline
Benzenamine, 4-chloro-
106-47-8
P024
Chlorobenzene
Benzene, chloro-
108-90-7
U037
Chlorobenzilate
Benzeneacetic acid, 4-chloro-
α
-
(4-chlorophenyl)-
α
-hydroxy-,
ethyl ester
510-15-6
U038
p-Chloro-m-cresol
Phenol, 4-chloro-3-methyl-
59-50-7
U039
2-Chloroethyl vinyl ether
Ethene, (2-chloroethoxy)-
110-75-8
U042
Chloroform
Methane, trichloro-
67-66-3
U044
Chloromethyl methyl ether
Methane, chloromethoxy-
107-30-2
U046
β
-Chloronaphthalene
Naphthalene, 2-chloro-
91-58-7
U047
o-Chlorophenol
Phenol, 2-chloro-
95-57-8
U048
1-(o-Chlorophenyl)thiourea
Thiourea, (2-chlorophenyl)-
5344-82-1
P026
Chloroprene
1,3-Butadiene, 2-chloro-
126-99-8
3-Chloropropionitrile
Propanenitrile, 3-chloro-
542-76-7
P027
157
Chromium
Same
7440-47-3
Chromium compounds, N.O.S.
Chrysene
Same
218-01-9
U050
Citrus red No. 2
2-Naphthalenol, 1-[(2,5-
dimethoxyphenyl)azo]-
6358-53-8
Coal tar creosote
Same
8007-45-2
Copper cyanide
Copper cyanide CuCN
544-92-3
P029
Copper dimethyldithiocarbamate
Copper, bis(dimethylcarbamo-
dithioato-S,S’)-,
137-29-1
Creosote
Same
U051
Cresols (Cresylic acid)
Phenol, methyl-
1319-77-3
U052
Crotonaldehyde
2-Butenal
4170-30-3
U053
m-Cumenyl methylcarbamate
Phenol, 3-(methylethyl)-, methyl
carbamate
64-00-6
P202
Cyanides (soluble salts and
complexes), N.O.S.
P030
Cyanogen
Ethanedinitrile
460-19-5
P031
Cyanogen bromide
Cyanogen bromide (CN)Br
506-68-3
U246
Cyanogen chloride
Cyanogen chloride (CN)Cl
506-77-4
P033
Cycasin
β
-D-glucopyranoside, (methyl-
ONN-azoxy)methyl-
14901-08-7
Cycloate
Carbamothioic acid, cyclohexyl-
ethyl-, S-ethyl ester
1134-23-2
2-Cyclohexyl-4,6-dinitrophenol
Phenol, 2-cyclohexyl-4,6-
dinitro-
131-89-5
P034
Cyclophosphamide
2H-1,3,2-Oxazaphosphorin-2-
amine, N,N-bis(2-chloro-
ethyl)tetrahydro-, 2-oxide
50-18-0
U058
2,4-D
Acetic acid, (2,4-dichloro-
phenoxy)-
94-75-7
U240
2,4-D, salts and esters
Acetic acid, (2,4-
dichlorophenoxy)-, salts and
esters
U240
Daunomycin
5, 12-Naphthacenedione, 8-
acetyl-10-[(3-amino-2,3,6-
trideoxy-
α
-L-lyxo-hexo-
pyranosyl)oxy]-7,8,9,10-
tetrahydro-6,8,11-trihydroxy-l-
methoxy-, 8S-cis)-
20830-81-3
U059
Dazomet
2H-1,3,5-thiadiazine-2-thione,
tetrahydro-3,5-dimethyl
533-74-4
DDD
Benzene, 1,1'-(2,2-dichloro-
ethylidene)bis[4-chloro-
72-54-8
U060
DDE
Benzene, 1,1'-(dichloroethenyl-
idene)bis[4-chloro-
72-55-9
158
DDT
Benzene, 1,1'-(2,2,2-trichloro-
ethylidene)bis[4-chloro-
50-29-3
U061
Diallate
Carbamothioic acid, bis(1-
methylethyl)-, S-(2,3-dichloro-
2-propenyl) ester
2303-16-4
U062
Dibenz[a,h]acridine
Same
226-36-8
Dibenz[a,j]acridine
Same
224-42-0
Dibenz[a,h]anthracene
Same
53-70-3
U063
7H-Dibenzo[c,g]carbazole
Same
194-59-2
Dibenzo[a,e]pyrene
Naphtho[1,2,3,4-def]chrysene
192-65-4
Dibenzo[a,h]pyrene
Dibenzo[b,def]chrysene
189-64-0
Dibenzo[a,i]pyrene
Benzo[rst]pentaphene
189-55-9
U064
1,2-Dibromo-3-chloropropane
Propane, 1,2-dibromo-3-chloro-
96-12-8
U066
Dibutyl phthalate
1,2-Benzenedicarboxylic acid,
dibutyl ester
84-74-2
U069
o-Dichlorobenzene
Benzene, 1,2-dichloro-
95-50-1
U070
m-Dichlorobenzene
Benzene, 1,3-dichloro-
541-73-1
U071
p-Dichlorobenzene
Benzene, 1,4-dichloro-
106-46-7
U072
Dichlorobenzene, N.O.S.
Benzene, dichloro-
25321-22-6
3,3'-Dichlorobenzidine
[1,1'-Biphenyl]-4,4'-diamine,
3,3'-dichloro-
91-94-1
U073
1,4-Dichloro-2-butene
2-Butene, 1,4-dichloro-
764-41-0
U074
Dichlorodifluoromethane
Methane, dichlorodifluoro-
75-71-8
U075
Dichloroethylene, N.O.S.
Dichloroethylene
25323-30-2
1,1-Dichloroethylene
Ethene, 1,1-dichloro-
75-35-4
U078
1,2-Dichloroethylene
Ethene, 1,2-dichloro-, (E)-
156-60-5
U079
Dichloroethyl ether
Ethane, 1,1'-oxybis[2-chloro-
111-44-4
U025
Dichloroisopropyl ether
Propane, 2,2'-oxybis[2-chloro-
108-60-1
U027
Dichloromethoxyethane
Ethane, 1,1'-[methylenebis-
(oxy)bis[2-chloro-
111-91-1
U024
Dichloromethyl ether
Methane, oxybis[chloro-
542-88-1
P016
2,4-Dichlorophenol
Phenol, 2,4-dichloro-
120-83-2
U081
2,6-Dichlorophenol
Phenol, 2,6-dichloro-
87-65-0
U082
Dichlorophenylarsine
Arsonous dichloride, phenyl-
696-28-6
P036
Dichloropropane, N.O.S.
Propane, dichloro-
26638-19-7
Dichloropropanol, N.O.S.
Propanol, dichloro-
26545-73-3
Dichloropropene, N.O.S.
1-Propene, dichloro-
26952-23-8
1,3-Dichloropropene
1-Propene, 1,3-dichloro-
542-75-6
U084
Dieldrin
2,7:3,6-Dimethanonaphth[2, 3-
b]oxirene,3,4,5,6,9,9-hexa-
chloro-1a,2,2a,3,6, 6a,7,7a-
octahydro-,
(1a
α
,2
β
,2a
α
,3
β
,6
β
,6a
α
,7
β
,7a
α
)-
60-57-1
P037
1,2:3,4-Diepoxybutane
2,2'-Bioxirane
1464-53-5
U085
159
Diethylarsine
Arsine, diethyl-
692-42-2
P038
Diethylene glycol, dicarbamate
Ethanol, 2,2'-oxybis-,
dicarbamate
5952-26-1
U395
1,4-Diethyleneoxide
1,4-Dioxane
123-91-1
U108
Diethylhexyl phthalate
1,2-Benzenedicarboxylic acid,
bis(2-ethylhexyl) ester
117-81-7
U028
N,N’-Diethylhydrazine
Hydrazine, 1,2-diethyl-
1615-80-1
U086
O,O-Diethyl-S-methyl dithio-
phosphate
Phosphorodithioic acid, O,O-
diethyl S-methyl ester
3288-58-2
U087
Diethyl-p-nitrophenyl phosphate
Phosphoric acid, diethyl 4-nitro-
phenyl ester
311-45-5
P041
Diethyl phthalate
1,2-Benzenedicarboxylic acid,
diethyl ester
84-66-2
U088
O,O-Diethyl O-pyrazinyl
phosphorothioate
Phosphorothioic acid, O,O-
diethyl O-pyrazinyl ester
297-97-2
P040
Diethylstilbestrol
Phenol, 4,4'-(1,2-diethyl-1,2-
ethenediyl)bis-, (E)-
56-53-1
U089
Dihydrosafrole
1,3-Benzodioxole, 5-propyl-
94-58-6
U090
Diisopropylfluorophosphate
(DFP)
Phosphorofluoridic acid, bis(1-
methylethyl) ester
55-91-4
P043
Dimethoate
Phosphorodithioic acid, O,O-
dimethyl S-[2-(methylamino)-2-
oxoethyl] ester
60-51-5
P044
Dimetilan
Carbamic acid, dimethyl-, 1-
[(dimethylamino) carbonyl]-5-
methyl-1H-pyrazol-3-yl ester
644-64-4
P191
3,3'-Dimethoxybenzidine
[1,1'-Biphenyl]-4,4'-diamine,
3,3'-dimethoxy-
119-90-4
U091
p-Dimethylaminoazobenzene
Benzenamine, N,N-dimethyl-4-
(phenylazo)-
60-11-7
U093
7,12-Dimethylbenz[a]anthracene
Benz[a]anthracene, 7,12-
dimethyl-
57-97-6
U094
3,3'-Dimethylbenzidine
[1,1'-Biphenyl]-4,4'-diamine,
3,3'-dimethyl-
119-93-7
U095
Dimethylcarbamoyl chloride
Carbamic chloride, dimethyl-
79-44-7
U097
1,1-Dimethylhydrazine
Hydrazine, 1,1-dimethyl-
57-14-7
U098
1,2-Dimethylhydrazine
Hydrazine, 1,2-dimethyl-
540-73-8
U099
α
,
α
-Dimethylphenethylamine
Benzeneethanamine,
α
,
α
-
dimethyl-
122-09-8
P046
2,4-Dimethylphenol
Phenol, 2,4-dimethyl-
105-67-9
U101
Dimethylphthalate
1,2-Benzenedicarboxylic acid,
dimethyl ester
131-11-3
U102
Dimethyl sulfate
Sulfuric acid, dimethyl ester
77-78-1
U103
Dinitrobenzene, N.O.S.
Benzene, dinitro-
25154-54-5
4,6-Dinitro-o-cresol
Phenol, 2-methyl-4,6-dinitro-
534-52-1
P047
160
4,6-Dinitro-o-cresol salts
P047
2,4-Dinitrophenol
Phenol, 2,4-dinitro-
51-28-5
P048
2,4-Dinitrotoluene
Benzene, 1-methyl-2,4-dinitro-
121-14-2
U105
2,6-Dinitrotoluene
Benzene, 2-methyl-1,3-dinitro-
606-20-2
U106
Dinoseb
Phenol, 2-(1-methylpropyl)-4,6-
dinitro-
88-85-7
P020
Di-n-octyl phthalate
1,2-Benzenedicarboxylic acid,
dioctyl ester
117-84-0
U107
Diphenylamine
Benzenamine, N-phenyl-
122-39-4
1,2-Diphenylhydrazine
Hydrazine, 1,2-diphenyl-
122-66-7
U109
Di-n-propylnitrosamine
1-Propanamine, N-nitroso-N-
propyl-
621-64-7
U111
Disulfiram
Thioperoxydicarbonic diamide,
tetraethyl
97-77-8
Disulfoton
Phosphorodithioic acid, O,O-
diethyl S-[2-(ethylthio)ethyl]
ester
298-04-4
P039
Dithiobiuret
Thioimidodicarbonic diamide
[(H
2
N)C(S)]
2
NH
541-53-7
P049
Endosulfan
6, 9-Methano-2,4,3-benzodioxa-
thiepen,6,7,8,9,10,10-
hexachloro-1,5,5a,6,9,9a-
hexahydro-, 3-oxide,
115-29-7
P050
Endothal
7-Oxabicyclo[2.2.1]heptane-
2,3-dicarboxylic acid
145-73-3
P088
Endrin
2,7:3,6-Dimethanonaphth[2,3-
b]oxirene, 3,4,5,6,9,9-hexa-
chloro-1a,2,2a,3,6,6a,7,7a-
octahydro-, (1a
α
,2
β
,2a
β
,3
α
,6
α
,6a
β
,7
β
,7a
α
)-
,
72-20-8
P051
Endrin metabolites
P051
Epichlorohydrin
Oxirane, (chloromethyl)-
106-89-8
U041
Epinephrine
1,2-Benzenediol, 4-[1-hydroxy-
2-(methylamino)ethyl]-, (R)-
51-43-4
P042
EPTC
Carbamothioic acid, dipropyl-,
S-ethyl ester
759-94-4
Ethyl carbamate (urethane)
Carbamic acid, ethyl ester
51-79-6
U238
Ethyl cyanide
Propanenitrile
107-12-0
P101
Ethylenebisdithiocarbamic acid
Carbamodithioic acid, 1,2-
ethanediylbis-
111-54-6
U114
Ethylenebisdithiocarbamic acid,
salts and esters
U114
Ethylene dibromide
Ethane, 1,2-dibromo-
106-93-4
U067
Ethylene dichloride
Ethane, 1,2-dichloro-
107-06-2
161
Ethylene glycol monoethyl ether
Ethanol, 2-ethoxy-
110-80-5
U359
Ethyleneimine
Aziridine
151-56-4
P054
Ethylene oxide
Oxirane
75-21-8
U115
Ethylenethiourea
2-Imidazolidinethione
96-45-7
U116
Ethylidine dichloride
Ethane, 1,1-dichloro-
75-34-3
U076
Ethyl methacrylate
2-Propenoic acid, 2-methyl-,
ethyl ester
97-63-2
U118
Ethyl methanesulfonate
Methanesulfonic acid, ethyl
ester
62-50-0
U119
Ethyl Ziram
Zinc, bis(diethylcarbamo-
dithioato-S,S’)-
14324-55-1
U407
Famphur
Phosphorothioc acid, O-[4-
[(dimethylamino)sulfonyl]-
phenyl] O,O-dimethyl ester
52-85-7
P097
Ferbam
Iron, tris(dimethylcarbamo-
dithioato-S,S’)-,
14484-64-1
Fluoranthene
Same
206-44-0
U120
Fluorine
Same
7782-41-4
P056
Fluoroacetamide
Acetamide, 2-fluoro-
640-19-7
P057
Fluoroacetic acid, sodium salt
Acetic acid, fluoro-, sodium salt
62-74-8
P058
Formaldehyde
Same
50-00-0
U122
Formetanate hydrochloride
Methanimidamide, N,N-
dimethyl-N’-[3-[[(methylamino)-
carbonyl]oxy]phenyl]-, mono-
hydrochloride
23422-53-9
P198
Formic acid
Same
64-18-16
U123
Formparanate
Methanimidamide, N,N-
dimethyl-N’-[2-methyl-4-
[[(methylamino)carbonyl]oxy]-
phenyl]-
17702-57-7
P197
Glycidylaldehyde
Oxiranecarboxaldehyde
765-34-4
U126
Halomethanes, N.O.S.
Heptachlor
4,7-Methano-1H-
indene,1,4,5,6,7,8,8-
heptachloro-3a,4,7,7a-tetra-
hydro-
76-44-8
P059
Heptachlor epoxide
2,5-Methano-2H-indeno[1,
2b]oxirene, 2,3,4,5,6,7,7-hepta-
chloro-1a,1b,5,5a,6,6a-hexa-
hydro-,
(1a
α
,1b
β
,2
α
,5
α
,5a
β
,6
β
,6a
α
)-
1024-57-3
Heptachlor epoxide (
α
,
β
, and
γ
isomers)
Heptachlorodibenzofurans
Heptachlorodibenzo-p-dioxins
162
Hexachlorobenzene
Benzene, hexachloro-
118-74-1
U127
Hexachlorobutadiene
1,3-Butadiene, 1,1,2,3,4,4-
hexachloro-
87-68-3
U128
Hexachlorocyclo-pentadiene
1,3-Cyclopentadiene,
1,2,3,4,5,5-hexachloro-
77-47-4
U130
Hexachlorodibenzo-p-dioxins
Hexachlorodibenzofurans
Hexachloroethane
Ethane, hexachloro-
67-72-1
U131
Hexachlorophene
Phenol, 2,2'-methylene-
bis[3,4,6-trichloro-
70-30-4
U132
Hexachloropropene
1-Propene, 1,1,2,3,3,3-
hexachloro-
1888-71-7
U243
Hexaethyltetraphosphate
Tetraphosphoric acid, hexaethyl
ester
757-58-4
P062
Hydrazine
Same
302-01-2
U133
Hydrogen cyanide
Hydrocyanic acid
74-90-8
P063
Hydrogen fluoride
Hydrofluoric acid
7664-39-3
U134
Hydrogen sulfide
Hydrogen sulfide H
2
S
7783-06-4
U135
Indeno[1,2,3-cd]pyrene
Same
193-39-5
U137
3-Iodo-2-propynyl-n-butyl-
carbamate
Carbamic acid, butyl-, 3-iodo-2-
propynyl ester
55406-53-6
Isobutyl alcohol
1-Propanol, 2-methyl-
78-83-1
U140
Isodrin
1,4:5,8-Dimethanonaph-
thalene,1,2,3,4,10,10-hexa-
chloro-1,4,4a,5,8,8a-
hexahydro-,
(1
α
,4
α
,4a
β
,5
β
,8
β
,8a
β
)-,
465-73-6
P060
Isolan
Carbamic acid, dimethyl-, 3-
methyl-1-(1-methylethyl)-1H-
pyrazol-5-yl ester
119-38-0
P192
Isosafrole
1,3-Benzodioxole, 5-(1-
propenyl)-
120-58-1
U141
Kepone
1,3,4-Metheno-2H-cyclobuta-
[cd]pentalen-2-one,
1,1a,3,3a,4,5,5,5a,5b,6-
decachlorooctahydro-,
143-50-0
U142
Lasiocarpine
2-Butenoic acid, 2-methyl-, 7-
[[2,3-dihydroxy-2-(1-
methoxyethyl)-3-methyl-1-
oxobutoxy]methyl]-2,3,5,7a-
tetrahydro-1H-pyrrolizin-l-yl
ester, [1S-[1-
α
(Z),7(2S*,3R*),7a
α
]]-
303-34-1
U143
Lead
Same
7439-92-1
Lead and compounds, N.O.S.
163
Lead acetate
Acetic acid, lead (2+) salt
301-04-2
U144
Lead phosphate
Phosphoric acid, lead (2+) salt
(2:3)
7446-27-7
U145
Lead subacetate
Lead, bis(acetato-O)tetra-
hydroxytri-
1335-32-6
U146
Lindane
Cyclohexane, 1,2,3,4,5,6-hexa-
chloro-, 1
α
,2
α
,3
β
,4
α
,5
α
,6
β
)-
58-89-9
U129
Maleic anhydride
2,5-Furandione
108-31-6
U147
Maleic hydrazide
3,6-Pyridazinedione, 1,2-
dihydro-
123-33-1
U148
Malononitrile
Propanedinitrile
109-77-3
U149
Manganese dimethyldithio-
carbamate
Manganese, bis(dimethyl-
carbamodithioato-S,S’)-,
15339-36-3
P196
Melphalan
L-Phenylalanine, 4-[bis(2-
chloroethyl)amino]-
148-82-3
U150
Mercury
Same
7439-97-6
U151
Mercury compounds, N.O.S.
Mercury fulminate
Fulminic acid, mercury (2+)
salt
628-86-4
P065
Metam Sodium
Carbamodithioic acid, methyl-,
monosodium salt
137-42-8
Methacrylonitrile
2-Propenenitrile, 2-methyl-
126-98-7
U152
Methapyrilene
1,2-Ethanediamine, N,N-
dimethyl-N’-2-pyridinyl-N’-(2-
thienylmethyl)-
91-80-5
U155
Methiocarb
Phenol, (3,5-dimethyl-4-
(methylthio)-, methylcarbamate
2032-65-7
P199
Metholmyl
Ethanimidothioic acid, N-
[[(methylamino)carbonyl]oxy]-,
methyl ester
16752-77-5
P066
Methoxychlor
Benzene, 1,1'-(2,2,2-trichloro-
ethylidene)bis[4-methoxy-
72-43-5
U247
Methyl bromide
Methane, bromo-
74-83-9
U029
Methyl chloride
Methane, chloro-
74-87-3
U045
Methylchlorocarbonate
Carbonochloridic acid, methyl
ester
79-22-1
U156
Methyl chloroform
Ethane, 1,1,1-trichloro-
71-55-6
U226
3-Methylcholanthrene
Benz[j]aceanthrylene, 1,2-
dihydro-3-methyl-
56-49-5
U157
4,4'-Methylenebis(2-chloro-
aniline)
Benzenamine, 4,4'-methylene-
bis[2-chloro-
101-14-4
U158
Methylene bromide
Methane, dibromo-
74-95-3
U068
Methylene chloride
Methane, dichloro-
75-09-2
U080
Methyl ethyl ketone (MEK)
2-Butanone
78-93-3
U159
Methyl ethyl ketone peroxide
2-Butanone, peroxide
1338-23-4
U160
164
Methyl hydrazine
Hydrazine, methyl-
60-34-4
P068
Methyl iodide
Methane, iodo-
74-88-4
U138
Methyl isocyanate
Methane, isocyanato-
624-83-9
P064
2-Methyllactonitrile
Propanenitrile, 2-hydroxy-2-
methyl-
75-86-5
P069
Methyl methacrylate
2-Propenoic acid, 2-methyl-,
methyl ester
80-62-6
U162
Methyl methanesulfonate
Methanesulfonic acid, methyl
ester
66-27-3
Methyl parathion
Phosphorothioic acid, O,O-
dimethyl O-(4-nitrophenyl) ester
298-00-0
P071
Methylthiouracil
4-(1H)-Pyrimidinone, 2,3-
dihydro-6-methyl-2-thioxo-
56-04-2
U164
Metolcarb
Carbamic acid, methyl-, 3-
methylphenyl ester
1129-41-5
P190
Mexacarbate
Phenol, 4-(dimethylamino)-3,5-
dimethyl-, methylcarbamate
(ester)
315-18-4
P128
Mitomycin C
Azirino[2', 3':3, 4]pyrrolo[1,
2-a]indole-4, 7-dione, 6-amino-
8-[[(aminocarbonyl)oxy]-
methyl]-1,1a,2,8,8a,8b-
hexahydro-8a-methoxy-5-
methyl-, [1a-S-
(1a
α
,8
β
,8a
α
,8b
α
)]-,
50-07-7
U010
Molinate
1H-Azepine-1-carbothioic acid,
hexahydro-, S-ethyl ester
2212-67-1
MNNG
Guanidine, N-methyl-N’-nitro-
N-nitroso-
70-25-7
U163
Mustard gas
Ethane, 1,1'-thiobis[2-chloro-
505-60-2
U165
Naphthalene
Same
91-20-3
U165
1,4-Naphthoquinone
1,4-Naphthalenedione
130-15-4
U166
α
-Naphthylamine
1-Naphthalenamine
134-32-7
U167
β
-Naphthylamine
2-Naphthalenamine
91-59-8
U168
α
-Naphthylthiourea
Thiourea, 1-naphthalenyl-
86-88-4
P072
Nickel
Same
7440-02-0
Nickel compounds, N.O.S.
Nickel carbonyl
Nickel carbonyl Ni(CO)
4
, (T-
4)-
13463-39-3
P073
Nickel cyanide
Nickel cyanide Ni(CN)
2
557-19-7
P074
Nicotine
Pyridine, 3-(1-methyl-2-
pyrrolidinyl)-, (S)-
54-11-5
P075
Nicotine salts
P075
Nitric oxide
Nitrogen oxide NO
10102-43-9
P076
p-Nitroaniline
Benzenamine, 4-nitro-
100-01-6
P077
165
Nitrobenzene
Benzene, nitro-
98-95-3
P078
Nitrogen dioxide
Nitrogen oxide NO
2
10102-44-0
P078
Nitrogen mustard
Ethanamine, 2-chloro-N-(2-
chloroethyl)-N-methyl-
51-75-2
Nitrogen mustard, hydrochloride
salt
Nitrogen mustard N-oxide
Ethanamine, 2-chloro-N-(2-
chloroethyl)-N-methyl-, N-oxide
126-85-2
Nitrogen mustard, N-oxide,
hydrochloride salt
Nitroglycerin
1,2,3-Propanetriol, trinitrate
55-63-0
P081
p-Nitrophenol
Phenol, 4-nitro-
100-02-7
U170
2-Nitropropane
Propane, 2-nitro-
79-46-9
U171
Nitrosamines, N.O.S.
35576-91-1
N-Nitrosodi-n-butylamine
1-Butanamine, N-butyl-N-
nitroso-
924-16-3
U172
N-Nitrosodiethanolamine
Ethanol, 2,2'-(nitrosoimino)bis-
1116-54-7
U173
N-Nitrosodiethylamine
Ethanamine, N-ethyl-N-nitroso-
55-18-5
U174
N-Nitrosodimethylamine
Methanamine, N-methyl-N-
nitroso-
62-75-9
P082
N-Nitroso-N-ethylurea
Urea, N-ethyl-N-nitroso-
759-73-9
U176
N-Nitrosomethylethylamine
Ethanamine, N-methyl-N-
nitroso-
10595-95-6
N-Nitroso-N-methylurea
Urea, N-methyl-N-nitroso-
684-93-5
U177
N-Nitroso-N-methylurethane
Carbamic acid, methylnitroso-,
ethyl ester
615-53-2
U178
N-Nitrosomethylvinylamine
Vinylamine, N-methyl-N-
nitroso-
4549-40-0
P084
N-Nitrosomorpholine
Morpholine, 4-nitroso-
59-89-2
N-Nitrosonornicotine
Pyridine, 3-(1-nitroso-2-
pyrrolidinyl)-, (S)-
16543-55-8
N-Nitrosopiperidine
Piperidine, 1-nitroso-
100-75-4
U179
N-Nitrosopyrrolidine
Pyrrolidine, 1-nitroso-
930-55-2
U180
N-Nitrososarcosine
Glycine, N-methyl-N-nitroso-
13256-22-9
5-Nitro-o-toluidine
Benzenamine, 2-methyl-5-nitro-
99-55-8
U181
Octamethylpyrophosphoramide
Diphosphoramide, octamethyl-
152-16-9
P085
Osmium tetroxide
Osmium oxide OsO
4
, (T-4)
20816-12-0
P087
Oxamyl
Ethanimidothioc acid, 2-
(dimethylamino)-N-[[(methyl-
amino)carbonyl]oxy]-2-oxo-,
methyl ester
23135-22-0
P194
Paraldehyde
1,3,5-Trioxane, 2,4,6-trimethyl-
123-63-7
U182
Parathion
Phosphorothioic acid, O,O-
diethyl O-(4-nitrophenyl) ester
56-38-2
P089
166
Pebulate
Carbamothioic acid, butylethyl-,
S-propyl ester
1114-71-2
Pentachlorobenzene
Benzene, pentachloro-
608-93-5
U183
Pentachlorodibenzo-p-dioxins
Pentachlorodibenzofurans
Pentachloroethane
Ethane, pentachloro-
76-01-7
U184
Pentachloronitrobenzene (PCNB)
Benzene, pentachloronitro-
82-68-8
U185
Pentachlorophenol
Phenol, pentachloro-
87-86-5
See F027
Phenacetin
Acetamide, N-(4-ethoxyphenyl)-
62-44-2
U187
Phenol
Same
108-95-2
U188
Phenylenediamine
Benzenediamine
25265-76-3
Phenylmercury acetate
Mercury, (acetato-O)phenyl-
62-38-4
P092
Phenylthiourea
Thiourea, phenyl-
103-85-5
P093
Phosgene
Carbonic dichloride
75-44-5
P095
Phosphine
Same
7803-51-2
P096
Phorate
Phosphorodithioic acid, O,O-
diethyl S-[(ethylthio)methyl]
ester
298-02-2
P094
Phthalic acid esters, N.O.S.
Phthalic anhydride
1,3-Isobenzofurandione
85-44-9
U190
Physostigmine
Pyrrolo[2,3-b]indol-5-ol,
1,2,3,3a,8,8a-hexahydro-
1,3a,8-trimethyl-, methyl-
carbamate (ester), (3aS-cis)-
57-47-6
P204
Physostigmine salicylate
Benzoic acid, 2-hydroxy-,
compound with (3aS-cis)-
1,2,3,3a,8,8a-hexahydro-
1,3a,8-trimethylpyrrolo[2,3-b]-
indol-5-yl methylcarbamate
ester (1:1)
57-64-7
P188
2-Picoline
Pyridine, 2-methyl-
109-06-8
U191
Polychlorinated biphenyls,
N.O.S.
Potassium cyanide
Same
151-50-8
P098
Potassium dimethyldithio-
carbamate
Carbamodithioc acid, dimethyl,
potassium salt
128-03-0
Potassium n-hydroxymethyl-n-
methyl-dithiocarbamate
Carbamodithioc acid, (hydroxy-
methyl)methyl-, monopotassium
salt
51026-28-9
Potassium n-methyldithio-
carbamate
Carbamodithioc acid, methyl-
monopotassium salt
137-41-7
Potassium silver cyanide
Argentate(1-), bis(cyano-C)-,
potassium)
506-61-6
P099
Potassium pentachlorophenate
Pentachlorophenol, potassium
salt
7778736
None
167
Promecarb
Phenol, 3-methyl-5-(1-methyl-
ethyl)-, methyl carbamate
2631-37-0
P201
Pronamide
Benzamide, 3,5-dichloro-N-
(1,1-dimethyl-2-propynyl)-
23950-58-5
U192
1,3-Propane sultone
1,2-Oxathiolane, 2,2-dioxide
1120-71-4
U193
Propham
Carbamic acid, phenyl-, 1-
methylethyl ester
122-42-9
U373
Propoxur
Phenol, 2-(1-methylethoxy)-,
methylcarbamate
114-26-1
U411
n-Propylamine
1-Propanamine
107-10-8
U194
Propargyl alcohol
2-Propyn-1-ol
107-19-7
P102
Propylene dichloride
Propane, 1,2-dichloro-
78-87-5
U083
1,2-Propylenimine
Aziridine, 2-methyl-
75-55-8
P067
Propylthiouracil
4(1H)-Pyrimidinone, 2,3-
dihydro-6-propyl-2-thioxo-
51-52-5
Prosulfocarb
Carbamothioic acid, dipropyl-,
S-(phenylmethyl) ester
52888-80-9
U387
Pyridine
Same
110-86-1
U196
Reserpine
Yohimban-16-carboxylic acid,
11,17-dimethoxy-18-[(3,4,5-tri-
methoxybenzoyl)oxy]-, methyl
ester, (3
β
,16
β
,17
α
,18
β
,20
α
)-,
50-55-5
U200
Resorcinol
1,3-Benzenediol
108-46-3
U201
Saccharin
1,2-Benzisothiazol-3(2H)-one,
1,1-dioxide
81-07-2
U202
Saccharin salts
U202
Safrole
1,3-Benzodioxole, 5-(2-
propenyl)-
94-59-7
U203
Selenium
Same
7782-49-2
Selenium compounds, N.O.S.
Selenium dioxide
Selenious acid
7783-00-8
U204
Selenium sulfide
Selenium sulfide SeS
2
7488-56-4
U205
Selenium, tetrakis(dimethyl-
dithiocarbamate
Carbamodithioic acid, dimethyl-
, tetraanhydrosulfide with
orthothioselenious acid
144-34-3
Selenourea
Same
630-10-4
P103
Silver
Same
7440-22-4
Silver compounds, N.O.S.
Silver cyanide
Silver cyanide AgCN
506-64-9
P104
Silvex (2,4,5-TP)
Propanoic acid, 2-(2,4,5-
trichlorophenoxy)-
93-72-1
See F027
Sodium cyanide
Sodium cyanide NaCN
143-33-9
P106
Sodium dibutyldithiocarbamate
Carbamodithioic acid, dibutyl-,
sodium salt
136-30-1
168
Sodium diethyldithiocarbamate
Carbamodithioic acid, diethyl-,
sodium salt
148-18-5
Sodium dimethyldithiocarbamate
Carbamodithioic acid, dimethyl-
, sodium salt
128-04-1
Sodium pentachlorophenate
Pentachlorophenol, sodium salt
131522
None
Streptozotocin
D-Glucose, 2-deoxy-2-
[[(methylnitrosoamino)ca-
rbonyl]amino]-
18883-66-4
U206
Strychnine
Strychnidin-10-one
57-24-9
P108
Strychnine salts
P108
Sulfallate
Carbamodithioic acid, diethyl-,
2-chloro-2-propenyl ester
95-06-7
TCDD
Dibenzo[b,e][1,4]dioxin,
2,3,7,8-tetrachloro-
1746-01-6
Tetrabutylthiuram disulfide
Thioperoxydicarbonic diamide,
tetrabutyl
1634-02-2
Tetramethylthiuram monosulfide
Bis(dimethylthiocarbamoyl)
sulfide
97-74-5
1,2,4,5-Tetrachlorobenzene
Benzene, 1,2,4,5-tetrachloro-
95-94-3
U207
Tetrachlorodibenzo-p-dioxins
Tetrachlorodibenzofurans
Tetrachloroethane, N.O.S.
Ethane, tetrachloro-, N.O.S.
25322-20-7
1,1,1,2-Tetrachloroethane
Ethane, 1,1,1,2-tetrachloro-
630-20-6
U208
1,1,2,2-Tetrachloroethane
Ethane, 1,1,2,2-tetrachloro-
79-34-5
U209
Tetrachloroethylene
Ethene, tetrachloro-
127-18-4
U210
2,3,4,6-Tetrachlorophenol
Phenol, 2,3,4,6-tetrachloro-
58-90-2
See F027
2,3,4,6-Tetrachlorophenol,
potassium salt
Same
53535276
None
2,3,4,6-Tetrachlorophenol,
sodium salt
Same
25567559
None
Tetraethyldithiopyrophosphate
Thiodiphosphoric acid,
tetraethyl ester
3689-24-5
P109
Tetraethyl lead
Plumbane, tetraethyl-
78-00-2
P110
Tetraethylpyrophosphate
Diphosphoric acid, tetraethyl
ester
107-49-3
P111
Tetranitromethane
Methane, tetranitro-
509-14-8
P112
Thallium
Same
7440-28-0
Thallium compounds
Thallic oxide
Thallium oxide Tl
2
O
3
1314-32-5
P113
Thallium (I) acetate
Acetic acid, thallium (1+) salt
563-68-8
U214
Thallium (I) carbonate
Carbonic acid, dithallium (1+)
salt
6533-73-9
U215
Thallium (I) chloride
Thallium chloride TlCl
7791-12-0
U216
Thallium (I) nitrate
Nitric acid, thallium (1+) salt
10102-45-1
U217
169
Thallium selenite
Selenious acid, dithallium (1+)
salt
12039-52-0
P114
Thallium (I) sulfate
Sulfuric acid, dithallium (1+)
salt
7446-18-6
P115
Thioacetamide
Ethanethioamide
62-55-5
U218
Thiodicarb
Ethanimidothioic acid, N,N’-
[thiobis[(methylimino)-
carbonyloxy]]-bis-, dimethyl
ester
59669-26-0
U410
Thiofanox
2-Butanone, 3,3-dimethyl-1-
(methylthio)-, O-
[(methylamino)carbonyl]oxime
39196-18-4
P045
Thiophanate-methyl
Carbamic acid, [1,2-
phyenylenebis(iminocarbono-
thioyl)]-bis-, dimethyl ester
23564-05-8
U409
Thiomethanol
Methanethiol
74-93-1
U153
Thiophenol
Benzenethiol
108-98-5
P014
Thiosemicarbazide
Hydrazinecarbothioamide
79-19-6
P116
Thiourea
Same
62-56-6
P219
Thiram
Thioperoxydicarbonic diamide
[(H
2
N)C(S)]
2
S
2
, tetramethyl-
137-26-8
U244
Tirpate
1,3-Dithiolane-2-carbox-
aldehyde, 2,4-dimethyl-, O-
[(methylamino)carbonyl] oxime
26419-73-8
P185
Toluene
Benzene, methyl-
108-88-3
U220
Toluenediamine
Benzenediamine, ar-methyl-
25376-45-8
U221
Toluene-2,4-diamine
1,3-Benzenediamine, 4-methyl-
95-80-7
Toluene-2,6-diamine
1,3-Benzenediamine, 2-methyl-
823-40-5
Toluene-3,4-diamine
1,2-Benzenediamine, 4-methyl-
496-72-0
Toluene diisocyanate
Benzene, 1,3-diisocyanato-
methyl-
26471-62-5
U223
o-Toluidine
Benzenamine, 2-methyl-
95-53-4
U328
o-Toluidine hydrochloride
Benzeneamine, 2-methyl-,
hydrochloride
636-21-5
U222
p-Toluidine
Benzenamine, 4-methyl-
106-49-0
U353
Toxaphene
Same
8001-35-2
P123
Triallate
Carbamothioic acid, bis(1-
methylethyl)-, S-(2,3,3-tri-
chloro-2-propenyl) ester
2303-17-5
U389
2,4,6-Tribromophenol
Tribromophenol, 2,4,6-
118-79-6
U408
1,2,4-Trichlorobenzene
Benzene, 1,2,4-trichloro-
120-82-1
1,1,2-Trichloroethane
Ethane, 1,1,2-trichloro-
79-00-5
U227
Trichloroethylene
Ethene, trichloro-
79-01-6
U228
Trichloromethanethiol
Methanethiol, trichloro-
75-70-7
P118
Trichloromonofluoromethane
Methane, trichlorofluoro-
75-69-4
U121
170
2,4,5-Trichlorophenol
Phenol, 2,4,5-trichloro-
95-95-4
See F027
2,4,6-Trichlorophenol
Phenol, 2,4,6-trichloro-
88-06-2
See F027
2,4,5-T
Acetic acid, (2,4,5-trichloro-
phenoxy)-
93-76-5
See F027
Trichloropropane, N.O.S.
25735-29-9
1,2,3-Trichloropropane
Propane, 1,2,3-trichloro-
96-18-4
Triethylamine
Ethanamine, N,N-diethyl-
121-44-8
U404
O,O,O-Triethylphosphorothioate
Phosphorothioic acid, O,O,O-
triethyl ester
126-68-1
1,3,5-Trinitrobenzene
Benzene, 1,3,5-trinitro-
99-35-4
U234
Tris(l-aziridinyl)phosphine sulfide
Aziridine, 1,1',1"-phosphino-
thioylidynetris-
52-24-4
Tris(2,3-dibromopropyl)
phosphate
1-Propanol, 2,3-dibromo-,
phosphate (3:1)
126-72-7
U235
Trypan blue
2,7-Naphthalenedisulfonic acid,
3,3'-[(3,3'-dimethyl[1,1'-
biphenyl]-4,4'-diyl)-
bis(azo)]bis[5-amino-4-
hydroxy]-, tetrasodium salt
72-57-1
U236
Uracil mustard
2,4-(1H,3H)-Pyrimidinedione,
5-[bis(2-chloroethyl)amino]-
66-75-1
U237
Vanadium pentoxide
Vanadium oxide V
2
O
5
1314-62-1
P120
Vernolate
Carbamothioc acid, dipropyl-,
S-propyl ester
1929-77-7
Vinyl chloride
Ethene, chloro-
75-01-4
U043
Warfarin
2H-1-Benzopyran-2-one, 4-
hydroxy-3-(3-oxo-1-phenyl-
butyl)-, when present at
concentrations less than 0.3
percent
81-81-2
U248
Warfarin
2H-1-Benzopyran-2-one, 4-
hydroxy-3-(3-oxo-1-phenyl-
butyl)-, when present at
concentrations greater than 0.3
percent
81-81-2
P001
Warfarin salts, when present at
concentrations less than 0.3
percent
U248
Warfarin salts, when present at
concentrations greater than 0.3
percent
P001
Zinc cyanide
Zinc cyanide Zn(CN)
2
557-21-1
P121
Zinc phosphide
Zinc phosphide P
2
Zn
3
, when
present at concentrations greater
than 10 percent
1314-84-7
P122
171
Zinc phosphide
Zinc phosphide P
2
Zn
3
, when
present at concentrations of 10
percent or less
1314-84-7
U249
Ziram
Zinc, bis(dimethylcarbamo-
dithioato-S,S’)- (T-4)-
137-30-4
P205
Note: The abbreviation N.O.S. (not otherwise specified) signifies those members of the general
class that are not specifically listed by name in this Section.
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
Section 721.Appendix Y Table to Section 721.138
Chemical name
CAS No
Composite
value
(mg/kg)
Heating
value
(BTU/lb)
Concentra-
tion limit
(mg/kg at
10,000
Btu/lb)
Minimum
required
detection
limit
(mg/kg)
Total Nitrogen as N
NA
9000
18400
4900
Total Halogens as Cl
NA
1000
18400
540
Total Organic Halogens as
Cl
NA
--
--
(Note 1)
Polychlorinated biphenyls,
total [Arocolors, total]
1336-36-3
ND
--
ND
1.4
Cyanide, total
57-12-5
ND
--
ND
1.0
Metals:
Antimony, total
7440-36-0
ND
--
12
Arsenic, total
7440-38-2
ND
--
0.23
Barium, total
7440-39-3
ND
--
23
Beryllium, total
7440-41-7
ND
--
1.2
Cadmium, total
7440-43-9
--
ND
1.2
Chromium, total
7440-47-3
ND
--
2.3
Cobalt
7440-48-4
ND
--
4.6
Lead, total
7439-92-1
57
18100
31
Manganese
7439-96-5
ND
--
1.2
Mercury, total
7439-97-6
ND
--
0.25
Nickel, total
7440-02-0
106
18400
58
Selenium, total
7782-49-2
ND
--
0.23
Silver, total
7440-22-4
ND
--
2.3
Thallium, total
7440-28-0
ND
--
23
Hydrocarbons:
Benzo[a]anthracene
56-55-3
ND
--
2400
Benzene
71-43-2
8000
19600
4100
Benzo[b]fluoranthene
205-99-2
ND
--
2400
172
Benzo[k]fluoranthene
207-08-9
ND
--
2400
Benzo[a]pyrene
50-32-8
ND
--
2400
Chrysene
218-01-9
ND
--
2400
Dibenzo[a,h]anthracene
53-70-3
ND
--
2400
7,12-Dimethylbenz[a]-
anthracene
57-97-6
ND
--
2400
Fluoranthene
206-44-0
ND
--
2400
Indeno(1,2,3-cd)pyrene
193-39-5
ND
--
2400
3-Methylcholanthrene
56-49-5
ND
--
2400
Naphthalene
91-20-3
6200
19400
3200
Toluene
108-88-3
69000
19400
36000
Oxygenates:
Acetophenone
98-86-2
ND
--
2400
Acrolein
107-02-8
ND
--
39
Allyl alcohol
107-18-6
ND
--
30
Bis(2-ethylhexyl)-
phthalate [Di-2-ethyl-
hexyl phthalate]
117-81-7
ND
--
2400
Butyl benzyl phthalate
85-68-7
ND
--
2400
o-Cresol [2-Methyl
phenol]
95-48-7
ND
--
2400
m-Cresol [3-Methyl
phenol]
108-39-4
ND
--
2400
p-Cresol [4-Methyl
phenol]
106-44-5
ND
--
2400
Di-n-butyl phthalate
84-74-2
ND
--
2400
Diethyl phthalate
84-66-2
ND
--
2400
2,4-Dimethylphenol
105-67-9
ND
--
2400
Dimethyl phthalate
131-11-3
ND
--
2400
Di-n-octyl phthalate
117-84-0
ND
--
2400
Endothall
145-73-3
ND
--
100
Ethyl methacrylate
97-63-2
ND
--
39
2-Ethoxyethanol
[Ethylene glycol
monoethyl ether].
110-80-5
ND
--
100
Isobutyl alcohol
78-83-1
ND
--
39
Isosafrole
120-58-1
ND
--
2400
Methyl ethyl ketone [2-
Butanone]
78-93-3
ND
--
39
Methyl methacrylate
80-62-6
ND
--
39
1,4-Naphthoquinone
130-15-4
ND
--
2400
Phenol
108-95-2
ND
--
2400
173
Propargyl alcohol [2-
Propyn-l-ol]
107-19-7
ND
--
30.
Safrole
94-59-7
ND
--
2400
Sulfonated Organics:
Carbon disulfide
75-15-0
ND
--
ND
39
Disulfoton
298-04-4
ND
--
ND
2400
Ethyl methanesulfonate
62-50-0
ND
--
ND
2400
Methyl methane-
sulfonate
66-27-3
ND
--
ND
2400
Phorate
298-02-2
ND
--
ND
2400
1,3-Propane sultone
1120-71-4
ND
--
ND
100
Tetraethyldithiopyro-
phosphate [Sulfotepp]
3689-24-5
ND
--
ND
2400
Thiophenol [Benzene-
thiol]
108-98-5
ND
--
ND
30
O,O,O-Triethyl
phosphorothioate
126-68-1
ND
--
ND
2400
Nitrogenated Organics:
Acetonitrile [Methyl
cyanide]
75-05-8
ND
--
ND
39
2-Acetylaminofluorene
[2-AAF]
53-96-3
ND
--
ND
2400
Acrylonitrile
107-13-1
ND
--
ND
39
4-Aminobiphenyl
92-67-1
ND
--
ND
2400
4-Aminopyridine
504-24-5
ND
--
ND
100
Aniline
62-53-3
ND
--
ND
2400
Benzidine
92-87-5
ND
--
ND
2400
Dibenz[a,j]acridine
224-42-0
ND
--
ND
2400
O,O-Diethyl O-
pyrazinyl phophoro-
thioate [Thionazin].
297-97-2
ND
--
ND
2400
Dimethoate
60-51-5
ND
--
ND
2400
p-(Dimethylamino)azo-
benzene [4-Dimethyl-
aminoazobenzene].
60-11-7
ND
--
ND
2400
3,3'-Dimethylbenzidine
119-93-7
ND
--
ND
2400
a,a-Dimethylphenethyl-
amine.
122-09-8
ND
--
ND
2400
3,3'-Dimethoxy-
benzidine
119-90-4
ND
--
ND
100
1,3-Dinitrobenzene [m-
Dinitrobenzene]
99-65-0
ND
--
ND
2400
4,6-Dinitro-o-cresol
534-52-1
ND
--
ND
2400
174
2,4-Dinitrophenol
51-28-5
ND
--
ND
2400
2,4-Dinitrotoluene
121-14-2
ND
--
ND
2400
2,6-Dinitrotoluene
606-20-2
ND
--
ND
2400
Dinoseb [2-sec-Butyl-
4,6-dinitrophenol]
88-85-7
ND
--
ND
2400
Diphenylamine
122-39-4
ND
--
ND
2400
Ethyl carbamate
[Urethane]
51-79-6
ND
--
ND
100
Ethylenethiourea (2-
Imidazolidinethione)
96-45-7
ND
--
ND
110
Famphur
52-85-7
ND
--
ND
2400
Methacrylonitrile
126-98-7
ND
--
ND
39
Methapyrilene
91-80-5
ND
--
ND
2400
Methomyl
16752-77-5
ND
--
ND
57
2-Methyllactonitrile
[Acetone cyanohydrin].
75-86-5
ND
--
ND
100
Methyl parathion
298-00-0
ND
--
ND
2400
MNNG (N-Metyl-N-
nitroso-N’-nitro-
guanidine)
70-25-7
ND
--
ND
110
1-Naphthylamine, [
α
-
Naphthylamine]
134-32-7
ND
--
ND
2400
2-Naphthylamine, [
β
-
Naphthylamine]
91-59-8
ND
--
ND
2400
Nicotine
54-11-5
ND
--
ND
100
4-Nitroaniline, [p-
Nitroaniline]
100-01-6
ND
--
ND
2400
Nitrobenzene
98-95-3
ND
--
ND
2400
p-Nitrophenol, [p-
Nitrophenol]
100-02-7
ND
--
ND
2400
5-Nitro-o-toluidine
99-55-8
ND
--
ND
2400
N-Nitrosodi-n-butyl-
amine
924-16-3
ND
--
ND
2400
N-Nitrosodiethylamine
55-18-5
ND
--
ND
2400
N-Nitrosodiphenyl-
amine, [Diphenylnitros-
amine]
86-30-6
ND
--
ND
2400
N-Nitroso-N-methyl-
ethylamine
10595-95-6
ND
--
ND
2400
N-Nitrosomorpholine
59-89-2
ND
--
ND
2400
N-Nitrosopiperidine
100-75-4
ND
--
ND
2400
N-Nitrosopyrrolidine
930-55-2
ND
--
ND
2400
2-Nitropropane
79-46-9
ND
--
ND
30
175
Parathion
56-38-2
ND
--
ND
2400
Phenacetin
62-44-2
ND
--
ND
2400
1,4-Phenylene diamine,
[p-Phenylenediamine]
106-50-3
ND
--
ND
2400
N-Phenylthiourea
103-85-5
ND
--
ND
57
2-Picoline [alpha-
Picoline]
109-06-8
ND
--
ND
2400
Propythioracil [6-
Propyl-2-thiouracil]
51-52-5
ND
--
ND
100
Pyridine
110-86-1
ND
--
ND
2400
Strychnine
57-24-9
ND
--
ND
100
Thioacetamide
62-55-5
ND
--
ND
57
Thiofanox
39196-18-4
ND
--
ND
100
Thiourea
62-56-6
ND
--
ND
57
Toluene-2,4-diamine
[2,4-Diaminotoluene]
95-80-7
ND
--
ND
57
Toluene-2,6-diamine
[2,6-Diaminotoluene]
823-40-5
ND
--
ND
57
o-Toluidine
95-53-4
ND
--
ND
2400
p-Toluidine
106-49-0
ND
--
ND
100
1,3,5-Trinitrobenzne,
[sym-Trinitobenzene]
99-35-4
ND
--
ND
2400
Halogenated Organics:
Allyl chloride
107-05-1
ND
--
ND
39
Aramite
140-57-8
ND
--
ND
2400
Benzal chloride [Di-
chloromethyl benzene]
98-87-3
ND
--
ND
100
Benzyl chloride
100-44-77
ND
--
ND
100
Bis(2-chloroethyl)ether
[Dichloroethyl ether]
111-44-4
ND
--
ND
2400
Bromoform [Tribromo-
methane]
75-25-2
ND
--
ND
39
Bromomethane [Methyl
bromide]
74-83-9
ND
--
ND
39
4-Bromophenyl phenyl
ether [p-Bromodiphenyl
ether]
101-55-3
ND
--
ND
2400
Carbon tetrachloride
56-23-5
ND
--
ND
39
Chlordane
57-74-9
ND
--
ND
14
p-Chloroaniline
106-47-8
ND
--
ND
2400
Chlorobenzene
108-90-7
ND
--
ND
39
Chlorobenzilate
510-15-6
ND
--
ND
2400
p-Chloro-m-cresol
59-50-7
ND
--
ND
2400
176
2-Chloroethyl vinyl
ether
110-75-8
ND
--
ND
39
Chloroform
67-66-3
ND
--
ND
39
Chloromethane [Methyl
chloride]
74-87-3
ND
--
ND
39
2-Chloronaphthalene
[beta-Chlorophthalene]
91-58-7
ND
--
ND
2400
2-Chlorophenol [o-
Chlorophenol]
95-57-8
ND
--
ND
2400
Chloroprene [2-Chloro-
1,3-butadiene]
1126-99-8
ND
--
ND
39
2,4-D [2,4-Dichloro-
phenoxyacetic acid]
94-75-7
ND
--
ND
7.0
Diallate
2303-16-4
ND
--
ND
2400
1,2-Dibromo-3-chloro-
propane
96-12-8
ND
--
ND
39
1,2-Dichlorobenzene
[o-Dichlorobenzene]
95-50-1
ND
--
ND
2400
1,3-Dichlorobenzene
[m-Dichlorobenzene]
541-73-1
ND
--
ND
2400
1,4-Dichlorobenzene
[p-Dichlorobenzene]
106-46-7
ND
--
ND
2400
3,3'-Dichlorobenzidine
91-94-1
ND
--
ND
2400
Dichlorodifluoro-
methane [CFC-12]
75-71-8
ND
--
ND
39
1,2-Dichloroethane
[Ethylene dichloride]
107-06-2
ND
--
ND
39
1,1-Dichloroethylene
[Vinylidene chloride]
75-35-4
ND
--
ND
39
Dichloromethoxy
ethane [Bis(2-chloro-
ethoxy)methane
111-91-1
ND
--
ND
2400
2,4-Dichlorophenol
120-83-2
ND
--
ND
2400
2,6-Dichlorophenol
87-65-0
ND
--
ND
2400
1,2-Dichloropropane
[Propylene dichloride]
78-87-5
ND
--
ND
39
cis-1,3-Dichloro-
propylene
10061-01-5
ND
--
ND
39
trans-1,3-Dichloro-
propylene
10061-02-6
ND
--
ND
39
1,3-Dichloro-2-
propanol
96-23-1
ND
--
ND
30
Endosulfan I
959-98-8
ND
--
ND
1.4
Endosulfan II
33213-65-9
ND
--
ND
1.4
177
Endrin
72-20-8
ND
--
ND
1.4
Endrin aldehyde
7421-93-4
ND
--
ND
1.4
Endrin Ketone
53494-70-5
ND
--
ND
1.4
Epichlorohydrin [1-
Chloro-2,3-epoxy
propane]
106-89-8
ND
--
ND
30
Ethylidene dichloride
[1,1-Dichloroethane]
75-34-3
ND
--
ND
39
2-Fluoroacetamide
640-19-7
ND
--
ND
100
Heptachlor
76-44-8
ND
--
ND
1.4
Heptachlor epoxide
1024-57-3
ND
--
ND
2.8
Hexachlorobenzene
118-74-1
ND
--
ND
2400
Hexachloro-1,3-buta-
diene [Hexachlorobuta-
diene]
87-68-3
ND
--
ND
2400
Hexachlorocyclopenta-
diene
77-47-4
ND
--
ND
2400
Hexachloroethane
67-72-1
ND
--
ND
2400
Hexachlorophene
70-30-4
ND
--
ND
59000
Hexachloropropene
[Hexachloropropylene]
1888-71-7
ND
--
ND
2400
Isodrin
465-73-6
ND
--
ND
2400
Kepone [Chlordecone]
143-50-0
ND
--
ND
4700
Lindane [gamma-Hexa-
chlorocyclohexane]
[gamma-BHC]
58-89-9
ND
--
ND
1.4
Methylene chloride
[Dichloromethane]
75-09-2
ND
--
ND
39
4,4'-methylene-bis(2-
chloroaniline)
101-14-4
ND
--
ND
100
Methyl iodide [Iodo-
methane]
74-88-4
ND
--
ND
39
Pentachlorobenzene
608-93-5
ND
--
ND
2400
Pentachloroethane
76-01-7
ND
--
ND
39
Pentachloronitro-
benzene [PCNB]
[Quintobenzene]
[Quintozene]
82-68-8
ND
--
ND
2400
Pentachlorophenol
87-86-5
ND
--
ND
2400
Pronamide
23950-58-5
ND
--
ND
2400
Silvex [2,4,5-Tri-
chlorophenoxy-
propionic acid]
93-72-1
ND
--
ND
7.0
178
2,3,7,8-Tetrachloro-
dibenzo-p-dioxin
[2,3,7,8-TCDD]
1746-01-6
ND
--
ND
30
1,2,4,5-Tetrachloro-
benzene
95-94-3
ND
--
ND
2400
1,1,2,2-Tetrachloro-
ethane
79-34-5
ND
--
ND
39
Tetrachloroethylene
[Perchloroethylene]
127-18-4
ND
--
ND
39
2,3,4,6-Tetrachloro-
phenol
58-90-2
ND
--
ND
2400
1,2,4-Trichlorobenzene
120-82-1
ND
--
ND
2400
1,1,1-Trichloroethane
[Methyl chloroform]
71-55-6
ND
--
ND
39
1,1,2-Trichloroethane
[Vinyl trichloride]
79-00-5
ND
--
ND
39
Trichloroethylene
79-01-6
ND
--
ND
39
Trichlorofluoromethane
[Trichloromonofluoro-
methane]
75-69-4
ND
--
ND
39
2,4,5-Trichlorophenol
95-95-4
ND
--
ND
2400
2,4,6-Trichlorophenol
88-06-2
ND
--
ND
2400
1,2,3-Trichloropropane
96-18-4
ND
--
ND
39
Vinyl Chloride
75-01-4
ND
--
ND
39
NA means not applicable.
ND means nondetect.
Note 1: 25 (mg/kg at 10,000 Btu/lb) as organic halogen or as the individual halogenated
organics listed in the table at the levels indicated.
(Source: Added at 24 Ill. Reg. ________, effective ______________________)
TITLE 35: ENVIRONMENTAL PROTECTION
SUBTITLE G: WASTE DISPOSAL
CHAPTER I: POLLUTION CONTROL BOARD
SUBCHAPTER c: HAZARDOUS WASTE OPERATING REQUIREMENTS
PART 722
STANDARDS APPLICABLE TO GENERATORS OF HAZARDOUS
WASTE
179
SUBPART A: GENERAL
Section
722.110
Purpose, Scope and Applicability
722.111
Hazardous Waste Determination
722.112
USEPA Identification Numbers
SUBPART B: THE MANIFEST
Section
722.120
General Requirements
722.121
Acquisition of Manifests
722.122
Number of Copies
722.123
Use of the Manifest
SUBPART C: PRE-TRANSPORT REQUIREMENTS
Section
722.130
Packaging
722.131
Labeling
722.132
Marking
722.133
Placarding
722.134
Accumulation Time
SUBPART D: RECORDKEEPING AND REPORTING
Section
722.140
Recordkeeping
722.141
Annual Reporting
722.142
Exception Reporting
722.143
Additional Reporting
722.144
Special Requirements for Generators of between 100 and 1000 kilograms per
month
SUBPART E: EXPORTS OF HAZARDOUS WASTE
Section
722.150
Applicability
722.151
Definitions
722.152
General Requirements
722.153
Notification of Intent to Export
722.154
Special Manifest Requirements
722.155
Exception Report
722.156
Annual Reports
722.157
Recordkeeping
722.158
International Agreements
SUBPART F: IMPORTS OF HAZARDOUS WASTE
Section
722.160
Imports of Hazardous Waste
180
SUBPART G: FARMERS
Section
722.170
Farmers
SUBPART H: TRANSFRONTIER SHIPMENTS OF HAZARDOUS WASTE
FOR RECOVERY WITHIN THE OECD
Section
722.180
Applicability
722.181
Definitions
722.182
General Conditions
722.183
Notification and Consent
722.184
Tracking Document
722.185
Contracts
722.186
Provisions Relating to Recognized Traders
722.187
Reporting and Recordkeeping
722.189
OECD Waste Lists
722.Appendix A
Hazardous Waste Manifest
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 R84-9 at 9 Ill. Reg. 11950, effective July
24, 1985; amended in R85-22 at 10 Ill. Reg. 1131, effective January 2, 1986; amended in R86-
1 at 10 Ill. Reg. 14112, effective August 12, 1986; amended in R86-19 at 10 Ill. Reg. 20709,
effective December 2, 1986; amended in R86-46 at 11 Ill. Reg. 13555, effective August 4,
1987; amended in R87-5 at 11 Ill. Reg. 19392, effective November 12, 1987; amended in R87-
39 at 12 Ill. Reg. 13129, effective July 29, 1988; amended in R88-16 at 13 Ill. Reg. 452,
effective December 27, 1988; amended in R89-1 at 13 Ill. Reg. 18523, effective November 13,
1989; amended in R90-10 at 14 Ill. Reg. 16653, effective September 25, 1990; amended in
R90-11 at 15 Ill. Reg. 9644, effective June 17, 1991; amended in R91-1 at 15 Ill. Reg. 14562,
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. 17696, effective November 6, 1992; amended in R93-4 at 17
Ill. Reg. 20822, effective November 22, 1993; amended in R95-6 at 19 Ill. Reg. 9935,
effective June 27, 1995; amended in R95-20 at 20 Ill. Reg. 11236, effective August 1, 1996;
amended in R96-10/R97-3/R97-5 at 22 Ill. Reg. 603, effective December 16, 1997; amended in
R97-21/R98-3/R98-5 at 22 Ill. Reg. 17950, effective September 28, 1998; amended in R00-5 at
24 Ill. Reg. 1136, effective January 6, 2000; amended in R00-13 at 24 Ill. Reg. ________,
effective ______________________.
181
SUBPART C: PRE-TRANSPORT REQUIREMENTS
Section 722.134
Accumulation Time
a)
Except as provided in subsection (d), (e), or (f), (g), (h), or (i) of this Section, a
generator is exempt from all the requirements in 35 Ill. Adm. Code 725.Subparts
G and H, except for 35 Ill. Adm. Code 725.211 and 725.214, and may
accumulate hazardous waste on-site for 90 days or less without a permit or
without having interim status, provided that the following conditions are fulfilled:
1)
The waste is placed in or on one of the following:
A)
In containers, and the generator complies with 35 Ill. Adm. Code
725.Subparts I, AA, BB, and CC;
B)
In tanks, and the generator complies with 35 Ill. Adm. Code
725.Subparts J, AA, BB, and CC, except 35 Ill. Adm. Code
725.297(c) and 725.300;
C)
On drip pads, and the generator complies with 35 Ill. Adm. Code
725.Subpart W and maintains the following records at the facility:
i)
A description of the procedures that will be followed to
ensure that all wastes are removed from the drip pad and
associated collection system at least once every 90 days,
and
ii)
Documentation of each waste removal, including the
quantity of waste removed from the drip pad and the sump
or collection system and the date and time of removal; or
D)
In containment buildings, and the generator complies with 35 Ill.
Adm. Code 725.Subpart DD (has placed its Professional Engineer
(PE) certification that the building complies with the design
standards specified in 35 Ill. Adm. Code 725.1101 in the facility’s
operating record prior to the date of initial operation of the unit).
The owner or operator shall maintain the following records at the
facility:
i)
A written description of procedures to ensure that each
waste volume remains in the unit for no more than 90
days, a written description of the waste generation and
management practices for the facility showing that they are
consistent with respecting respect to the 90 day limit, and
documentation that the procedures are complied with; or
182
ii)
Documentation that the unit is emptied at least once every
90 days;
BOARD NOTE: The “in addition” hanging subsection that appears in
the Federal rules after 40 CFR 262.34(a)(1)(iv)(B) is in the introduction
to subsection (a) of this Section.
2)
The date upon which each period of accumulation begins is clearly
marked and visible for inspection on each container;
3)
While being accumulated on-site, each container and tank is labeled or
marked clearly with the words “Hazardous Waste”; and
4)
The generator complies with the requirements for treatment, storage, and
disposal facility owners or operators in 35 Ill. Adm. Code 725.Subparts
C and D and with 35 Ill. Adm. Code 725.116 and 728.107(a)(4)
728.107(a)(5).
b)
A generator that accumulates hazardous waste for more than 90 days is an
operator of a storage facility and is subject to the requirements of 35 Ill. Adm.
Code 724 and 725 and the permit requirements of 35 Ill. Adm. Code 702, 703
and 705 unless the generator has been granted an extension of the 90-day period.
If hazardous wastes must remain on-site for longer than 90 days due to
unforeseen, temporary, and uncontrollable circumstances, the generator may
seek an extension of up to 30 days by means of a variance or provisional
variance, pursuant to Section 37 of the Environmental Protection Act and 35 Ill.
Adm. Code 180 (Agency procedural regulations).
c)
Accumulation near the point of generation.
1)
A generator may accumulate as much as 55 gallons of hazardous waste
or one quart of acutely hazardous waste listed in 35 Ill. Adm. Code
721.133(e) in containers at or near any point of generation where wastes
initially accumulate that is under the control of the operator of the process
generating the waste without a permit or interim status and without
complying with subsection (a) of this Section, provided the generator
does the following:
A)
Complies with 35 Ill. Adm. Code 725.271, 725.272, and
725.273(a); and
B)
Marks the generator’s containers either with the words
“Hazardous Waste” or with other words that identify the contents
of the containers.
183
2)
A generator that accumulates either hazardous waste or acutely hazardous
waste listed in 35 Ill. Adm. Code 721.133(e) in excess of the amounts
listed in subsection (c)(1) of this Section at or near any point of
generation must, with respect to that amount of excess waste, comply
within three days with subsection (a) of this Section or other applicable
provisions of this Chapter. During the three day period the generator
must continue to comply with subsection (c)(1) of this Section. The
generator must mark the container holding the excess accumulation of
hazardous waste with the date the excess amount began accumulating.
d)
A generator that generates greater than 100 kilograms but less than 1000
kilograms of hazardous waste in a calendar month may accumulate hazardous
waste on-site for 180 days or less without a permit or without having interim
status provided that the following conditions are fulfilled:
1)
The quantity of waste accumulated on-site never exceeds 6000 kilograms;
2)
The generator complies with the requirements of 35 Ill. Adm. Code
725.Subpart I (except 35 Ill. Adm. Code 725.276 and 725.278);
3)
The generator complies with the requirements of 35 Ill. Adm. Code
725.301;
4)
The generator complies with the requirements of subsections (a)(2) and
(a)(3) of this Section, 35 Ill. Adm. Code 725.Subpart C, and 35 Ill.
Adm. Code 728.107(a)(5); and
5)
The generator complies with the following requirements:
A)
At all times there must be at least one employee either on the
premises or on call (i.e., available to respond to an emergency by
reaching the facility within a short period of time) with the
responsibility for coordinating all emergency response measures
specified in subsection (d)(5)(D) of this Section. The employee is
the emergency coordinator.
B)
The generator shall post the following information next to the
telephone:
i)
The name and telephone number of the emergency
coordinator;
ii)
Location of fire extinguishers and spill control material
and, if present, fire alarm; and
184
iii)
The telephone number of the fire department, unless the
facility has a direct alarm.
C)
The generator shall ensure that all employees are thoroughly
familiar with proper waste handling and emergency procedures,
relevant to their responsibilities during normal facility operations
and emergencies.
D)
The emergency coordinator or designee shall respond to any
emergencies that arise. The applicable responses are as follows:
i)
In the event of a fire, call the fire department or attempt to
extinguish it using a fire extinguisher;
ii)
In the event of a spill, contain the flow of hazardous waste
to the extent possible and, as soon as is practicable, clean
up the hazardous waste and any contaminated materials or
soil; and
iii)
In the event of a fire, explosion, or other release that could
threaten human health outside the facility, or when the
generator has knowledge that a spill has reached surface
water, the generator shall immediately notify the National
Response Center (using its 24-hour toll free number 800-
424-8802). The report must include the following
information: the name, address, and USEPA identification
number (Section 722.112 of this Part) of the generator; the
date, time, and type of incident (e.g., spill or fire); the
quantity and type of hazardous waste involved in the
incident; the extent of injuries, if any; and the estimated
quantity and disposition of recoverable materials, if any.
e)
A generator that generates greater than 100 kilograms but less than 1000
kilograms of hazardous waste in a calendar month and that must transport the
waste or offer the waste for transportation over a distance of 200 miles or more
for off-site treatment, storage, or disposal may accumulate hazardous waste on-
site for 270 days or less without a permit or without having interim status,
provided that the generator complies with the requirements of subsection (d) of
this Section.
f)
A generator that generates greater than 100 kilograms but less than 1000
kilograms of hazardous waste in a calendar month and that accumulates
hazardous waste in quantities exceeding 6000 kg or accumulates hazardous waste
for more than 180 days (or for more than 270 days if the generator must
185
transport the waste or offer the waste for transportation over a distance of 200
miles or more) is an operator of a storage facility and is subject to the
requirements of 35 Ill. Adm. Code 724 and 725 and the permit requirements of
35 Ill. Adm. Code 703, unless the generator has been granted an extension to the
180-day (or 270-day if applicable) period. If hazardous wastes must remain on-
site for longer than 180 days (or 270 days if applicable) due to unforeseen,
temporary, and uncontrollable circumstances, the generator may seek an
extension of up to 30 days by means of variance or provisional variance pursuant
to Section 37 of the Environmental Protection Act.
g) A generator that generates 1,000 kilograms or greater of hazardous waste per calendar
month which also generates wastewater treatment sludges from electroplating
operations that meet the listing description for the RCRA hazardous waste code F006,
may accumulate F006 waste on-site for more than 90 days, but not more than 180
days, without a permit or without having interim status provided that the generator fulfills
the following conditions:
1) The generator has implemented pollution prevention practices that reduce the
amount of any hazardous substances, pollutants, or contaminants entering F006
or otherwise released to the environment prior to its recycling;
2) The F006 waste is legitimately recycled through metals recovery;
3) No more than 20,000 kilograms of F006 waste is accumulated on-site at any
one time; and
4) The F006 waste is managed in accordance with the following conditions:
A) The F006 waste is placed in one of the following containing devices:
i) In containers and the generator complies with the applicable
requirements of 35 Ill. Adm. Code 725.Subparts I, AA, BB,
and CC;
ii) In tanks and the generator complies with the applicable
requirements of 35 Ill. Adm. Code 725.Subparts J, AA, BB,
and CC, except35 Ill. Adm. Code 725.297(c) and 725.300; or
iii) In containment buildings, and the generator complies with 35 Ill.
Adm. Code 725.Subpart DD and has placed its professional
engineer certification that the building complies with the design
standards specified in 35 Ill. Adm. Code 725.1101 in the
facility's operating record prior to operation of the unit. The
186
owner or operator shall maintain the records listed in subsection
(g)(4)(F) of this Section at the facility.
B) In addition, such a generator is exempt from all the requirements in 35
Ill. Adm. Code 725.Subparts G and H, except for 35 Ill. Adm. Code
725.211 and 725.214.
C) The date upon which each period of accumulation begins is clearly
marked and visible for inspection on each container;
D) While being accumulated on-site, each container and tank is labeled or
marked clearly with the words, “Hazardous Waste;” and
E) The generator complies with the requirements for owners or operators
in 35 Ill. Adm. Code 725.Subparts C and D, with 35 Ill. Adm. Code
725.116, and with 35 Ill. Adm. Code 728.107(a)(5).
F) Required records for a containment building:
i) A written description of procedures to ensure that the F006
waste remains in the unit for no more than 180 days, a written
description of the waste generation and management practices
for the facility showing that they are consistent with the 180-day
limit, and documentation that the generator is complying with the
procedures; or
ii) Documentation that the unit is emptied at least once every 180
days.
BOARD NOTE: The Board has codified 40 CFR
262.34(g)(4)(A)(iii)(
1
) and (g)(4)(A)(iii)(
2
) as subsections (g)(4)(F)(i)
and (g)(4)(F)(ii) because Illinois Administrative Code codification
requirments do not allow the use of a fifth level of subsection indents.
h) A generator that generates 1,000 kilograms or greater of hazardous waste per calendar
month which also generates wastewater treatment sludges from electroplating
operations that meet the listing description for the RCRA hazardous waste code F006
and which must transport this waste or offer this waste for transportation over a
distance of 200 miles or more for off-site metals recovery may accumulate F006 waste
on-site for more than 90 days, but not more than 270 days, without a permit or without
having interim status if the generator complies with the requirements of paragraphs
(g)(1) through (g)(4) of this Section.
187
i) A generator accumulating F006 in accordance with paragraphs (g) and (h) of this
Section that accumulates F006 waste on-site for more than 180 days (or for more than
270 days if the generator must transport this waste or offer this waste for transportation
over a distance of 200 miles or more), or which accumulates more than 20,000
kilograms of F006 waste on-site is an operator of a storage facility, and such a
generator is subject to the requirements of 35 Ill. Adm. Code 724 and 725 and the
permit requirements of 35 Ill. Adm. Code 702 and 703, unless the generator has been
granted an extension to the 180-day (or 270-day, if applicable) period or an exception
to the 20,000 kilogram accumulation limit.
1) On a case-by-case basis, the Board will grant a provisional variance that allows
an extension of the accumulation time up to an additional 30 days pursuant to
Section 37 of the Act on notification that the Agency has found that the F006
waste must remain on-site for longer than 180 days (or 270 days if applicable)
due to unforeseen, temporary, and uncontrollable circumstances.
2) On a case-by-case basis, the Boarrd will grant a provisional variance that
allows an exception to the 20,000 kilogram accumulation limit on notification
that the Agency has found that more than 20,000 kilograms of F006 waste must
remain on-site due to unforeseen, temporary, and uncontrollable circumstances.
3) A generator shall follow the procedure of 35 Ill. Adm. Code 180 (Agency
procedural rules) when seeking a provisional variance under subsection (i)(1) or
(i)(2) of this Section.
(Source: Amended at 24 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
188
SUBPART B: GENERAL FACILITY STANDARDS
Section
724.110
Applicability
724.111
Identification Number
724.112
Required Notices
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
189
SUBPART F: RELEASES FROM SOLID WASTE MANAGEMENT UNITS
Section
724.190
Applicability
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
190
SUBPART I: USE AND MANAGEMENT OF CONTAINERS
Section
724.270
Applicability
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
191
SUBPART L: WASTE PILES
Section
724.350
Applicability
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
192
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 FOR SOLID WASTE
MANAGEMENT UNITS
Section
724.652
Corrective Action Management Units
724.653
Temporary Units
724.654
Staging Piles
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
724.934
Test Methods and Procedures
724.935
Recordkeeping requirements
724.936
Reporting Requirements
193
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
724.1102
Closure and Post-closure Care
SUBPART EE: HAZARDOUS WASTE MUNITIONS AND EXPLOSIVES
STORAGE
Section
724.1200
Applicability
194
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.
________, effective ______________________.
SUBPART A: GENERAL PROVISIONS
Section 724.101
Purpose, Scope, and Applicability
a)
The purpose of this Part is to establish minimum standards that define the
acceptable management of hazardous waste.
195
b)
The standards in this Part apply to owners and operators of all facilities that treat,
store, or dispose of hazardous waste, except as specifically provided otherwise in
this Part or 35 Ill. Adm. Code 721.
c)
The requirements of this Part apply to a person disposing of hazardous waste by
means of ocean disposal subject to a permit issued under the Marine Protection,
Research and Sanctuaries Act (16 U.S.C. USC 1431-1434, 33 USC 1401) only
to the extent they are included in a RCRA permit by rule granted to such a
person under 35 Ill. Adm. Code 703.141. A “RCRA permit” is a permit
required by Section 21(f) of the Environmental Protection Act and 35 Ill. Adm.
Code 703.121.
BOARD NOTE: This Part does apply to the treatment or storage of hazardous
waste before it is loaded onto an ocean vessel for incineration or disposal at sea.
d)
The requirements of this Part apply to a person disposing of hazardous waste by
means of underground injection subject to a permit issued by the Agency
pursuant to Section 12(g) of the Environmental Protection Act only to the extent
they are required by 35 Ill. Adm. Code 704.Subpart F.
BOARD NOTE: This Part does apply to the above-ground treatment or storage
of hazardous waste before it is injected underground.
e)
The requirements of this Part apply to the owner or operator of a POTW
(publicly owned treatment works) that treats, stores, or disposes of hazardous
waste only to the extent included in a RCRA permit by rule granted to such a
person under 35 Ill. Adm. Code 703.141.
f)
This subsection corresponds with 40 CFR 264.1(f), which provides that the
federal regulations do not apply to T/S/D activities in authorized states, except
under limited, enumerated circumstances. This statement maintains structural
consistency with USEPA rules.
g)
The requirements of this Part do not apply to:
1)
The owner or operator of a facility permitted by the Agency under
Section 21 of the Environmental Protection Act to manage municipal or
industrial solid waste, if the only hazardous waste the facility treats,
stores, or disposes of is excluded from regulation under this Part by 35
Ill. Adm. Code 721.105.
BOARD NOTE: The owner or operator may be subject to 35 Ill. Adm.
Code 807 and may have to have a supplemental permit under 35 Ill.
Adm. Code 807.210.
196
2)
The owner or operator of a facility managing recyclable materials
described in 35 Ill. Adm. Code 721.106(a)(2) through (a)(4) (except to
the extent that requirements of this Part are referred to in 35 Ill. Adm.
Code 726.Subparts C, F, G, or H or 35 Ill. Adm. Code 739).
3)
A generator accumulating waste on-site in compliance with 35 Ill. Adm.
Code 722.134.
4)
A farmer disposing of waste pesticides from the farmer’s own use in
compliance with 35 Ill. Adm. Code 722.170.
5)
The owner or operator of a totally enclosed treatment facility, as defined
in 35 Ill. Adm. Code 720.110.
6)
The owner or operator of an elementary neutralization unit or a
wastewater treatment unit, as defined in 35 Ill. Adm. Code 720.110,
provided that if the owner or operator is diluting hazardous ignitable
(D001) wastes (other than the D001 High TOC Subcategory defined in
35 Ill. Adm. Code 728.Table T) or reactive (D003) waste to remove the
characteristic before land disposal, the owner or operator must comply
with the requirements set out in Section 724.117(b).
7)
This subsection corresponds with 40 CFR 264.1(g)(7), reserved by
USEPA. This statement maintains structural consistency with USEPA
rules.
8)
Immediate response:
A)
Except as provided in subsection (g)(8)(B) of this Section, a
person engaged in treatment or containment activities during
immediate response to any of the following situations:
i)
A discharge of a hazardous waste;
ii)
An imminent and substantial threat of a discharge of
hazardous waste;
iii)
A discharge of a material that becomes a hazardous waste
when discharged; or
iv)
An immediate threat to human health, public safety,
property, or the environment from the known or suspected
presence of military munitions, other explosive material, or
an explosive device, as determined by an explosives or
munitions emergency response specialist as defined in 35
197
Ill. Adm. Code 720.110.
B)
An owner or operator of a facility otherwise regulated by this Part
must comply with all applicable requirements of Subparts C and D
of this Part.
C)
Any person that is covered by subsection (g)(8)(A) of this Section
and that continues or initiates hazardous waste treatment or
containment activities after the immediate response is over is
subject to all applicable requirements of this Part and 35 Ill. Adm.
Code 702, 703, and 705 for those activities.
D)
In the case of an explosives or munitions emergency response, if a
federal, State, or local official acting within the scope of his or her
official responsibilities or an explosives or munitions emergency
response specialist determines that immediate removal of the
material or waste is necessary to protect human health or the
environment, that official or specialist may authorize the removal
of the material or waste by transporters that do not have USEPA
identification numbers and without the preparation of a manifest.
In the case of emergencies involving military munitions, the
responding military emergency response specialist’s organizational
unit shall retain records for three years identifying the dates of the
response, the responsible persons responding, the type and
description of material addressed, and its disposition.
9)
A transporter storing manifested shipments of hazardous waste in
containers meeting the requirements of 35 Ill. Adm. Code 722.130 at a
transfer facility for a period of ten days or less.
10)
The addition of absorbent materials to waste in a container (as defined in
35 Ill. Adm. Code 720) or the addition of waste to absorbent material in
a container, provided these actions occur at the time waste is first placed
in the container, and Sections 724.117(b), 724.271, and 724.272 are
complied with.
11)
A universal waste handler or universal waste transporter (as defined in 35
Ill. Adm. Code 720.110) that handles any of the wastes listed below is
subject to regulation under 35 Ill. Adm. Code 733 when handling the
following universal wastes:
A)
Batteries, as described in 35 Ill. Adm. Code 733.102;
B)
Pesticides, as described in 35 Ill. Adm. Code 733.103;
198
C)
Thermostats, as described in 35 Ill. Adm. Code 733.104; and
D)
Mercury-containing lampsLamps, as described in 35 Ill. Adm.
Code 733.107 733.105.
BOARD NOTE: Subsection (g)(11)(D) of this Section was added
pursuant to Section 22.23a of the Act [415 ILCS 5/22.23a] (see
P.A. 90-502, effective August 19, 1997).
h)
This Part applies to owners and operators of facilities that treat, store, or dispose
of hazardous wastes referred to in 35 Ill. Adm. Code 728.
i)
35 Ill. Adm. Code 726.505 identifies when the requirements of this Part apply to
the storage of military munitions classified as solid waste under 35 Ill. Adm.
Code 726.302. The treatment and disposal of hazardous waste military
munitions are subject to the applicable permitting, procedural, and technical
standards in 35 Ill. Adm. Code 702, 703, 705, 720 through 726, and 728.
j)
The requirements of Subparts B, C, and D of this Part and Section 724.201 do
not apply to remediation waste management sites. (However, some remediation
waste management sites may be a part of a facility that is subject to a traditional
RCRA permit because the facility is also treating, storing, or disposing of
hazardous wastes that are not remediation wastes. In these cases, Subparts B, C,
and D of this Part, and Section 724.201 do apply to the facility subject to the
traditional RCRA permit.) Instead of the requirements of Subparts B, C, and D
of this Part, owners or operators of remediation waste management sites shall
comply with the following requirements:
1)
The owner or operator shall obtain an EPA identification number by
applying to USEPA using USEPA Form 8700-12;
2)
The owner or operator shall obtain a detailed chemical and physical
analysis of a representative sample of the hazardous remediation wastes to
be managed at the site. At a minimum, the analysis must contain all of
the information that must be known to treat, store, or dispose of the waste
according to this Part and 35 Ill. Adm. Code 728, and the owner or
operator shall keep the analysis accurate and up to date;
3)
The owner or operator shall prevent people who are unaware of the
danger from entering the site, and the owner or operator shall minimize
the possibility for unauthorized people or livestock entering onto the
active portion of the remediation waste management site, unless the
owner or operator can demonstrate the following to the Agency:
A)
Physical contact with the waste, structures, or equipment within
199
the active portion of the remediation waste management site will
not injure people or livestock who that may enter the active
portion of the remediation waste management site; and
B)
Disturbance of the waste or equipment by people or livestock who
that enter onto the active portion of the remediation waste
management site will not cause a violation of the requirements of
this Part;
4)
The owner or operator shall inspect the remediation waste management
site for malfunctions, deterioration, operator errors, and discharges that
may be causing or may lead to a release of hazardous waste constituents
to the environment or a threat to human health. The owner or operator
shall conduct these inspections often enough to identify problems in time
to correct them before they harm human health or the environment, and
the owner or operator shall remedy the problem before it leads to a
human health or environmental hazard. Where a hazard is imminent or
has already occurred, the owner or operator shall immediately take
remedial action;
5)
The owner or operator shall provide personnel with classroom or on-the-
job training on how to perform their duties in a way that ensures the
remediation waste management site complies with the requirements of this
Part, and on how to respond effectively to emergencies;
6)
The owner or operator shall take precautions to prevent accidental
ignition or reaction of ignitable or reactive waste, and the owner or
operator shall prevent threats to human health and the environment from
ignitable, reactive, and incompatible waste;
7)
For remediation waste management sites subject to regulation under
Subparts I through O and Subpart X of this Part, the owner or operator
shall design, construct, operate, and maintain a unit within a 100-year
floodplain to prevent washout of any hazardous waste by a 100-year
flood, unless the owner or operator can meet the requirements of Section
724.118(b);
8)
The owner or operator shall not place any non-containerized or bulk
liquid hazardous waste in any salt dome formation, salt bed formation,
underground mine, or cave;
9)
The owner or operator shall develop and maintain a construction quality
assurance program for all surface impoundments, waste piles, and landfill
units that are required to comply with Sections 724.321(c) and (d),
724.351(c) and (d), and 724.401(c) and (d) at the remediation waste
200
management site, according to the requirements of Section 724.119;
10)
The owner or operator shall develop and maintain procedures to prevent
accidents and a contingency and emergency plan to control accidents that
occur. These procedures must address proper design, construction,
maintenance, and operation of remediation waste management units at the
site. The goal of the plan must be to minimize the possibility of, and the
hazards from, a fire, explosion, or any unplanned sudden or non-sudden
release of hazardous waste or hazardous waste constituents to air, soil, or
surface water that could threaten human health or the environment. The
plan must explain specifically how to treat, store, and dispose of the
hazardous remediation waste in question, and must be implemented
immediately whenever a fire, explosion, or release of hazardous waste or
hazardous waste constituents occurs that could threaten human health or
the environment;
11)
The owner or operator shall designate at least one employee, either on
the facility premises or on call (that is, available to respond to an
emergency by reaching the facility quickly), to coordinate all emergency
response measures. This emergency coordinator must be thoroughly
familiar with all aspects of the facility’s contingency plan, all operations
and activities at the facility, the location and characteristics of waste
handled, the location of all records within the facility, and the facility
layout. In addition, this person must have the authority to commit the
resources needed to carry out the contingency plan;
12)
The owner or operator shall develop, maintain, and implement a plan to
meet the requirements in subsections (j)(2) through (j)(6) and (j)(9)
through (j)(10) of this Section; and
13)
The owner or operator shall maintain records documenting compliance
with subsections (j)(1) through (j)(12) of this Section.
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
SUBPART O: INCINERATORS
Section 724.440
Applicability
a)
The regulations in this Subpart apply to owners and operators of facilities that
incinerate hazardous waste, except as Section 724.101 provides otherwise. The
following facility owners and operators are considered to incinerate hazardous
waste:
201
1)
Owners or operators of hazardous waste incinerators (as defined in 35 Ill.
Adm. Code 720.110); and
2)
Owners or operators who that burn hazardous waste in boilers or in
industrial furnaces in order to destroy the wastes.
b) Integration of the MACT standards.
1) Except as provided by subsection (b)(2) of this Section, the standards of
this Part no longer apply when an 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.
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:
Under [the approach adopted by USEPA as a] final rule, MACT
air emissions and related operating requirements are to be
included in title V permits; RCRA permits will continue to be
required for all other aspects of the combustion unit and the
facility that are governed by RCRA (e.g., corrective action,
general facility standards, other combustor-specific concerns such
as materials handling, risk-based emissions limits and operating
requirements, as appropriate, and other hazardous waste
management units).
64 Fed Reg. 52828, 52975 (Sept. 30,1999).
bc)
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
202
analysis 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 35 Ill. Adm. Code 721.Subpart D
solely because it is ignitable (Hazard Code I), corrosive (Hazard
Code C), or both; or
B)
Listed as a hazardous waste in 35 Ill. Adm. Code 721.Subpart D
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; or
C)
A hazardous waste solely because it possesses the characteristic of
ignitability, as determined by the test for characteristics of
hazardous wastes under 35 Ill. Adm. Code 721.Subpart C; 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 35 Ill. Adm. Code 721.Appendix H, which that
would reasonably be expected to be in the waste.
cd)
If the waste to be burned is one which that is described by paragraphs subsection
(b)(1)(A), (b)(1)(B), (b)(1)(C), or (b)(1)(D) and contains insignificant
concentrations of the hazardous constituents listed in 35 Ill. Adm. Code
721.Appendix H, then the Agency may, in establishing permit conditions,
exempt the applicant from all requirements of this Subpart, except Section
724.441 (Waste analysis 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.
de)
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
short-term and incinerator permits).
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
203
SUBPART X: MISCELLANEOUS UNITS
Section 724.701
Environmental Performance Standards
A miscellaneous unit must be located, designed, constructed, operated, maintained, and closed
in a manner that will ensure protection of human health and the environment. Permits for
miscellaneous units are to contain such terms and provisions as are necessary to protect human
health and the environment, including, but not limited to, as appropriate, design and operating
requirements, detection and monitoring requirements, and requirements for responses to
releases of hazardous waste or hazardous constituents from the unit. Permit terms and
provisions must include those requirements of 724.Subparts I through O and AA through CC
of this Part; and 35 Ill. Adm. Code 702, 703, and 730; and 40 CFR 63, Subpart EEE,
incorporated by reference in 35 Ill. Adm. Code 720.111, that are appropriate for the
miscellaneous unit being permitted. Protection of human health and the environment includes,
but is not limited to:
a)
Prevention of any releases that may have adverse effects on human health or the
environment due to migration of waste constituents in the groundwater or
subsurface environment, considering:
1)
The volume and physical and chemical characteristics of the waste in the
unit, including its potential for migration through soil, liners, or other
containing structures;
2)
The hydrologic and geologic characteristics of the unit and the
surrounding area;
3)
The existing quality of groundwater, including other sources of
contamination and their cumulative impact on the groundwater;
4)
The quantity and direction of groundwater flow;
5)
The proximity to and withdrawal rates of current and potential
groundwater users;
6)
The patterns of land use in the region;
7)
The potential for deposition or migration of waste constituents into
subsurface physical structures and the root zone of food-chain crops and
other vegetation;
8)
The potential for health risks caused by human exposure to waste
constituents; and
9)
The potential for damage to domestic animals, wildlife, crops, vegetation,
204
and physical structures caused by exposure to waste constituents.
b)
Prevention of any releases that may have adverse effects on human health or the
environment due to migration of waste constituents in surface water, in wetlands,
or on the soil surface, considering:
1)
The volume and physical and chemical characteristics of the waste in the
unit;
2)
The effectiveness and reliability of containing, confining, and collecting
systems and structures in preventing migration;
3)
The hydrologic characteristics of the unit and surrounding area, including
the topography of the land around the unit;
4)
The patterns of precipitation in the region;
5)
The quantity, quality, and direction of groundwater flow;
6)
The proximity of the unit to surface waters;
7)
The current and potential uses of the nearby surface waters and any
water quality standards in 35 Ill. Adm. Code 302 or 303;
8)
The existing quality of surface waters and surface soils, including other
sources of contamination and their cumulative impact on surface waters
and surface soils;
9)
The patterns of land use in the region;
10)
The potential for health risks caused by human exposure to waste
constituents; and
11)
The potential for damage to domestic animals, wildlife, crops, vegetation,
and physical structures casued caused by exposure to waste constituents.
c)
Prevention of any release that may have adverse effects on human health or the
environment due to migration of waste constituents in the air, considering:
1)
The volume and physical and chemical characteristics of the waste in the
unit, including its potential for the emission and dispersal of gases,
aerosols, and particulates;
2)
The effectiveness and reliability of systems and structures to reduce or
prevent emissions of hazardous constituents to the air;
205
3)
The operating characteristics of the unit;
4)
The atmospheric, meteorologic, and topographic characteristics of the unit
and the surrounding area;
5)
The existing quality of the air, including other sources of contamination
and their cumulative impact on the air;
6)
The potential for health risks caused by human exposure to waste
constituents; and
7)
The potential for damage to domestic animals, wildlife, crops, vegetation,
and physical structures caused by waste constituents.
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
SUBPART CC: AIR EMISSION STANDARDS FOR TANKS, SURFACE
IMPOUNDMENTS, AND CONTAINERS
Section 724.983
Waste Determination Procedures
a)
Waste determination procedure for average volatile organic (VO) concentration
of a hazardous waste at the point of waste origination.
1)
An owner or operator shall determine the average VO concentration at
the point of waste origination for each hazardous waste placed in a waste
management unit exempted under the provisions of Section 724.982(c)(1)
from using air emission controls in accordance with standards specified in
Section 724.984 through Section 724.987, as applicable to the waste
management unit.
A)
An owner or operator shall make an initial determination of the
average VO concentration of the waste stream before the first time
any portion of the material in the hazardous waste stream is placed
in a waste management unit exempted under the provisions of
Section 724.982(c)(1) from using air emission controls.
Thereafter, an owner or operator shall make an initial
determination of the average VO concentration of the waste
stream for each averaging period that a hazardous waste is
managed in the unit.
B)
An owner or operator shall perform a new waste determination
whenever changes to the source generating the waste stream are
206
reasonably likely to cause the average VO concentration of the
hazardous waste to increase to a level that is equal to or greater
than the applicable VO concentration limits specified in Section
724.982.
2)
For a waste determination that is required by subsection (a)(1) of this
Section, the average VO concentration of a hazardous waste at the point
of waste origination must be determined in accordance with the
procedures specified in 35 Ill. Adm. Code 725.984(a)(2) through (a)(4).
b)
Waste determination procedures for treated hazardous waste.
1)
An owner or operator shall perform the applicable waste determination
for each treated hazardous waste placed in a waste management unit
exempted under the provisions of Section 724.982(c)(2)(A) through
(c)(2)(F) from using air emission controls in accordance with standards
specified in Sections 724.984 through 724.987, as applicable to the waste
management unit.
A)
An owner or operator shall make an initial determination of the
average VO concentration of the waste stream before the first time
any portion of the material in the treated waste stream is placed in
the exempt waste management unit. Thereafter, an owner or
operator shall update the information used for the waste
determination at least once every 12 months following the date of
the initial waste determination.
B)
An owner or operator shall perform a new waste determination
whenever changes to the process generating or treating the waste
stream are reasonably likely to cause the average VO
concentration of the hazardous waste to increase to such a level
that the applicable treatment conditions specified in Section
724.982(c)(2) are not achieved.
2)
The waste determination for a treated hazardous waste must be performed
in accordance with the procedures specified in 35 Ill. Adm. Code
725.984(b)(2) through (b)(9), as applicable to the treated hazardous
waste.
c)
Procedure to determine the maximum organic vapor pressure of a hazardous
waste in a tank.
1)
An owner or operator shall determine the maximum organic vapor
pressure for each hazardous waste placed in a tank using Tank Level 1
controls in accordance with standards specified in Section 724.984(c).
207
2)
The maximum organic vapor pressure of the hazardous waste may be
determined in accordance with the procedures specified in 35 Ill. Adm.
Code 725.984(c)(2) through (c)(4).
d)
The procedure for determining no detectable organic emissions for the purpose
of complying with this Subpart must be conducted in accordance with the
procedures specified in 35 Ill. Adm. Code 725.984(d).
(Source: Amended at 24 Ill. Reg. 1146, effective January 6, 2000)
TITLE 35: ENVIRONMENTAL PROTECTION
SUBTITLE G: WASTE DISPOSAL
CHAPTER I: POLLUTION CONTROL BOARD
SUBCHAPTER c: HAZARDOUS WASTE OPERATING REQUIREMENTS
PART 725
INTERIM STATUS STANDARDS FOR OWNERS AND OPERATORS OF
HAZARDOUS WASTE TREATMENT, STORAGE, AND DISPOSAL
FACILITIES
SUBPART A: GENERAL PROVISIONS
Section
725.101
Purpose, Scope, and Applicability
725.104
Imminent Hazard Action
SUBPART B: GENERAL FACILITY STANDARDS
Section
725.110
Applicability
725.111
USEPA Identification Number
725.112
Required Notices
725.113
General Waste Analysis
725.114
Security
725.115
General Inspection Requirements
725.116
Personnel Training
725.117
General Requirements for Ignitable, Reactive, or Incompatible Wastes
725.118
Location Standards
725.119
Construction Quality Assurance Program
SUBPART C: PREPAREDNESS AND PREVENTION
Section
725.130
Applicability
725.131
Maintenance and Operation of Facility
725.132
Required Equipment
208
725.133
Testing and Maintenance of Equipment
725.134
Access to Communications or Alarm System
725.135
Required Aisle Space
725.137
Arrangements with Local Authorities
SUBPART D: CONTINGENCY PLAN AND EMERGENCY
PROCEDURES
Section
725.150
Applicability
725.151
Purpose and Implementation of Contingency Plan
725.152
Content of Contingency Plan
725.153
Copies of Contingency Plan
725.154
Amendment of Contingency Plan
725.155
Emergency Coordinator
725.156
Emergency Procedures
SUBPART E: MANIFEST SYSTEM, RECORDKEEPING AND
REPORTING
Section
725.170
Applicability
725.171
Use of Manifest System
725.172
Manifest Discrepancies
725.173
Operating Record
725.174
Availability, Retention and Disposition of Records
725.175
Annual Report
725.176
Unmanifested Waste Report
725.177
Additional Reports
SUBPART F: GROUNDWATER MONITORING
Section
725.190
Applicability
725.191
Groundwater Monitoring System
725.192
Sampling and Analysis
725.193
Preparation, Evaluation and Response
725.194
Recordkeeping and Reporting
SUBPART G: CLOSURE AND POST-CLOSURE CARE
Section
725.210
Applicability
725.211
Closure Performance Standard
725.212
Closure Plan; Amendment of Plan
725.213
Closure; Time Allowed for Closure
725.214
Disposal or Decontamination of Equipment, Structures and Soils
725.215
Certification of Closure
725.216
Survey Plat
209
725.217
Post-closure Care and Use of Property
725.218
Post-Closure Care Plan; Amendment of Plan
725.219
Post-Closure Notices
725.220
Certification of Completion of Post-Closure Care
725.221
Alternative Post-Closure Care Requirements
SUBPART H: FINANCIAL REQUIREMENTS
Section
725.240
Applicability
725.241
Definitions of Terms as Used in this Subpart
725.242
Cost Estimate for Closure
725.243
Financial Assurance for Closure
725.244
Cost Estimate for Post-closure Care
725.245
Financial Assurance for Post-closure Monitoring and Maintenance
725.246
Use of a Mechanism for Financial Assurance of Both Closure and Post-closure
Care
725.247
Liability Requirements
725.248
Incapacity of Owners or Operators, Guarantors or Financial Institutions
725.251
Promulgation of Forms (Repealed)
SUBPART I: USE AND MANAGEMENT OF CONTAINERS
Section
725.270
Applicability
725.271
Condition of Containers
725.272
Compatibility of Waste with Container
725.273
Management of Containers
725.274
Inspections
725.276
Special Requirements for Ignitable or Reactive Waste
725.277
Special Requirements for Incompatible Wastes
725.278
Air Emission Standards
SUBPART J: TANK SYSTEMS
Section
725.290
Applicability
725.291
Assessment of Existing Tank System’s Integrity
725.292
Design and Installation of New Tank Systems or Components
725.293
Containment and Detection of Releases
725.294
General Operating Requirements
725.295
Inspections
725.296
Response to leaks or spills and disposition of Tank Systems
725.297
Closure and Post-Closure Care
725.298
Special Requirements for Ignitable or Reactive Waste
725.299
Special Requirements for Incompatible Wastes
725.300
Waste Analysis and Trial Tests
725.301
Generators of 100 to 1000 Kilograms of Hazardous Waste Per Month
210
725.302
Air Emission Standards
SUBPART K: SURFACE IMPOUNDMENTS
Section
725.320
Applicability
725.321
Design and Operating Requirements
725.322
Action Leakage Rate
725.323
Response Actions
725.324
Containment System
725.325
Waste Analysis and Trial Tests
725.326
Monitoring and Inspections
725.328
Closure and Post-closure Care
725.329
Special Requirements for Ignitable or Reactive Waste
725.330
Special Requirements for Incompatible Wastes
725.331
Air Emission Standards
SUBPART L: WASTE PILES
Section
725.350
Applicability
725.351
Protection from Wind
725.352
Waste Analysis
725.353
Containment
725.354
Design and Operating Requirements
725.355
Action Leakage Rates
725.356
Special Requirements for Ignitable or Reactive Waste
725.357
Special Requirements for Incompatible Wastes
725.358
Closure and Post-closure Care
725.359
Response Actions
725.360
Monitoring and Inspection
SUBPART M: LAND TREATMENT
Section
725.370
Applicability
725.372
General Operating Requirements
725.373
Waste Analysis
725.376
Food Chain Crops
725.378
Unsaturated Zone (Zone of Aeration) Monitoring
725.379
Recordkeeping
725.380
Closure and Post-closure
725.381
Special Requirements for Ignitable or Reactive Waste
725.382
Special Requirements for Incompatible Wastes
SUBPART N: LANDFILLS
Section
725.400
Applicability
211
725.401
Design Requirements
725.402
Action Leakage Rate
725.403
Response Actions
725.404
Monitoring and Inspection
725.409
Surveying and Recordkeeping
725.410
Closure and Post-closure
725.412
Special Requirements for Ignitable or Reactive Waste
725.413
Special Requirements for Incompatible Wastes
725.414
Special Requirements for Liquid Wastes
725.415
Special Requirements for Containers
725.416
Disposal of Small Containers of Hazardous Waste in Overpacked Drums (Lab
Packs)
SUBPART O: INCINERATORS
Section
725.440
Applicability
725.441
Waste Analysis
725.445
General Operating Requirements
725.447
Monitoring and Inspection
725.451
Closure
725.452
Interim Status Incinerators Burning Particular Hazardous Wastes
SUBPART P: THERMAL TREATMENT
Section
725.470
Other Thermal Treatment
725.473
General Operating Requirements
725.475
Waste Analysis
725.477
Monitoring and Inspections
725.481
Closure
725.482
Open Burning; Waste Explosives
725.483
Interim Status Thermal Treatment Devices Burning Particular Hazardous Waste
SUBPART Q: CHEMICAL, PHYSICAL AND BIOLOGICAL
TREATMENT
Section
725.500
Applicability
725.501
General Operating Requirements
725.502
Waste Analysis and Trial Tests
725.503
Inspections
725.504
Closure
725.505
Special Requirements for Ignitable or Reactive Waste
725.506
Special Requirements for Incompatible Wastes
212
SUBPART R: UNDERGROUND INJECTION
Section
725.530
Applicability
SUBPART W: DRIP PADS
Section
725.540
Applicability
725.541
Assessment of existing drip pad integrity
725.542
Design and installation of new drip pads
725.543
Design and operating requirements
725.544
Inspections
725.545
Closure
SUBPART AA: AIR EMISSION STANDARDS FOR PROCESS VENTS
Section
725.930
Applicability
725.931
Definitions
725.932
Standards: Process Vents
725.933
Standards: Closed-Vent Systems and Control Devices
725.934
Test methods and procedures
725.935
Recordkeeping Requirements
SUBPART BB: AIR EMISSION STANDARDS FOR EQUIPMENT LEAKS
Section
725.950
Applicability
725.951
Definitions
725.952
Standards: Pumps in Light Liquid Service
725.953
Standards: Compressors
725.954
Standards: Pressure Relief Devices in Gas/Vapor Service
725.955
Standards: Sampling Connecting Systems
725.956
Standards: Open-ended Valves or Lines
725.957
Standards: Valves in Gas/Vapor or Light Liquid Service
725.958
Standards: Pumps, Valves, Pressure Relief Devices, Flanges and other
Connectors
725.959
Standards: Delay of Repair
725.960
Standards: Closed-vent Systems and Control Devices
725.961
Percent Leakage Alternative for Valves
725.962
Skip Period Alternative for Valves
725.963
Test Methods and Procedures
725.964
Recordkeeping Requirements
SUBPART CC: AIR EMISSION STANDARDS FOR TANKS, SURFACE
IMPOUNDMENTS, AND CONTAINERS
Section
725.980
Applicability
213
725.981
Definitions
725.982
Schedule for Implementation of Air Emission Standards
725.983
Standards: General
725.984
Waste Determination Procedures
725.985
Standards: Tanks
725.986
Standards: Surface Impoundments
725.987
Standards: Containers
725.988
Standards: Closed-Vent Systems and Control Devices
725.989
Inspection and Monitoring Requirements
725.990
Recordkeeping Requirements
725.991
Alternative Tank Emission Control Requirements (Repealed)
SUBPART DD: CONTAINMENT BUILDINGS
Section
725.1100
Applicability
725.1101
Design and operating standards
725.1102
Closure and Post Closure-Care
SUBPART EE: HAZARDOUS WASTE MUNITIONS AND EXPLOSIVES
STORAGE
Section
725.1200
Applicability
725.1201
Design and Operating Standards
725.1202
Closure and Post-Closure Care
725.Appendix A
Recordkeeping Instructions
725.Appendix B
EPA Report Form and Instructions (Repealed)
725.Appendix C
EPA Interim Primary Drinking Water Standards
725.Appendix D
Tests for Significance
725.Appendix E
Examples of Potentially Incompatible Waste
725.Appendix F
Compounds With Henry’s Law Constant Less Than 0.1 Y/X (at 25°C)
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. 14034, effective
October 12, 1983; amended in R84-9 at 9 Ill. Reg. 11869, effective July 24, 1985; amended in
R85-22 at 10 Ill. Reg. 1085, effective January 2, 1986; amended in R86-1 at 10 Ill. Reg.
14069, effective August 12, 1986; amended in R86-28 at 11 Ill. Reg. 6044, effective March
24, 1987; amended in R86-46 at 11 Ill. Reg. 13489, effective August 4, 1987; amended in
R87-5 at 11 Ill. Reg. 19338, effective November 10, 1987; amended in R87-26 at 12 Ill. Reg.
2485, effective January 15, 1988; amended in R87-39 at 12 Ill. Reg. 13027, effective July 29,
1988; amended in R88-16 at 13 Ill. Reg. 437, effective December 28, 1988; amended in R89-1
214
at 13 Ill. Reg. 18354, effective November 13, 1989; amended in R90-2 at 14 Ill. Reg. 14447,
effective August 22, 1990; amended in R90-10 at 14 Ill. Reg. 16498, effective September 25,
1990; amended in R90-11 at 15 Ill. Reg. 9398, effective June 17, 1991; amended in R91-1 at
15 Ill. Reg. 14534, effective October 1, 1991; amended in R91-13 at 16 Ill. Reg. 9578,
effective June 9, 1992; amended in R92-1 at 16 Ill. Reg. 17672, effective November 6, 1992;
amended in R92-10 at 17 Ill. Reg. 5681, effective March 26, 1993; amended in R93-4 at 17 Ill.
Reg. 20620, effective November 22, 1993; amended in R93-16 at 18 Ill. Reg. 6771, effective
April 26, 1994; amended in R94-7 at 18 Ill. Reg. 12190, effective July 29, 1994; amended in
R94-17 at 18 Ill. Reg. 17548, effective November 23, 1994; amended in R95-6 at 19 Ill. Reg.
9566, effective June 27, 1995; amended in R95-20 at 20 Ill. Reg. 11078, effective August 1,
1996; amended in R96-10/R97-3/R97-5 at 22 Ill. Reg. 369, effective December 16, 1997;
amended in R98-12 at 22 Ill. Reg. 7620, effective April 15, 1998; amended in R97-21/R98-
3/R98-5 at 22 Ill. Reg. 17620, effective September 28, 1998; amended in R98-21/R99-2/R99-7
at 23 Ill. Reg. 1850, effective January 19, 1999; amended in R99-15 at 23 Ill. Reg. 9168,
effective July 26, 1999; amended in R00-5 at 24 Ill. Reg. 1076, effective January 6, 2000;
amended in R00-13 at 24 Ill. Reg. ________, effective ______________________.
SUBPART A: GENERAL PROVISIONS
Section 725.101
Purpose, Scope
,
and Applicability
a)
The purpose of this Part is to establish minimum standards that define the
acceptable management of hazardous waste during the period of interim status
and until certification of final closure or, if the facility is subject to post-closure
care requirements, until post-closure care responsibilities are fulfilled.
b)
Except as provided in Section 725.980(b), the standards in this Part and 35 Ill.
Adm. Code 724.652 through 724.654 apply to owners and operators of facilities
that treat, store, or dispose of hazardous waste that have fully complied with the
requirements for interim status under Section 3005(e) of the Resource
Conservation and Recovery Act (RCRA) (42 USC 6901 et seq.) and 35 Ill.
Adm. Code 703, until either a permit is issued under Section 3005 of the
Resource Conservation and Recovery Act or Section 21(f) of the Environmental
Protection Act, or until applicable closure and post-closure care responsibilities
under this Part are fulfilled, and to those owners and operators of facilities in
existence on November 19, 1980, that have failed to provide timely notification
as required by Section 3010(a) of RCRA or that have failed to file Part A of the
Permit Application, as required by 40 CFR 270.10(e) and (g) or 35 Ill. Adm.
Code 703.150 and 703.152. These standards apply to all treatment, storage, or
disposal of hazardous waste at these facilities after November 19, 1980, except
as specifically provided otherwise in this Part or 35 Ill. Adm. Code 721.
BOARD NOTE: As stated in Section 3005(a) of RCRA, after the effective date
of regulations under that Section (i.e., 40 CFR 270 and 124) the treatment,
215
storage, or disposal of hazardous waste is prohibited except in accordance with a
permit. Section 3005(e) of RCRA provides for the continued operation of an
existing facility that meets certain conditions until final administrative disposition
of the owner’s and operator’s permit application is made. 35 Ill. Adm. Code
703.140 et seq. provide that a permit is deemed issued under Section 21(f)(1) of
the Environmental Protection Act under conditions similar to federal interim
status.
c)
The requirements of this Part do not apply to:
1)
A person disposing of hazardous waste by means of ocean disposal
subject to a permit issued under the Marine Protection, Research and
Sanctuaries Act (16 USC 1431-1434; 33 USC 1401);
BOARD NOTE: This Part applies to the treatment or storage of
hazardous waste before it is loaded into an ocean vessel for incineration
or disposal at sea, as provided in subsection (b) of this Section.
2)
This subsection corresponds with 40 CFR 265.1(c)(2), marked
“reserved” by USEPA. This statement maintains structural consistency
with USEPA rules;
3)
The owner or operator of a POTW (publicly owned treatment works)
that treats, stores, or disposes of hazardous waste;
BOARD NOTE: The owner or operator of a facility under subsections
(c)(1) and (c)(3) is subject to the requirements of 35 Ill. Adm. Code 724
to the extent they are included in a permit by rule granted to such a
person under 35 Ill. Adm. Code 702 and 703 or are required by 35 Ill.
Adm. Code 704.Subpart F.
4)
This subsection corresponds with 40 CFR 265.1(c)(4), which pertains
exclusively to the applicability of the federal regulations in authorized
states. There is no need for a parallel provision in the Illinois
regulations. This statement maintains structural consistency with USEPA
rules;
5)
The owner or operator of a facility permitted, licensed, or registered by
Illinois to manage municipal or industrial solid waste, if the only
hazardous waste the facility treats, stores, or disposes of is excluded from
regulation under this Part by 35 Ill. Adm. Code 721.105;
6)
The owner or operator of a facility managing recyclable materials
described in 35 Ill. Adm. Code 721.106(a)(2) through (a)(4), except to
the extent that requirements of this Part are referred to in 35 Ill. Adm.
216
Code 726.Subparts C, F, G, or H or 35 Ill. Adm. Code 739;
7)
A generator accumulating waste on-site in compliance with 35 Ill. Adm.
Code 722.134, except to the extent the requirements are included in 35
Ill. Adm. Code 722.134;
8)
A farmer disposing of waste pesticides from the farmer’s own use in
compliance with 35 Ill. Adm. Code 722.170;
9)
The owner or operator of a totally enclosed treatment facility, as defined
in 35 Ill. Adm. Code 720.110;
10)
The owner or operator of an elementary neutralization unit or a
wastewater treatment unit as defined in 35 Ill. Adm. Code 720.110,
provided that if the owner or operator is diluting hazardous ignitable
(D001) wastes (other than the D001 High TOC Subcategory defined in
35 Ill. Adm. Code 728.Table T) or reactive (D003) waste in order to
remove the characteristic before land disposal, the owner or operator
shall comply with the requirements set out in Section 725.117(b);
11)
Immediate response:
A)
Except as provided in subsection (c)(11)(B) of this Section, a
person engaged in treatment or containment activities during
immediate response to any of the following situations:
i)
A discharge of a hazardous waste;
ii)
An imminent and substantial threat of a discharge of a
hazardous waste;
iii)
A discharge of a material that becomes a hazardous waste
when discharged; or
iv)
An immediate threat to human health, public safety,
property, or the environment from the known or suspected
presence of military munitions, other explosive material, or
an explosive device, as determined by an explosives or
munitions emergency response specialist as defined in 35
Ill. Adm. Code 720.110.
B)
An owner or operator of a facility otherwise regulated by this Part
shall comply with all applicable requirements of 725.Subparts C
and D of this Part.
217
C)
Any person that is covered by subsection (c)(11)(A) of this
Section that continues or initiates hazardous waste treatment or
containment activities after the immediate response is over is
subject to all applicable requirements of this Part and 35 Ill. Adm.
Code 702, 703, and 705 for those activities;
D)
In the case of an explosives or munitions emergency response, if a
federal, state, or local official acting within the scope of his or her
official responsibilities or an explosives or munitions emergency
response specialist determines that immediate removal of the
material or waste is necessary to protect human health or the
environment, that official or specialist may authorize the removal
of the material or waste by transporters that do not have USEPA
identification numbers and without the preparation of a manifest.
In the case of emergencies involving military munitions, the
responding military emergency response specialist’s organizational
unit shall retain records for three years identifying the dates of the
response, the responsible persons responding, the type and
description of material addressed, and its disposition;
12)
A transporter storing manifested shipments of hazardous waste in
containers meeting the requirements of 35 Ill. Adm. Code 722.130 at a
transfer facility for a period of ten days or less;
13)
The addition of absorbent material to waste in a container (as defined in
35 Ill. Adm. Code 720.110) or the addition of waste to the absorbent
material in a container, provided that these actions occur at the time that
the waste is first placed in the containers and Sections 725.117(b),
725.271, and 725.272 are complied with;
14)
A universal waste handler or universal waste transporter (as defined in 35
Ill. Adm. Code 720.110) that handles any of the wastes listed below is
subject to regulation under 35 Ill. Adm. Code 733 when handling the
following universal wastes:
A)
Batteries, as described in 35 Ill. Adm. Code 733.102;
B)
Pesticides, as described in 35 Ill. Adm. Code 733.103;
C)
Thermostats, as described in 35 Ill. Adm. Code 733.104 and; and
D)
Mercury-containing lampsLamps, as described in 35 Ill. Adm.
Code 733.107 733.105.
BOARD NOTE: Subsection (c)(14)(D) of this Section was added
218
pursuant to Section 22.23a of the Act [415 ILCS 5/22.23a] (see
P.A. 90-502, effective August 19, 1997).
d)
The following hazardous wastes must not be managed at facilities subject to
regulation under this Part: hazardous waste numbers F020, F021, F022, F023,
F026, or F027 unless:
1)
The wastewater treatment sludge is generated in a surface impoundment
as part of the plant’s wastewater treatment system;
2)
The waste is stored in tanks or containers;
3)
The waste is stored or treated in waste piles that meet the requirements of
35 Ill. Adm. Code 724.350(c) and all other applicable requirements of
725.Subpart L of this Part;
4)
The waste is burned in incinerators that are certified pursuant to the
standards and procedures in Section 725.452; or
5)
The waste is burned in facilities that thermally treat the waste in a device
other than an incinerator and that are certified pursuant to the standards
and procedures in Section 725.483.
e)
This Part applies to owners and operators of facilities that treat, store, or dispose
of hazardous wastes referred to in 35 Ill. Adm. Code 728, and the 35 Ill. Adm.
Code 728 standards are considered material conditions or requirements of the
interim status standards of this Part.
f)
35 Ill. Adm. Code 726.505 identifies when the requirements of this Part apply to
the storage of military munitions classified as solid waste under 35 Ill. Adm.
Code 726.302. The treatment and disposal of hazardous waste military
munitions are subject to the applicable permitting, procedural, and technical
standards in 35 Ill. Adm. Code 702, 703, 705, 720 through 726, and 728.
g)
Other bodies of regulations may apply to a person, facility, or activity, such as
35 Ill. Adm. Code 809 (special waste hauling), 35 Ill. Adm. Code 807 or 810
through 817 (solid waste landfills), 35 Ill. Adm. Code 848 or 849 (used and
scrap tires), or 35 Ill. Adm. Code 1420 through 1422 (potentially infectious
medical waste), depending on the provisions of those other regulations.
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
219
SUBPART O: INCINERATORS
Section 725.440
Applicability
a)
The regulations in this Subpart apply to owners or operators of hazardous waste
incinerators (as defined in 35 Ill. Adm. Code 720.110), except as 35 Ill. Adm.
Code 724.101 provides otherwise.
b) Integration of the MACT standards.
1) Except as provided by subsection (b)(2) of this Section, the standards of
this Part no longer apply when an 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.
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.
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.
bc)
Owners and operators of incinerators burning hazardous waste are exempt from
all of the requirements of this Subpart, except Section 725.451 (Closure),
provided that the owner or operator has documented, in writing, that the waste
would not reasonably be expected to contain any of the hazardous constituents
listed in 35 Ill. Adm. Code 721.Appendix H and such documentation is retained
at the facility, if the waste to be burned is:
1)
Listed as a hazardous waste in 35 Ill. Adm. Code 721.Subpart D, solely
because it is ignitable (Hazard Code I), corrosive (Hazard Code C), or
both; or
2)
Listed as a hazardous waste in 35 Ill. Adm. Code 721.Subpart D, solely
because it is reactive (Hazard Code R) for characteristics other than those
listed in 35 Ill. Adm. Code 721.123(a)(4) and (5), and will not be burned
when other hazardous wastes are present in the combustion zone; or
3)
A hazardous waste solely because it possesses the characteristic of
220
ignitability, corrosivity, or both, as determined by the tests for
characteristics of hazardous wastes under 35 Ill. Adm. Code 721.Subpart
C; or
4)
A hazardous waste solely because it possesses the reactivity
characteristics described by 35 Ill. Adm. Code 721.123 (a)(1), (2), (3),
(6), (7) or (8) and will not be burned when other hazardous wastes are
present in the combustion zone.
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
SUBPART CC: AIR EMISSION STANDARDS FOR TANKS, SURFACE
IMPOUNDMENTS, AND CONTAINERS
Section 725.980
Applicability
a)
The requirements of this Subpart apply to owners and operators of all facilities
that treat, store, or dispose of hazardous waste in tanks, surface impoundments,
or containers that are subject to Subpart I, J, or K of this Part, except as Section
725.101 and subsection (b) of this Section provide otherwise.
b)
The requirements of this Subpart do not apply to the following waste
management units at the facility:
1)
A waste management unit that holds hazardous waste placed in the unit
before December 6, 1996, and in which no hazardous waste is added to
the unit on or after December 6, 1996.
2)
A container that has a design capacity less than or equal to 0.1 m
3
(3.5 ft
3
or 26.4 gal).
3)
A tank in which an owner or operator has stopped adding hazardous
waste and the owner or operator has begun implementing or completed
closure pursuant to an approved closure plan.
4)
A surface impoundment in which an owner or operator has stopped
adding hazardous waste (except to implement an approved closure plan)
and the owner or operator has begun implementing or completed closure
pursuant to an approved closure plan.
5)
A waste management unit that is used solely for on-site treatment or
storage of hazardous waste that is placed in the unit as a result of
implementing remedial activities required pursuant to the Act or Board
regulations or under the corrective action authorities of RCRA sections
221
3004(u), 3004(v) or 3008(h); CERCLA authorities; or similar federal or
state State authorities.
6)
A waste management unit that is used solely for the management of
radioactive mixed waste in accordance with all applicable regulations
under the authority of the Atomic Energy Act (42 USC 2011 et seq.) and
the Nuclear Waste Policy Act of 1982 (42 USC 10101 et seq.).
7)
A hazardous waste management unit that the owner or operator certifies
is equipped with and operating air emission controls in accordance with
the requirements of an applicable federal Clean Air Act regulation
codified under 40 CFR 60, 61, or 63. For the purpose of complying
with this subsection (b)(7), a tank for which the air emission control
includes an enclosure, as opposed to a cover, must be in compliance with
the enclosure and control device requirements of Section 725.985(i),
except as provided in Section 725.983(c)(5).
8)
A tank that has a process vent, as defined in 35 Ill. Adm. Code 725.931.
c)
For the owner and operator of a facility subject to this Subpart that has received
a final RCRA permit prior to December 6, 1996, the following requirements
apply:
1)
The requirements of 35 Ill. Adm. Code 724.Subpart CC must be
incorporated into the permit when the permit is reissued, renewed, or
modified in accordance with the requirements of 35 Ill. Adm. Code 703
and 705.
2)
Until the date when the permit is reissued, renewed, or modified in
accordance with the requirements of 35 Ill. Adm. Code 703 and 705, the
owner and operator is subject to the requirements of this Subpart.
d)
The requirements of this Subpart, except for the recordkeeping requirements
specified in Section 725.990(i), are stayed for a tank or container used for the
management of hazardous waste generated by organic peroxide manufacturing
and its associated laboratory operations, when the owner or operator of the unit
meets all of the following conditions:
1)
The owner or operator identifies that the tank or container receives
hazardous waste generated by an organic peroxide manufacturing process
producing more than one functional family of organic peroxides or
multiple organic peroxides within one functional family, that one or more
of these organic peroxides could potentially undergo self-accelerating
thermal decomposition at or below ambient temperatures, and that organic
peroxides are the predominant products manufactured by the process.
222
For the purposes of this subsection, “organic peroxide” means an organic
compound that contains the bivalent -O-O- structure and which may be
considered to be a structural derivative of hydrogen peroxide where one
or both of the hydrogen atoms has been replaced by an organic radical.
2)
The owner or operator prepares documentation, in accordance with
Section 725.990(i), explaining why an undue safety hazard would be
created if air emission controls specified in Sections 725.985 through
725.988 are installed and operated on the tanks and containers used at the
facility to manage the hazardous waste generated by the organic peroxide
manufacturing process or processes meeting the conditions of subsection
(d)(1) of this Section.
3)
The owner or operator notifies the Agency in writing that hazardous
waste generated by an organic peroxide manufacturing process or
processes meeting the conditions of subsection (d)(1) of this Section are
managed at the facility in tanks or containers meeting the conditions of
subsection (d)(2) of this Section. The notification must state the name and
address of the facility and be signed and dated by an authorized
representative of the facility owner or operator.
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
Section 725.984
Waste Determination Procedures
a)
Waste determination procedure for volatile organic (VO) concentration of a
hazardous waste at the point of waste origination.
1)
An owner or operator shall determine the average VO concentration at
the point of waste origination for each hazardous waste placed in a waste
management unit exempted under the provisions of Section 725.983(c)(1)
from using air emission controls in accordance with standards specified in
Section 725.985 through Section 725.988, as applicable to the waste
management unit.
A)
An owner or operator shall make an initial determination of the
average VO concentration of the waste stream before the first time
any portion of the material in the hazardous waste stream is placed
in a waste management unit exempted under the provisions of
Section 725.983(c)(1) from using air emission controls.
Thereafter, an owner or operator shall make an initial
determination of the average VO concentration of the waste
stream for each averaging period that a hazardous waste is
managed in the unit.
223
B)
An owner or operator shall perform a new waste determination
whenever changes to the source generating the waste stream are
reasonably likely to cause the average VO concentration of the
hazardous waste to increase to a level that is equal to or greater
than the VO concentration limits specified in Section
725.983(c)(1).
2)
For a waste determination that is required by subsection (a)(1) of this
Section, the average VO concentration of a hazardous waste at the point
of waste origination must be determined using either direct measurement,
as specified in subsection (a)(3) of this Section, or by knowledge of the
waste, as specified in subsection (a)(4) of this Section.
3)
Direct measurement to determine average VO concentration of a
hazardous waste at the point of waste origination.
A)
Identification. The owner or operator shall identify and record
the point of waste origination for the hazardous waste.
B)
Sampling. Samples of the hazardous waste stream must be
collected at the point of waste origination in such a manner that
volatilization of organics contained in the waste and in the
subsequent sample is minimized and an adequately representative
sample is collected and maintained for analysis by the selected
method.
i)
The averaging period to be used for determining the
average VO concentration for the hazardous waste stream
on a mass-weighted average basis must be designated and
recorded. The averaging period can represent any time
interval that the owner or operator determines is
appropriate for the hazardous waste stream but must not
exceed one year.
ii)
A sufficient number of samples, but no fewer than four
samples, must be collected for a hazardous waste
determination. All of the samples for a given waste
determination must be collected within a one-hour period.
The average of the four or more sample results constitutes
a waste determination for the waste stream. One or more
waste determinations may be required to represent the
complete range of waste compositions and quantities that
occur during the entire averaging period due to normal
variations in the operating conditions for the source or
process generating the hazardous waste stream. Examples
224
of such normal variations are seasonal variations in waste
quantity or fluctuations in ambient temperature.
iii)
All samples must be collected and handled in accordance
with written procedures prepared by the owner or
operator and documented in a site sampling plan. This
plan must describe the procedure by which representative
samples of the hazardous waste stream are collected so that
a minimum loss of organics occurs throughout the sample
collection and handling process, and by which sample
integrity is maintained. A copy of the written sampling
plan must be maintained on-site in the facility operating
records. An example of an acceptable sampling plan
includes a plan incorporating sample collection and
handling procedures in accordance with the requirements
specified in “Test Methods for Evaluating Solid Waste,
Physical/Chemical Methods,” USEPA Publication SW-
846, incorporated by reference in 35 Ill. Adm. Code
720.111, or in Method 25D in 40 CFR 60, appendix A,
incorporated by reference in 35 Ill. Adm. Code 720.111.
iv)
Sufficient information, as specified in the “site sampling
plan” required under subsection (a)(3)(B)(iii) of this
Section, must be prepared and recorded to document the
waste quantity represented by the samples and, as
applicable, the operating conditions for the source or
process generating the hazardous waste represented by the
samples.
C)
Analysis. Each collected sample must be prepared and analyzed
in accordance with one or more of the methods listed in
subsections (a)(3)(C)(i) through (a)(3)(C)(ix) of this Section,
including the appropriate quality assurance and quality control
(QA/QC) checks and use of target compounds for calibration. If
Method 25D in 40 CFR 60, appendix A, incorporated by
reference in 35 Ill. Adm. Code 720.111, is not used, then one or
more methods should be chosen that are appropriate to ensure that
the waste determination accounts for and reflects all organic
compounds in the waste with Henry’s law constant values at least
0.1 mole-fraction-in-the-gas-phase/mole-fraction-in-the-liquid-phase
(0.1 Y/X) (which can also be expressed as 1.8
×
10
-6
atmospheres/gram-mole/m
3
) at 25° C (77° F). Each of the
analytical methods listed in subsections (a)(3)(C)(ii) through
(a)(3)(C)(vii) of this Section has an associated list of approved
chemical compounds for which USEPA considers the method
225
appropriate for measurement. If an owner or operator uses
USEPA Method 624, 625, 1624, or 1625 in 40 CFR 136,
appendix A, incorporated by reference in 35 Ill. Adm. Code
720.111, to analyze one or more compounds that are not on that
method’s published list, the Alternative Test Procedure contained
in 40 CFR 136.4 and 136.5, incorporated by reference in 35 Ill.
Adm. Code 720.111, must be followed. If an owner or operator
uses USEPA Method 8260 or 8270 in “Test Methods for
Evaluating Solid Waste, Physical/Chemical Methods”, USEPA
Publication SW-846, incorporated by reference in 35 Ill. Adm.
Code 720.111, to analyze one or more compounds that are not on
that method’s published list, the procedures in subsection
(a)(3)(C)(viii) of this Section must be followed. At the owner’s or
operator’s discretion, the owner or operator may adjust test data
measured by a method other than Method 25D to the
corresponding average VO concentration value that would have
been obtained, had the waste samples been analyzed using Method
25D. To adjust these data, the measured concentration of each
individual chemical constituent contained in the waste is multiplied
by the constituent-specific adjustment factor (f
m25D
). If the owner
or operator elects to adjust test data, the adjustment must be made
to all individual chemical constituents with a Henry's law constant
value greater than or equal to 0.1 Y/X at 25° C contained in the
waste. Constituent-specific adjustment factors (f
m25D
) can be
obtained by contacting the USEPA, Waste and Chemical
Processes Group, Office of Air Quality Planning and Standards,
Research Triangle Park, NC 27711.
i)
Method 25D in 40 CFR 60, appendix A, incorporated by
reference in 35 Ill. Adm. Code 720.111.
ii)
Method 624 in 40 CFR 136, appendix A, incorporated by
reference in 35 Ill. Adm. Code 720.111.
iii)
Method 625 in 40 CFR 136, appendix A, incorporated by
reference in 35 Ill. Adm. Code 720.111. Perform
corrections to the compounds for which the analysis is
being conducted based on the “accuracy as recovery”
using the factors in Table 7 of the method.
iv)
Method 1624 in 40 CFR 136, appendix A, incorporated
by reference in 35 Ill. Adm. Code 720.111.
v)
Method 1625 in 40 CFR 136, appendix A, incorporated
by reference in 35 Ill. Adm. Code 720.111.
226
vi)
Method 8260 in “Test Methods for Evaluating Solid
Waste, Physical/Chemical Methods”, USEPA Publication
SW-846, incorporated by reference in 35 Ill. Adm. Code
720.111. Maintain a formal quality assurance program
consistent with the requirements of Method 8260. The
quality assurance program must include the elements set
forth in subsection (a)(3)(F) of this Section.
vii)
Method 8270 in “Test Methods for Evaluating Solid
Waste, Physical/Chemical Methods”, USEPA Publication
SW-846, incorporated by reference in 35 Ill. Adm. Code
720.111. Maintain a formal quality assurance program
consistent with the requirements of Method 8270. The
quality assurance program must include the elements set
forth in subsection (a)(3)(F) of this Section.
viii)
Any other USEPA standard method that has been
validated in accordance with “Alternative Validation
Procedure for USEPA Waste and Wastewater Methods”,
40 CFR 63, appendix D, incorporated by reference in 35
Ill. Adm. Code 720.111. As an alternative, other USEPA
standard methods may be validated by the procedure
specified in subsection (a)(3)(C)(ix) of this Section.
ix)
Any other analysis method that has been validated in
accordance with the procedures specified in Section 5.1 or
Section 5.3, and the corresponding calculations in Section
6.1 or Section 6.3, of Method 301 in 40 CFR 63,
appendix A, incorporated by reference in 35 Ill. Adm.
Code 720.111. The data are acceptable if they meet the
criteria specified in Section 6.1.5 or Section 6.3.3 of
Method 301. If correction is required under Section 6.3.3
of Method 301, the data are acceptable if the correction
factor is within the range 0.7 to 1.30. Other Sections of
Method 301 are not required.
D)
Calculations.
i)
The average VO concentration (
C
) on a mass-weighted
basis must be calculated by using the results for all waste
determinations conducted in accordance with subsections
(a)(3)(B) and (a)(3)(C) of this Section and the following
equation:
227
C =
1
Q
x
n
i = 1
(Q x C )
T
i
i
∑
1Where:
C
=
Average VO concentration of the hazardous
waste at the point of waste origination on a
mass-weighted basis, in ppmw.
i =
Individual waste determination “i” of the
hazardous waste.
n =
Total number of waste determinations of the
hazardous waste conducted for the
averaging period (not to exceed one year).
Q
i
=
Mass quantity of the hazardous waste
stream represented by C
i
, in kg/hr.
Q
T
=
Total mass quantity of the hazardous waste
during the averaging period, in kg/hr.
C
i
=
Measured VO concentration of waste
determination “i”, as determined in
accordance with subsection (a)(3)(C) of this
Section (i.e., the average of the four or
more samples specified in subsection
(a)(3)(B)(ii) of this Section), in ppmw.
ii)
For the purpose of determining C
i
, for individual waste
samples analyzed in accordance with subsection (a)(3)(C)
of this Section, the owner or operator shall account for
VO concentrations determined to be below the limit of
detection of the analytical method by using the VO
concentration determined according to subsection (a)(3)(G)
of this Section.
E)
Provided that the test method is appropriate for the waste as
required under subsection (a)(3)(C) of this Section, the Agency
must determine compliance based on the test method used by the
owner or operator as recorded pursuant to Section 725.990(f)(1).
F)
The quality assurance program elements required under
228
subsections (a)(3)(C)(vi) and (a)(3)(C)(vii) of this Section are as
follows:
i)
Documentation of site-specific procedures to minimize the
loss of compounds due to volatilization, biodegradation,
reaction, or sorption during the sample collection, storage,
preparation, introduction, and analysis steps.
ii)
Measurement of the overall accuracy and precision of the
specific procedures.
BOARD NOTE: Subsections (a)(3)(F)(i) and (a)(3)(F)(ii) are
derived from 40 CFR 265.984(a)(3)(iii)(F)(1), (a)(3)(iii)(F)(2),
(a)(3)(iii)(G)(1), and (a)(3)(iii)(G)(2), which the Board has codified
here to comport with Illinois Administrative Code format
requirements.
G)
VO concentrations below the limit of detection must be considered
to be as follows:
i)
If Method 25D in 40 CFR 60, appendix A, incorporated
by reference in 35 Ill. Adm. Code 720.111, is used for the
analysis, the VO concentration must be considered to be
one-half the blank value determined in the method at
Section 4.4 of Method 25D in 40 CFR 60, appendix A.
ii)
If any other analytical method is used, the VO
concentration must be considered to be one-half the sum of
the limits of detection established for each organic
constituent in the waste that has a Henry’s law constant
value at least 0.1 mole-fraction-in-the-gas-phase/mole-
fraction-in-the-liquid-phase (0.1 Y/X) (which can also be
expressed as 1.8 x 10
-6
atmospheres/gram-mole/m
3
) at 25°
C.
BOARD NOTE: Subsections (a)(3)(G)(i) and (a)(3)(G)(ii) are
derived from 40 CFR 265.984(a)(3)(iv)(A)(1) and (a)(3)(iv)(A)(2),
which the Board has codified here to comport with Illinois
Administrative Code format requirements.
4)
Use of owner or operator knowledge to determine average VO
concentration of a hazardous waste at the point of waste origination.
A)
Documentation must be prepared that presents the information
used as the basis for the owner’s or operator’s knowledge of the
229
hazardous waste stream’s average VO concentration. Examples
of information that may be used as the basis for knowledge
include the following: material balances for the source or process
generating the hazardous waste stream; constituent-specific
chemical test data for the hazardous waste stream from previous
testing that are still applicable to the current waste stream;
previous test data for other locations managing the same type of
waste stream; or other knowledge based on information included
in manifests, shipping papers, or waste certification notices.
B)
If test data are used as the basis for knowledge, then the owner or
operator shall document the test method, sampling protocol, and
the means by which sampling variability and analytical variability
are accounted for in the determination of the average VO
concentration. For example, an owner or operator may use
organic concentration test data for the hazardous waste stream that
are validated in accordance with Method 301 in 40 CFR 63,
appendix A, incorporated by reference in 35 Ill. Adm. Code
720.111, as the basis for knowledge of the waste.
C)
An owner or operator using chemical constituent-specific
concentration test data as the basis for knowledge of the hazardous
waste may adjust the test data to the corresponding average VO
concentration value that would have been obtained had the waste
samples been analyzed using Method 25D in 40 CFR 60,
appendix A, incorporated by reference in 35 Ill. Adm. Code
720.111. To adjust these data, the measured concentration for
each individual chemical constituent contained in the waste is
multiplied by the appropriate constituent-specific adjustment factor
(f
m25D
).
D)
In the event that the Agency and the owner or operator disagree
on a determination of the average VO concentration for a
hazardous waste stream using knowledge, then the results from a
determination of average VO concentration using direct
measurement, as specified in subsection (a)(3) of this Section,
must be used to establish compliance with the applicable
requirements of this Subpart. The Agency may perform or
request that the owner or operator perform this determination
using direct measurement. The owner or operator may choose
one or more appropriate methods to analyze each collected sample
in accordance with the requirements of subsection (a)(3)(C) of this
Section.
b)
Waste determination procedures for treated hazardous waste.
230
1)
An owner or operator shall perform the applicable waste determination
for each treated hazardous waste placed in a waste management unit
exempted under the provisions of Section 725.983(c)(2)(A) through
(c)(2)(F) from using air emission controls in accordance with the
standards specified in Sections 725.985 through 725.988, as applicable to
the waste management unit.
A)
An owner or operator shall make an initial determination of the
average VO concentration of the waste stream before the first time
any portion of the material in the treated waste stream is placed in
the waste management unit exempt under Section 725.983(c)(2),
(c)(3), or (c)(4) from using air emission controls. Thereafter, an
owner or operator shall update the information used for the waste
determination at least once every 12 months following the date of
the initial waste determination.
B)
An owner or operator shall perform a new waste determination
whenever changes to the process generating or treating the waste
stream are reasonably likely to cause the average VO
concentration of the hazardous waste to increase to such a level
that the applicable treatment conditions specified in Section
725.983 (c)(2), (c)(3), or (c)(4) are not achieved.
2)
The owner or operator shall designate and record the specific provision
in Section 725.983(c)(2) under which the waste determination is being
performed. The waste determination for the treated hazardous waste
must be performed using the applicable procedures specified in
subsections (b)(3) through (b)(9) of this Section.
3)
Procedure to determine the average VO concentration of a hazardous
waste at the point of waste treatment.
A)
Identification. The owner or operator shall identify and record
the point of waste treatment for the hazardous waste.
B)
Sampling. Samples of the hazardous waste stream must be
collected at the point of waste treatment in such a manner that
volatilization of organics contained in the waste and in the
subsequent sample is minimized and an adequately representative
sample is collected and maintained for analysis by the selected
method.
i)
The averaging period to be used for determining the
average VO concentration for the hazardous waste stream
231
on a mass-weighted average basis must be designated and
recorded. The averaging period can represent any time
interval that the owner or operator determines is
appropriate for the hazardous waste stream but must not
exceed one year.
ii)
A sufficient number of samples, but no fewer than four
samples, must be collected and analyzed for a hazardous
waste determination. All of the samples for a given waste
determination must be collected within a one-hour period.
The average of the four or more sample results constitutes
a waste determination for the hazardous waste stream.
One or more waste determinations may be required to
represent the complete range of waste compositions and
quantities that occur during the entire averaging period due
to normal variations in the operating conditions for the
process generating or treating the hazardous waste stream.
Examples of such normal variations are seasonal variations
in waste quantity or fluctuations in ambient temperature.
iii)
All samples must be collected and handled in accordance
with written procedures prepared by the owner or
operator and documented in a site sampling plan. This
plan must describe the procedure by which representative
samples of the hazardous waste stream are collected so that
a minimum loss of organics occurs throughout the sample
collection and handling process, and by which sample
integrity is maintained. A copy of the written sampling
plan must be maintained on-site in the facility operating
records. An example of an acceptable sampling plan
includes a plan incorporating sample collection and
handling procedures in accordance with the requirements
specified in “Test Methods for Evaluating Solid Waste,
Physical/Chemical Methods,” USEPA Publication No.
SW-846, incorporated by reference in 35 Ill. Adm. Code
720.111, or in Method 25D in 40 CFR 60, appendix A,
incorporated by reference in 35 Ill. Adm. Code 720.111.
iv)
Sufficient information, as specified in the “site sampling
plan” required under subsection (a)(3)(B)(iii) of this
Section, must be prepared and recorded to document the
waste quantity represented by the samples and, as
applicable, the operating conditions for the process treating
the hazardous waste represented by the samples.
232
C)
Analysis. Each collected sample must be prepared and analyzed
in accordance with one or more of the methods listed in
subsections (b)(3)(C)(i) through (b)(3)(C)(ix) of this Section,
including appropriate quality assurance and quality control
(QA/QC) checks and use of target compounds for calibration.
When the owner or operator is making a waste determination for
a treated hazardous waste that is to be compared to an average
VO concentration at the point of waste origination or the point of
waste entry to the treatment system, to determine if the conditions
of 35 Ill. Adm. Code 724.982(c)(2)(A) through (c)(2)(F) or
Section 725.983(c)(2)(A) through (c)(2)(F) are met, then the waste
samples must be prepared and analyzed using the same method or
methods as were used in making the initial waste determinations at
the point of waste origination or at the point of entry to the
treatment system. If Method 25D in 40 CFR 60, appendix A is
not used, then one or more methods should be chosen that are
appropriate to ensure that the waste determination accounts for
and reflects all organic compounds in the waste with Henry’s law
constant values at least 0.1 mole-fraction-in-the-gas-phase/mole-
fraction-in-the-liquid-phase (0.1 Y/X) [(which can also be
expressed as 1.8
×
10
-6
atmospheres/gram-mole/m
3
]) at 25 degrees
Celsius. Each of the analytical methods listed in subsections
(b)(3)(C)(ii) through (b)(3)(C)(vii) of this Section has an associated
list of approved chemical compounds, for which USEPA
considers the method appropriate for measurement. If an owner
or operator uses USEPA Method 624, 625, 1624, or 1625 in 40
CFR 136, appendix A, incorporated by reference in 35 Ill. Adm.
Code 720.111, to analyze one or more compounds that are not on
that method’s published list, the Alternative Test Procedure
contained in 40 CFR 136.4 and 136.5, incorporated by reference
in 35 Ill. Adm. Code 720.111, must be followed. If an owner or
operator uses USEPA Method 8260 or 8270 in “Test Methods for
Evaluating Solid Waste, Physical/Chemical Methods”, USEPA
Publication SW-846, incorporated by reference in 35 Ill. Adm.
Code 720.111, to analyze one or more compounds that are not on
that method’s published list, the procedures in subsection
(b)(3)(C)(viii) of this Section must be followed. At the owner’s or
operator’s discretion, the owner or operator may adjust test data
measured by a method other than Method 25D to the
corresponding average VO concentration value that would have
been obtained, had the waste samples been analyzed using Method
25D. To adjust these data, the measured concentration of each
individual chemical constituent contained in the waste is multiplied
by the constituent-specific adjustment factor (f
m25D
). If the owner
or operator elects to adjust test data, the adjustment must be made
233
to all individual chemical constituents with a Henry's law constant
value greater than or equal to 0.1 Y/X at 25° C contained in the
waste. Constituent-specific adjustment factors (f
m25D
) can be
obtained by contacting the USEPA, Waste and Chemical
Processes Group, Office of Air Quality Planning and Standards,
Research Triangle Park, NC 27711.
i)
Method 25D in 40 CFR 60, appendix A, incorporated by
reference in 35 Ill. Adm. Code 720.111.
ii)
Method 624 in 40 CFR 136, appendix A, incorporated by
reference in 35 Ill. Adm. Code 720.111.
iii)
Method 625 in 40 CFR 136, appendix A, incorporated by
reference in 35 Ill. Adm. Code 720.111. Perform
corrections to the compounds for which the analysis is
being conducted based on the “accuracy as recovery”
using the factors in Table 7 of the method.
iv)
Method 1624 in 40 CFR 136, appendix A, incorporated
by reference in 35 Ill. Adm. Code 720.111.
v)
Method 1625 in 40 CFR 136, appendix A, incorporated
by reference in 35 Ill. Adm. Code 720.111.
vi)
Method 8260 in “Test Methods for Evaluating Solid
Waste, Physical/Chemical Methods”, USEPA Publication
SW-846, incorporated by reference in 35 Ill. Adm. Code
720.111. Maintain a formal quality assurance program
consistent with the requirements of Method 8260. The
quality assurance program must include the elements set
forth in subsection (b)(3)(E) of this Section.
vii)
Method 8270 in “Test Methods for Evaluating Solid
Waste, Physical/Chemical Methods”, USEPA Publication
SW-846, incorporated by reference in 35 Ill. Adm. Code
720.111. Maintain a formal quality assurance program
consistent with the requirements of Method 8270. The
quality assurance program must include the elements set
forth in subsection (b)(3)(E) of this Section.
viii)
Any other USEPA standard method that has been
validated in accordance with “Alternative Validation
Procedure for EPA Waste and Wastewater Methods”, 40
CFR 63, appendix D, incorporated by reference in 35 Ill.
234
Adm. Code 720.111. As an alternative, other USEPA
standard methods may be validated by the procedure
specified in subsection (b)(3)(C)(ix) of this Section.
ix)
Any other analysis method that has been validated in
accordance with the procedures specified in Section 5.1 or
Section 5.3, and the corresponding calculations in Section
6.1 or Section 6.3, of Method 301 in 40 CFR 63,
appendix A. The data are acceptable if they meet the
criteria specified in Section 6.1.5 or Section 6.3.3 of
Method 301. If correction is required under Section 6.3.3
of Method 301, the data are acceptable if the correction
factor is within the range 0.7 to 1.30. Other Sections of
Method 301 are not required.
D)
Calculations. The average VO concentration (
C
) on a mass-
weighted basis must be calculated by using the results for all
samples analyzed in accordance with subsection (b)(3)(C) of this
Section and the following equation:
C =
1
Q
x
n
i = 1
(Q x C )
T
i
i
∑
2
Where:
C
=
Average VO concentration of the hazardous waste
at the point of waste treatment on a mass-weighted
basis, in ppmw.
i =
Individual determination “i” of the hazardous
waste.
n =
Total number of waste determinations of the
hazardous waste collected for the averaging period
(not to exceed 1 year).
Q
i
=
Mass quantity of the hazardous waste stream
represented by C
i
, in kg/hr.
Q
T
=
Total mass quantity of hazardous waste during the
averaging period, in kg/hr.
C
i
=
Measured VO concentration of waste
235
determinations “i”, as determined in accordance
with the requirements of subsection (b)(3)(C) of this
Section (i.e., the average of the four or more
samples specified in subsection (b)(3)(B)(ii) of this
Section), in ppmw.
E)
Provided that the test method is appropriate for the waste as
required under subsection (b)(3)(C) of this Section, compliance
must be determined based on the test method used by the owner
or operator as recorded pursuant to Section 725.990(f)(1).
4)
Procedure to determine the exit concentration limit (C
t
) for a treated
hazardous waste.
A)
The point of waste origination for each hazardous waste treated
by the process at the same time must be identified.
B)
If a single hazardous waste stream is identified in subsection
(b)(4)(A) of this Section, then the exit concentration limit (C
t
) must
be 500 ppmw.
C)
If more than one hazardous waste stream is identified in
subsection (b)(4)(A) of this Section, then the average VO
concentration of each hazardous waste stream at the point of waste
origination must be determined in accordance with the
requirements of subsection (a) of this Section. The exit
concentration limit (C
t
) must be calculated by using the results
determined for each individual hazardous waste stream and the
following equation:
t
x
x
y
x
y
C
=
m
x = 1
(Q
x C
) +
n
y = 1
(Q
x500ppmw)
m
x = 1
Q
+
n
y = 1
Q
∑
∑
∑
∑
3
Where:
C
t
=
Exit concentration limit for treated hazardous
waste, in ppmw.
x =
Individual hazardous waste stream “x” that has an
average VO concentration less than 500 ppmw at
236
the point of waste origination, as determined in
accordance with the requirements of subsection (a)
of this Section.
y =
Individual hazardous waste stream “y” that has an
average VO concentration equal to or greater than
500 ppmw at the point of waste origination, as
determined in accordance with the requirements of
subsection (a) of this Section.
m =
Total number of “x” hazardous waste streams
treated by process.
n =
Total number of “y” hazardous waste streams
treated by process.
Q
x
=
Annual mass quantity of hazardous waste stream
“x”, in kg/yr.
Q
y
=
Annual mass quantity of hazardous waste stream
“y”, in kg/yr.
C
x
=
Average VO concentration of hazardous waste
stream “x” at the point of waste origination, as
determined in accordance with the requirements of
subsection (a) of this Section, in ppmw.
5)
Procedure to determine the organic reduction efficiency (R) for a treated
hazardous waste.
A)
The organic reduction efficiency (R) for a treatment process must
be determined based on results for a minimum of three
consecutive runs.
B)
All hazardous waste streams entering the process and all
hazardous waste streams exiting the treatment process must be
identified. The owner or operator shall prepare a sampling plan
for measuring these streams that accurately reflects the retention
time of the hazardous waste in the process.
C)
For each run, information must be determined for each hazardous
waste stream identified in subsection (b)(5)(B) of this Section,
using the following procedures:
i)
The mass quantity of each hazardous waste stream entering
237
the process (Q
b
) and the mass quantity of each hazardous
waste stream exiting the process (Q
a
) must be determined.
ii)
The average VO concentration at the point of waste
origination of each hazardous waste stream entering the
process (C
b
) during the run must be determined in
accordance with the requirements of subsections subsection
(a)(3) of this Section. The average VO concentration at
the point of waste treatment of each hazardous waste
stream exiting the process (C
a
) during the run must be
determined in accordance with the requirements of
subsection (b)(3) of this Section.
D)
The waste volatile organic mass flow entering the process (E
b
) and
the waste volatile organic mass flow exiting the process (E
a
) must
be calculated by using the results determined in accordance with
subsection (b)(5)(C) of this Section and the following equations:
b
6
bj
bj
E
=
1
10
m
j = 1
(Q
xC
)
∑
4
a
6
aj
aj
E
=
1
10
m
j = 1
(Q
xC
)
∑
5
Where:
E
a
=
Waste volatile organic mass flow exiting the
process, in kg/hr.
E
b
=
Waste volatile organic mass flow entering the
process, in kg/hr.
m =
Total number of runs (at least 3).
j =
Individual run “j”.
Q
bj
=
Mass quantity of hazardous waste entering the
process during run “j”, in kg/hr.
Q
aj
=
Average mass quantity of waste exiting the process
during run “j”, in kg/hr.
238
aj
C
=
Average VO concentration of hazardous waste
exiting the process during run “j”, as determined in
accordance with the requirements of subsection
(b)(3) of this Section, in ppmw.
bj
C
= Average VO concentration of hazardous waste
entering the process during run “j”, as determined
in accordance with the requirements of subsection
725.984 (a)(3) of this Section, in ppmw.
E)
The organic reduction efficiency of the process must be calculated
by using the results determined in accordance with subsection
(b)(5)(D) of this Section and the following equation:
R =
E
- E
E
x100%
b
a
b
6
Where:
R =
Organic reduction efficiency, in percent.
E
b
=
Waste volatile organic mass flow entering the
process as determined in accordance with the
requirements of subsection (b)(5)(D) of this
Section, in kg/hr.
E
a
=
Waste volatile organic mass flow exiting the
process as determined in accordance with the
requirements of subsection (b)(5)(D) of this
Section, in kg/hr.
6)
Procedure to determine the organic biodegradation efficiency (R
bio
) for a
treated hazardous waste.
A)
The fraction of organics biodegraded (F
bio
) must be determined
using the procedure specified in 40 CFR 63, Appendix appendix
C, incorporated by reference in 35 Ill. Adm. Code 720.111.
B)
The organic biodegradation efficiency (R
bio
) must be calculated by
using the following equation:
bio
bio
R
= F
x100%
7
Where:
239
R
bio
= Organic biodegradation efficiency, in percent.
F
bio
= Fraction of organic biodegraded, as determined in
accordance with the requirements of subsection
(b)(6)(A) of this Section.
7)
Procedure to determine the required organic mass removal rate (RMR)
for a treated hazardous waste.
A)
All of the hazardous waste streams entering the treatment process
must be identified.
B)
The average VO concentration of the hazardous waste stream at
the point of waste origination must be determined in accordance
with the requirements of subsection (a) of this Section.
C)
For each individual hazardous waste stream that has an average
volatile organic concentration equal to or greater than 500 ppmw
at the point of waste origination, the average volumetric flow rate
of hazardous waste and the density of the hazardous waste stream
at the point of waste origination must be determined.
D)
The required organic mass removal rate (RMR) for the hazardous
waste must be calculated by using the average VO concentration,
average volumetric flow rate, and density determined for each
individual hazardous waste stream, and the following equation:
RMR =
n
y = 1
V
x k
x
(C
-500ppmw)
10
y
y
y
6
∑
8
Where:
RMR = Required organic mass removal rate, in kg/hr.
y =
Individual hazardous waste stream “y” that has an
average volatile organic (VO) concentration equal
to or greater than 500 ppmw at the point of waste
origination, as determined in accordance with the
requirements of subsection (a) of this Section.
n =
Total number of “y” hazardous waste streams
treated by process.
240
V
y
=
Average volumetric flow rate of hazardous waste
stream “y” at the point of waste origination, in
m
3
/hr.
k
y
=
Density of hazardous waste stream “y”, in kg/m
3
.
C
y
= Average VO concentration of hazardous waste
stream “y” at the point of waste origination, as
determined in accordance with the requirements of
subsection (a) of this Section, in ppmw.
8)
Procedure to determine the actual organic mass removal rate (MR) for a
treated hazardous waste.
A)
The actual organic mass removal rate (MR) must be determined
based on results for a minimum of three consecutive runs. The
sampling time for each run must be one hour.
B)
The waste volatile organic mass flow entering the process (E
b
) and
the waste volatile organic mass flow exiting the process (E
a
) must
be determined in accordance with the requirements of subsection
(b)(5)(D) of this Section.
C)
The actual organic mass removal rate (MR) must be calculated by
using the mass flow rate determined in accordance with the
requirements of subsection (b)(8)(B) of this Section and the
following equation:
MR = E
- E
b
a
9
Where:
MR = Actual organic mass removal rate, in kg/hr.
E
b
=
Waste volatile organic mass flow entering the
process, as determined in accordance with the
requirements of subsection (b)(5)(D) of this
Section, in kg/hr.
E
a
=
Waste volatile organic mass flow exiting the
process, as determined in accordance with the
requirements of subsection (b)(5)(D) of this
Section, in kg/hr.
241
9)
Procedure to determine the actual organic mass biodegradation rate
(MR
bio
) for a treated hazardous waste.
A)
The actual organic mass biodegradation rate (MR
bio
) must be
determined based on results for a minimum of three consecutive
runs. The sampling time for each run must be one hour.
B)
The waste organic mass flow entering the process (E
b
) must be
determined in accordance with the requirements of subsection
(b)(5)(D) of this Section.
C)
The fraction of organic biodegraded (F
bio
) must be determined
using the procedure specified in 40 CFR 63, Appendix appendix
C, incorporated by reference in 35 Ill. Adm. Code 720.111.
D)
The actual organic mass biodegradation rate (MR
bio
) must be
calculated by using the mass flow rates and fraction of organic
biodegraded, as determined in accordance with the requirements
of subsections (b)(9)(B) and (b)(9)(C) of this Section, respectively,
and the following equation:
bio
b
bio
MR
= E
x F
10
Where:
MR
bio
= Actual organic mass biodegradation rate, in
kg/hr.
E
b
=
Waste organic mass flow entering the process, as
determined in accordance with the requirements of
subsection (b)(5)(D) of this Section, in kg/hr.
F
bio
= Fraction of organic biodegraded, as determined in
accordance with the requirements of subsection
(b)(9)(C) of this Section.
c)
Procedure to determine the maximum organic vapor pressure of a hazardous
waste in a tank.
1)
An owner or operator shall determine the maximum organic vapor
pressure for each hazardous waste placed in a tank using Tank Level 1
controls in accordance with standards specified in Section 725.985(c).
2)
An owner or operator shall use either direct measurement, as specified in
subsection (c)(3) of this Section, or knowledge of the waste, as specified
242
by subsection (c)(4) of this Section, to determine the maximum organic
vapor pressure that is representative of the hazardous waste composition
stored or treated in the tank.
3)
Direct measurement to determine the maximum organic vapor pressure of
a hazardous waste.
A)
Sampling. A sufficient number of samples must be collected to be
representative of the waste contained in the tank. All samples
must be conducted and handled in accordance with written
procedures prepared by the owner or operator and documented in
a site sampling plan. This plan must describe the procedure by
which representative samples of the hazardous waste are collected
so that a minimum loss of organics occurs throughout the sample
collection and handling process and by which sample integrity is
maintained. A copy of the written sampling plan must be
maintained on-site in the facility operating records. An example
of an acceptable sampling plan includes a plan incorporating
sample collection and handling procedures in accordance with the
requirements specified in “Test Methods for Evaluating Solid
Waste, Physical/Chemical Methods”, USEPA Publication No.
SW-846, incorporated by reference in 35 Ill. Adm. Code
720.111, or in Method 25D in 40 CFR 60, appendix A,
incorporated by reference in 35 Ill. Adm. Code 720.111.
B)
Analysis. Any appropriate one of the following methods may be
used to analyze the samples and compute the maximum organic
vapor pressure of the hazardous waste:
i)
Method 25E in 40 CFR 60, Appendix appendix A,
incorporated by reference in 35 Ill. Adm. Code 720.111;
ii)
Methods described in American Petroleum Institute
Publication 2517, incorporated by reference in 35 Ill.
Adm. Code 720.111;
iii)
Methods obtained from standard reference texts;
iv)
ASTM Method D 2879-92, incorporated by reference in
35 Ill. Adm. Code 720.111; or
v)
Any other method approved by the Agency.
4)
Use of knowledge to determine the maximum organic vapor pressure of
the hazardous waste. Documentation must be prepared and recorded that
243
presents the information used as the basis for the owner’s or operator’s
knowledge that the maximum organic vapor pressure of the hazardous
waste is less than the maximum vapor pressure limit listed in Section
725.985(b)(1)(A) for the applicable tank design capacity category. An
example of information that may be used is documentation that the
hazardous waste is generated by a process for which at other locations it
previously has been determined by direct measurement that the waste
maximum organic vapor pressure is less than the maximum vapor
pressure limit for the appropriate tank design capacity category.
d)
Procedure The procedure for determining no detectable organic emissions for the
purpose of complying with this Subpart is as follows:
1)
The test must be conducted in accordance with the procedures specified
in Method 21 of 40 CFR 60, appendix A, incorporated by reference in
35 Ill. Adm. Code 720.111. Each potential leak interface (i.e., a location
where organic vapor leakage could occur) on the cover and associated
closure devices must be checked. Potential leak interfaces that are
associated with covers and closure devices include, but are not limited to,
any of the following: the interface of the cover and its foundation
mounting, the periphery of any opening on the cover and its associated
closure device, and the sealing seat interface on a spring-loaded pressure
relief valve.
2)
The test must be performed when the unit contains a hazardous waste
having an organic concentration representative of the range of
concentrations for the hazardous waste expected to be managed in the
unit. During the test, the cover and closure devices must be secured in
the closed position.
3)
The detection instrument must meet the performance criteria of Method
21 of 40 CFR 60, appendix A, incorporated by reference in 35 Ill. Adm.
Code 720.111, except the instrument response factor criteria in Section
3.1.2(a) of Method 21 must be for the average composition of the organic
constituents in the hazardous waste placed in the waste management unit,
not for each individual organic constituent.
4)
The detection instrument must be calibrated before use on each day of its
use by the procedures specified in Method 21 of 40 CFR 60, appendix
A, incorporated by reference in 35 Ill. Adm. Code 720.111.
5)
Calibration gases must be as follows:
A)
Zero air (less than 10 ppmv hydrocarbon in air), and
244
B)
A mixture of methane or n-hexane in air at a concentration of
approximately, but less than, 10,000 ppmv methane or n-hexane.
6)
The background level must be determined according to the procedures in
Method 21 of 40 CFR 60, appendix A, incorporated by reference in 35
Ill. Adm. Code 720.111.
7)
Each potential leak interface must be checked by traversing the instrument
probe around the potential leak interface as close to the interface as
possible, as described in Method 21 of 40 CFR 60, appendix A,
incorporated by reference in 35 Ill. Adm. Code 720.111. In the case
when the configuration of the cover or closure device prevents a
complete traverse of the interface, all accessible portions of the interface
must be sampled. In the case when the configuration of the closure
device prevents any sampling at the interface and the device is equipped
with an enclosed extension or horn (e.g., some pressure relief devices),
the instrument probe inlet must be placed at approximately the center of
the exhaust area to the atmosphere.
8)
The arithmetic difference between the maximum organic concentration
indicated by the instrument and the background level must be compared
with the value of 500 ppmv except when monitoring a seal around a
rotating shaft that passes through a cover opening, in which case the
comparison must be as specified in subsection (d)(9) of this Section. If
the difference is less than 500 ppmv, then the potential leak interface is
determined to operate with no detectable organic emissions.
9)
For the seals around a rotating shaft that passes through a cover opening,
the arithmetic difference between the maximum organic concentration
indicated by the instrument and the background level must be compared
with the value of 10,000 ppmw. If the difference is less than 10,000
ppmw, then the potential leak interface is determined to operate with no
detectable organic emissions.
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
Section 725.987
Standards: Containers
a)
The provisions of this Section apply to the control of air pollutant emissions from
containers for which Section 725.983(b) references the use of this Section for
such air emission control.
b)
General requirements.
1)
The owner or operator shall control air pollutant emissions from each
245
container subject to this Section in accordance with the following
requirements, as applicable to the container, except when the special
provisions for waste stabilization processes specified in subsection (b)(2)
of this Section apply to the container.
A)
For a container having a design capacity greater than 0.1 m
3
(26
gal) and less than or equal to 0.46 m
3
(120 gal), the owner or
operator shall control air pollutant emissions from the container in
accordance with the Container Level 1 standards specified in
subsection (c) of this Section.
B)
For a container having a design capacity greater than 0.46 m
3
(120 gal) that is not in light material service, the owner or
operator shall control air pollutant emissions from the container in
accordance with the Container Level 1 standards specified in
subsection (c) of this Section.
C)
For a container having a design capacity greater than 0.46 m
3
(120 gal) that is in light material service, the owner or operator
shall control air pollutant emissions from the container in
accordance with the Container Level 2 standards specified in
subsection (d) of this Section.
2)
When a container having a design capacity greater than 0.1 m
3
(26 gal) is
used for treatment of a hazardous waste by a waste stabilization process,
the owner or operator shall control air pollutant emissions from the
container in accordance with the Container Level 3 standards specified in
subsection (e) of this Section at those times during the waste stabilization
process when the hazardous waste in the container is exposed to the
atmosphere.
c)
Container Level 1 standards.
1)
A container using Container Level 1 controls is one of the following:
A)
A container that meets the applicable USDOT regulations on
packaging hazardous materials for transportation, as specified in
subsection (f) of this Section.
B)
A container equipped with a cover and closure devices that form a
continuous barrier over the container openings so that when the
cover and closure devices are secured in the closed position there
are no visible holes, gaps, or other open spaces into the interior of
the container. The cover may be a separate cover installed on the
container (e.g., a lid on a drum or a suitably secured tarp on a
246
roll-off box) or may be an integral part of the container structural
design (e.g., a “portable tank” or bulk cargo container equipped
with a screw-type cap).
C)
An open-top container in which an organic-vapor suppressing
barrier is placed on or over the hazardous waste in the container
so that no hazardous waste is exposed to the atmosphere. One
example of such a barrier is application of a suitable organic-
vapor suppressing foam.
2)
A container used to meet the requirements of subsection (c)(1)(B) or
(c)(1)(C) of this Section must be equipped with covers and closure
devices, as applicable to the container, that are composed of suitable
materials to minimize exposure of the hazardous waste to the atmosphere
and to maintain the equipment integrity for as long as it is in service.
Factors to be considered in selecting the materials of construction and
designing the cover and closure devices must include the following: the
organic vapor permeability,; the effects of contact with the hazardous
waste or its vapor managed in the container; the effects of outdoor
exposure of the closure device or cover material to wind, moisture, and
sunlight; and the operating practices for which the container is intended to
be used.
3)
Whenever a hazardous waste is in a container using Container Level 1
controls, the owner or operator shall install all covers and closure devices
for the container, as applicable to the container, and secure and maintain
each closure device in the closed position except as follows:
A)
Opening of a closure device or cover is allowed for the purpose
of adding hazardous waste or other material to the container as
follows:
i)
In the case when the container is filled to the intended final
level in one continuous operation, the owner or operator
shall promptly secure the closure devices in the closed
position and install the covers, as applicable to the
container, upon conclusion of the filling operation.
ii)
In the case when discrete quantities or batches of material
intermittently are added to the container over a period of
time, the owner or operator shall promptly secure the
closure devices in the closed position and install covers, as
applicable to the container, upon either the container being
filled to the intended final level; the completion of a batch
loading after which no additional material will be added to
247
the container within 15 minutes; the person performing the
loading operation leaving the immediate vicinity of the
container; or the shutdown of the process generating the
material being added to the container, whichever condition
occurs first.
B)
Opening of a closure device or cover is allowed for the purpose
of removing hazardous waste from the container as follows:
i)
For the purpose of meeting the requirements of this
Section, an empty container, as defined in 35 Ill. Adm.
Code 721.107(b), may be open to the atmosphere at any
time (i.e., covers and closure devices are not required to
be secured in the closed position on an empty container).
ii)
In the case when discrete quantities or batches of material
are removed from the container but the container does not
meet the conditions to be an empty container, as defined in
35 Ill. Adm. Code 721.107(b), the owner or operator shall
promptly secure the closure devices in the closed position
and install covers, as applicable to the container, upon the
completion of a batch removal after which no additional
material will be removed from the container within 15
minutes or the person performing the unloading operation
leaves the immediate vicinity of the container, whichever
condition occurs first.
C)
Opening of a closure device or cover is allowed when access
inside the container is needed to perform routine activities other
than transfer of hazardous waste. Examples of such activities
include those times when a worker needs to open a port to
measure the depth of or sample the material in the container, or
when a worker needs to open a manhole hatch to access
equipment inside the container. Following completion of the
activity, the owner or operator shall promptly secure the closure
device in the closed position or reinstall the cover, as applicable to
the container.
D)
Opening of a spring-loaded, pressure-vacuum relief valve,
conservation vent, or similar type of pressure relief device that
vents to the atmosphere is allowed during normal operations for
the purpose of maintaining the container internal pressure in
accordance with the design specifications of the container. The
device must be designed to operate with no detectable organic
emissions when the device is secured in the closed position. The
248
settings at which the device opens must be established so that the
device remains in the closed position whenever the internal
pressure of the container is within the internal pressure operating
range determined by the owner or operator based on container
manufacturer recommendations, applicable regulations, fire
protection and prevention codes, standard engineering codes and
practices, or other requirements for the safe handling of
flammable, ignitable, explosive, reactive, or hazardous materials.
Examples of normal operating conditions that may require these
devices to open are during those times when the internal pressure
of the container exceeds the internal pressure operating range for
the container as a result of loading operations or diurnal ambient
temperature fluctuations.
E)
Opening of a safety device, as defined in Section 725.981, is
allowed at any time conditions require doing so to avoid an unsafe
condition.
4)
The owner or operator of containers using Container Level 1 controls
must inspect the containers and their covers and closure devices as
follows:
A)
In the case when a hazardous waste already is in the container at
the time the owner or operator first accepts possession of the
container at the facility and the container is not emptied within 24
hours after the container is accepted at the facility (i.e., it does not
meet the conditions for an empty container as specified in 35 Ill.
Adm. Code 721.107(b)), the owner or operator shall visually
inspect the container and its cover and closure devices to check
for visible cracks, holes, gaps, or other open spaces into the
interior of the container when the cover and closure devices are
secured in the closed position. The container visual inspection
must be conducted on or before the date on which the container is
accepted at the facility (i.e., the date when the container becomes
subject to the Subpart CC container standards). For the purposes
of this requirement, the date of acceptance is the date of signature
that the facility owner or operator enters on Item 20 of the
Uniform Hazardous Waste Manifest incorporated by reference in
35 Ill. Adm. Code 722.Appendix A (USEPA Forms 8700-22 and
8700-22A), as required under Section 725.171. If a defect is
detected, the owner or operator shall repair the defect in
accordance with the requirements of subsection (c)(4)(C) of this
Section.
B)
In the case when a container used for managing hazardous waste
249
remains at the facility for a period of one year or more, the owner
or operator shall visually inspect the container and its cover and
closure devices initially and thereafter, at least once every 12
months, to check for visible cracks, holes, gaps, or other open
spaces into the interior of the container when the cover and
closure devices are secured in the closed position. If a defect is
detected, the owner or operator shall repair the defect in
accordance with the requirements of subsection (c)(4)(C) of this
Section.
C)
When a defect is detected for in the container, cover, or closure
devices, the owner or operator shall make first efforts at repair of
the defect no later than 24 hours after detection, and repair must
be completed as soon as possible but no later than five calendar
days after detection. If repair of a defect cannot be completed
within five calendar days, then the hazardous waste must be
removed from the container and the container must not be used to
manage hazardous waste until the defect is repaired.
5)
The owner or operator shall maintain at the facility a copy of the
procedure used to determine that containers with capacity of 0.46 m
3
(120
gal) or greater, which do not meet applicable USDOT regulations as
specified in subsection (f) of this Section, are not managing hazardous
waste in light material service.
d)
Container Level 2 standards.
1)
A container using Container Level 2 controls is one of the following:
A)
A container that meets the applicable USDOT regulations on
packaging hazardous materials for transportation as specified in
subsection (f) of this Section.
B)
A container that operates with no detectable organic emissions, as
defined in Section 725.981, and determined in accordance with
the procedure specified in subsection (g) of this Section.
C)
A container that has been demonstrated within the preceding 12
months to be vapor-tight by using 40 CFR 60, appendix A,
Method 27, incorporated by reference in 35 Ill. Adm. Code
720.111, in accordance with the procedure specified in subsection
(h) of this Section.
2)
Transfer of hazardous waste in into or out of a container using Container
Level 2 controls must be conducted in such a manner as to minimize
250
exposure of the hazardous waste to the atmosphere, to the extent
practical, considering the physical properties of the hazardous waste and
good engineering and safety practices for handling flammable, ignitable,
explosive, reactive or other hazardous materials. Examples of container
loading procedures that the USEPA considers to meet the requirements of
this subsection (d)(2) include using any one of the following: a
submerged-fill pipe or other submerged-fill method to load liquids into the
container; a vapor-balancing system or a vapor-recovery system to collect
and control the vapors displaced from the container during filling
operations; or a fitted opening in the top of a container through which the
hazardous waste is filled and subsequently purging the transfer line before
removing it from the container opening.
3)
Whenever a hazardous waste is in a container using Container Level 2
controls, the owner or operator shall install all covers and closure devices
for the container, and secure and maintain each closure device in the
closed position, except as follows:
A)
Opening of a closure device or cover is allowed for the purpose
of adding hazardous waste or other material to the container as
follows:
i)
In the case when the container is filled to the intended final
level in one continuous operation, the owner or operator
shall promptly secure the closure devices in the closed
position and install the covers, as applicable to the
container, upon conclusion of the filling operation.
ii)
In the case when discrete quantities or batches of material
intermittently are added to the container over a period of
time, the owner or operator shall promptly secure the
closure devices in the closed position and install covers, as
applicable to the container, upon either the container being
filled to the intended final level; the completion of a batch
loading after which no additional material will be added to
the container within 15 minutes; the person performing the
loading operation leaving the immediate vicinity of the
container; or the shutdown of the process generating the
material being added to the container, whichever condition
occurs first.
B)
Opening of a closure device or cover is allowed for the purpose
of removing hazardous waste from the container as follows:
i)
For the purpose of meeting the requirements of this
251
Section, an empty container as defined in 35 Ill. Adm.
Code 721.107(b) may be open to the atmosphere at any
time (i.e., covers and closure devices are not required to
be secured in the closed position on an empty container).
ii)
In the case when discrete quantities or batches of material
are removed from the container but the container does not
meet the conditions to be an empty container as defined in
35 Ill. Adm. Code 721.107(b), the owner or operator shall
promptly secure the closure devices in the closed position
and install covers, as applicable to the container, upon the
completion of a batch removal after which no additional
material will be removed from the container within 15
minutes or the person performing the unloading operation
leaves the immediate vicinity of the container, whichever
condition occurs first.
C)
Opening of a closure device or cover is allowed when access
inside the container is needed to perform routine activities other
than transfer of hazardous waste. Examples of such activities
include those times when a worker needs to open a port to
measure the depth of or sample the material in the container, or
when a worker needs to open a manhole hatch to access
equipment inside the container. Following completion of the
activity, the owner or operator shall promptly secure the closure
device in the closed position or reinstall the cover, as applicable to
the container.
D)
Opening of a spring-loaded, pressure-vacuum relief valve,
conservation vent, or similar type of pressure relief device that
vents to the atmosphere is allowed during normal operations for
the purpose of maintaining the internal pressure of the container in
accordance with the container design specifications. The device
must be designed to operate with no detectable organic emission
when the device is secured in the closed position. The settings at
which the device opens must be established so that the device
remains in the closed position whenever the internal pressure of
the container is within the internal pressure operating range
determined by the owner or operator based on container
manufacturer recommendations, applicable regulations, fire
protection and prevention codes, standard engineering codes and
practices, or other requirements for the safe handling of
flammable, ignitable, explosive, reactive, or hazardous materials.
Examples of normal operating conditions that may require these
devices to open are during those times when the internal pressure
252
of the container exceeds the internal pressure operating range for
the container as a result of loading operations or diurnal ambient
temperature fluctuations.
E)
Opening of a safety device, as defined in Section 725.981, is
allowed at any time conditions require doing so to avoid an unsafe
condition.
4)
The owner or operator of containers using Container Level 2 controls
shall inspect the containers and their covers and closure devices as
follows:
A)
In the case when a hazardous waste already is in the container at
the time the owner or operator first accepts possession of the
container at the facility and the container is not emptied within 24
hours after the container is accepted at the facility (i.e., it does not
meet the conditions for an empty container as specified in 35 Ill.
Adm. Code 721.107(b)), the owner or operator shall visually
inspect the container and its cover and closure devices to check
for visible cracks, holes, gaps, or other open spaces into the
interior of the container when the cover and closure devices are
secured in the closed position. The container visual inspection
must be conducted on or before the date on which the container is
accepted at the facility (i.e., the date when the container becomes
subject to the Subpart CC container standards). For the purposes
of this requirement, the date of acceptance is the date of signature
that the facility owner or operator enters on Item 20 of the
Uniform Hazardous Waste Manifest incorporated by reference in
35 Ill. Adm. Code 722.Appendix A (USEPA Forms 8700-22 and
8700-22A), as required under Section 725.171. If a defect is
detected, the owner or operator shall repair the defect in
accordance with the requirements of subsection (d)(4)(C) of this
Section.
B)
In the case when a container used for managing hazardous waste
remains at the facility for a period of one year or more, the owner
or operator shall visually inspect the container and its cover and
closure devices initially and thereafter, at least once every 12
months, to check for visible cracks, holes, gaps, or other open
spaces into the interior of the container when the cover and
closure devices are secured in the closed position. If a defect is
detected, the owner or operator shall repair the defect in
accordance with the requirements of subsection (d)(4)(C) of this
Section.
253
C)
When a defect is detected for in the container, cover, or closure
devices, the owner or operator shall make first efforts at repair of
the defect no later than 24 hours after detection, and repair must
be completed as soon as possible but no later than five calendar
days after detection. If repair of a defect cannot be completed
within five calendar days, then the hazardous waste must be
removed from the container and the container must not be used to
manage hazardous waste until the defect is repaired.
e)
Container Level 3 standards.
1)
A container using Container Level 3 controls is one of the following:
A)
A container that is vented directly through a closed-vent system to
a control device in accordance with the requirements of subsection
(e)(2)(B) of this Section.
B)
A container that is vented inside an enclosure which is exhausted
through a closed-vent system to a control device in accordance
with the requirements of subsections (e)(2)(A) and (e)(2)(B) of this
Section.
2)
The owner or operator shall meet the following requirements, as
applicable to the type of air emission control equipment selected by the
owner or operator:
A)
The container enclosure must be designed and operated in
accordance with the criteria for a permanent total enclosure as
specified in “Procedure T—Criteria for and Verification of a
Permanent or Temporary Total Enclosure” under 40 CFR
52.741, appendix B, incorporated by reference in 35 Ill. Adm.
Code 720.111. The enclosure may have permanent or temporary
openings to allow worker access; passage of containers through
the enclosure by conveyor or other mechanical means; entry of
permanent mechanical or electrical equipment; or direct airflow
into the enclosure. The owner or operator shall perform the
verification procedure for the enclosure as specified in Section 5.0
to “Procedure T—Criteria for and Verification of a Permanent or
Temporary Total Enclosure” initially when the enclosure is first
installed and, thereafter, annually.
B)
The closed-vent system and control device must be designed and
operated in accordance with the requirements of Section 725.988.
3)
Safety devices, as defined in Section 725.981, may be installed and
254
operated as necessary on any container, enclosure, closed-vent system, or
control device used to comply with the requirements of subsection (e)(1)
of this Section.
4)
Owners and operators using Container Level 3 controls in accordance
with the provisions of this Subpart shall inspect and monitor the closed-
vent systems and control devices, as specified in Section 725.988.
5)
Owners and operators that use Container Level 3 controls in accordance
with the provisions of this Subpart shall prepare and maintain the records
specified in Section 725.990(d).
6)
The transfer of hazardous waste into or out of a container using
Container Level 3 controls must be conducted in such a manner as to
minimize exposure of the hazardous waste to the atmosphere, to the
extent practical considering the physical properties of the hazardous waste
and good engineering and safety practices for handling flammable,
ignitable, explosive, reactive, or other hazardous materials. Examples of
container loading procedures that USEPA considers to meet the
requirements of this subsection (e)(6) include using any one of the
following: the use of a submerged-fill pipe or other submerged-fill
method to load liquids into the container; the use of a vapor-balancing
system or a vapor-recovery system to collect and control the vapors
displaced from the container during filling operations; or the use of a
fitted opening in the top of a container through which the hazardous
waste is filled and subsequently purging the transfer line before removing
it from the container opening.
f)
For the purpose of compliance with subsection (c)(1)(A) or (d)(1)(A) of this
Section, containers must be used that meet the applicable USDOT regulations on
packaging hazardous materials for transportation as follows:
1)
The container meets the applicable requirements specified in 49 CFR 178,
“Specifications for Packaging”, or 49 CFR 179, “Specifications for Tank
Cars”, both incorporated by reference in 35 Ill. Adm. Code 720.111.
2)
Hazardous waste is managed in the container in accordance with the
applicable requirements specified in 49 CFR 107, subpart B,
“Exemptions”; 49 CFR 172, “Hazardous Materials Table, Special
Provisions, Hazardous Materials Communications, Emergency Response
Information, and Training Requirements”; 49 CFR 173, “Shippers—
General Requirements for Shipments and Packages”; and 49 CFR 180,
“Continuing Qualification and Maintenance of Packagings”, each
incorporated by reference in 35 Ill. Adm. Code 720.111.
255
3)
For the purpose of complying with this Subpart, no exceptions to the 49
CFR 178 or 179 regulations are allowed, except as provided for in
subsection (f)(4) of this Section.
4)
For a lab pack that is managed in accordance with the requirements of 49
CFR 178 for the purpose of complying with this Subpart, an owner or
operator may comply with the exceptions for combination packagings
specified in 49 CFR 173.12(b), incorporated by reference in 35 Ill. Adm.
Code 720.111.
g)
To determine compliance with the no detectable organic emissions requirements
of subsection (d)(1)(B) of this Section, the procedure specified in Section
725.984(d) must be used.
1)
Each potential leak interface (i.e., a location where organic vapor leakage
could occur) on the container, its cover, and associated closure devices,
as applicable to the container, must be checked. Potential leak interfaces
that are associated with containers include, but are not limited to: the
interface of the cover rim and the container wall; the periphery of any
opening on the container or container cover and its associated closure
device; and the sealing seat interface on a spring-loaded pressure-relief
valve.
2)
The test must be performed when the container is filled with a material
having a volatile organic concentration representative of the range of
volatile organic concentrations for the hazardous wastes expected to be
managed in this type of container. During the test, the container cover
and closure devices must be secured in the closed position.
h)
The procedure for determining a container to be vapor-tight using Method 27 of
40 CFR 60, appendix A for the purpose of complying with subsection (d)(1)(C)
of this Section is as follows:
1)
The test must be performed in accordance with Method 27 of 40 CFR
60, appendix A, incorporated by reference in 35 Ill. Adm. Code
720.111.
2)
A pressure measurement device must be used that has a precision of
±2.5 mm (0.10 inch) water and that is capable of measuring above the
pressure at which the container is to be tested for vapor tightness.
3)
If the test results determined by Method 27 indicate that the container
sustains a pressure change less than or equal to 750 Pascals (0.11 psig)
within five minutes after it is pressurized to a minimum of 4,500 Pascals
(0.65 psig), then the container is determined to be vapor-tight.
256
(Source: Amended at 24 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)
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)
257
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
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
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
726.Appendix C
Tier II Emission Rate Screening Limits for Free Chlorine and Hydrogen
Chloride
726.Appendix D
Reference Air Concentrations
258
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. ________, effective
______________________.
SUBPART H: HAZARDOUS WASTE BURNED IN BOILERS AND
INDUSTRIAL FURNACES
Section 726.200
Applicability
a)
The regulations of this Subpart apply to hazardous waste burned or processed in
a boiler or industrial furnace (BIF) (as defined in 35 Ill. Adm. Code 720.110)
irrespective of the purpose of burning or processing, except as provided by
subsections (b), (c), (d), and (f) of this Section. In this Subpart, the term “burn”
means burning for energy recovery or destruction or processing for materials
recovery or as an ingredient. The emissions standards of Sections 726.204,
726.205, 726.206, and 726.207 apply to facilities operating under interim status
or under a RCRA permit, as specified in Sections 726.202 and 726.203.
259
b) Integration of the MACT standards.
1) Except as provided by subsection (b)(2) of this Section, the standards of
this Part no longer apply when an affected source demonstrates
compliance with the maximum achievable control technology (MACT)
requirements of 40 CFR 63, subpart EEE, incorporated by reference in
35 Ill. Adm. Code 720.111, by conducting a comprehensive performance
test and submitting to the Agency a Notification of Compliance, under 40
CFR 63.1207(j) and 63.1210(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 following standards continue to apply:
A) The closure requirements of Sections 726.202(e)(11) and
726.203(l);
B) The standards for direct transfer of Section 726.211;
C) The standards for regulation of residues of Section 726.312; and
D) The applicable requirements of Subparts A through H, BB and
CC of 35 Ill. Adm. Code 724 and 725.
BOARD NOTE: Sections 9.1 and 39.5 of the Environmental Protection Act
[415 ILCS 5/9.1 and 39.5] make the federal MACT standards directly applicable
to entities in Illinois and authorize the Agency to issue permits based on the
federal standards. In adopting this subsection (b), USEPA stated as follows:
Under [the approach adopted by USEPA as a] final rule, MACT
air emissions and related operating requirements are to be
included in title V permits; RCRA permits will continue to be
required for all other aspects of the combustion unit and the
facility that are governed by RCRA (e.g., corrective action,
general facility standards, other combustor-specific concerns such
as materials handling, risk-based emissions limits and operating
requirements, as appropriate, and other hazardous waste
management units).
64 Fed Reg. 52828, 52975 (Sept. 30,1999).
bc)
The following hazardous wastes and facilities are not subject to regulation under
260
this Subpart:
1)
Used oil burned for energy recovery that is also a hazardous waste solely
because it exhibits a characteristic of hazardous waste identified in 35 Ill.
Adm. Code 721.Subpart C. Such used oil is subject to regulation under
35 Ill. Adm. Code 739, rather than this Subpart;
2)
Gas recovered from hazardous or solid waste landfills, when such gas is
burned for energy recovery;
3)
Hazardous wastes that are exempt from regulation under 35 Ill. Adm.
Code 721.104 and 721.106(a)(3)(C) and (a)(3)(D) and hazardous wastes
that are subject to the special requirements for conditionally exempt small
quantity generators under 35 Ill. Adm. Code 721.105; and
4)
Coke ovens, if the only hazardous waste burned is USEPA hazardous
waste no. K087 decanter tank tar sludge from coking operations.
cd)
Owners and operators of smelting, melting, and refining furnaces (including
pyrometallurgical devices such as cupolas, sintering machines, roasters, and
foundry furnaces, but not including cement kilns, aggregate kilns, or halogen
acid furnaces burning hazardous waste) that process hazardous waste solely for
metal recovery are conditionally exempt from regulation under this Subpart,
except for Sections 726.201 and 726.212.
1)
To be exempt from Sections 726.202 through 726.211, an owner or
operator of a metal recovery furnace or mercury recovery furnace shall
comply with the following requirements, except that an owner or
operator of a lead or a nickel-chromium recovery furnace or a metal
recovery furnace that burns baghouse bags used to capture metallic dust
emitted by steel manufacturing, shall comply with the requirements of
subsection (c)(3) (d)(3) of this Section, and an owner or operator of a
lead recovery furnace that is subject to regulation under the Secondary
Lead Smelting NESHAP of 40 CFR 63, subpart X shall comply with the
requirements of subsection (h) of this Section:
A)
Provide a one-time written notice to the Agency indicating the
following:
i)
The owner or operator claims exemption under this
subsection;
ii)
The hazardous waste is burned solely for metal recovery
consistent with the provisions of subsection (c)(2) of this
Section;
261
iii)
The hazardous waste contains recoverable levels of metals;
and
iv)
The owner or operator will comply with the sampling and
analysis and recordkeeping requirements of this subsection
(d);
B)
Sample and analyze the hazardous waste and other feedstocks as
necessary to comply with the requirements of this subsection (d)
under procedures specified by “Test Methods for Evaluating Solid
Waste, Physical/Chemical Methods,” SW-846, incorporated by
reference in 35 Ill. Adm. Code 720.111, or alternative methods
that meet or exceed the SW-846 method performance capabilities.
If SW-846 does not prescribe a method for a particular
determination, the owner or operator shall use the best available
method; and
C)
Maintain at the facility for at least three years records to document
compliance with the provisions of this subsection including limits
on levels of toxic organic constituents and Btu value of the waste,
and levels of recoverable metals in the hazardous waste compared
to normal non-hazardous waste feedstocks.
2)
A hazardous waste meeting either of the following criteria is not
processed solely for metal recovery:
A)
The hazardous waste has a total concentration of organic
compounds listed in 35 Ill. Adm. Code 721.Appendix H
exceeding 500 ppm by weight, as fired, and so is considered to be
burned for destruction. The concentration of organic compounds
in a waste as-generated may be reduced to the 500 ppm limit by
bona fide treatment that removes or destroys organic constituents.
Blending for dilution to meet the 500 ppm limit is prohibited, and
documentation that the waste has not been impermissibly diluted
must be retained in the records required by subsection (c)(1)(C) of
this Section; or
B)
The hazardous waste has a heating value of 5,000 Btu/lb or more,
as-fired, and is so considered to be burned as fuel. The heating
value of a waste as-generated may be reduced to below the 5,000
Btu/lb limit by bona fide treatment that removes or destroys
organic constituents. Blending for dilution to meet the 5,000
Btu/lb limit is prohibited and documentation that the waste has not
been impermissibly diluted must be retained in the records
262
required by subsection (c)(1)(C) of this Section.
3)
To be exempt from Sections 726.202 through 726.211, an owner or
operator of a lead, nickel-chromium, or mercury recovery furnace,
except for an owner or operator of a lead recovery furnace that is subject
to regulation under the Secondary Lead Smelting NESHAP of 40 CFR
63, subpart X, or a metal recovery furnace that burns baghouse bags
used to capture metallic dusts emitted by steel manufacturing shall provide
a one-time written notice to the Agency identifying each hazardous waste
burned and specifying whether the owner or operator claims an
exemption for each waste under this subsection (d) or subsection (c)(1) of
this Section. The owner or operator shall comply with the requirements
of subsection (c)(1) of this Section for those wastes claimed to be exempt
under that subsection and with the following requirements for those
wastes claimed to be exempt under this subsection (d):
A)
The hazardous wastes listed in .Appendices K, L, and M of this
Part and baghouse bags used to capture metallic dusts emitted by
steel manufacturing are exempt from the requirements of
subsection (c)(1) of this Section, provided that:
i)
A waste listed in Appendix K of this Part must contain
recoverable levels of lead;, a waste listed in Appendix L of
this Part must contain recoverable levels of nickel or
chromium, a waste listed in Appendix M of this Part must
contain recoverable levels of mercury and contain less than
500 ppm of 35 Ill. Adm. Code 261.Appendix H organic
constituents, and baghouse bags used to capture metallic
dusts emitted by steel manufacturing must contain
recoverable levels of metal;
ii)
The waste does not exhibit the Toxicity Characteristic
toxicity characteristic of 35 Ill. Adm. Code 721.124 for an
organic constituent;
iii)
The waste is not a hazardous waste listed in 35 Ill. Adm.
Code 721.Subpart D because it is listed for an organic
constituent, as identified in 35 Ill. Adm. Code
721.Appendix G; and
iv)
The owner or operator certifies in the one-time notice that
hazardous waste is burned under the provisions of
subsection (c)(3) of this Section and that sampling and
analysis will be conducted or other information will be
obtained as necessary to ensure continued compliance with
263
these requirements. Sampling and analysis must be
conducted according to subsection (c)(1)(B) of this Section,
and records to document compliance with subsection (c)(3)
of this Section must be kept for at least three years.
B)
The Agency may decide, on a case-by-case basis, that the toxic
organic constituents in a material listed in Appendix K, Appendix
L, or Appendix M of this Part that contains a total concentration
of more than 500 ppm toxic organic compounds listed in 35 Ill.
Adm. Code 721.Appendix H may pose a hazard to human health
and the environment when burned in a metal recovery furnace
exempt from the requirements of this Subpart. Under these
circumstances, after adequate notice and opportunity for comment,
the metal recovery furnace will become subject to the
requirements of this Subpart when burning that material. In
making the hazard determination, the Agency shall consider the
following factors:
i)
The concentration and toxicity of organic constituents in
the material;
ii)
The level of destruction of toxic organic constituents
provided by the furnace; and
iii)
Whether the acceptable ambient levels established in
Appendix D or E of this Part will be exceeded for any
toxic organic compound that may be emitted based on
dispersion modeling to predict the maximum annual
average off-site ground level concentration.
de)
The standards for direct transfer operations under Section 726.211 apply only to
facilities subject to the permit standards of Section 726.202 or the interim status
standards of Section 726.203.
ef)
The management standards for residues under Section 726.212 apply to any BIF
burning hazardous waste.
fg)
Owners and operators of smelting, melting, and refining furnaces (including
pyrometallurgical devices such as cupolas, sintering machines, roasters, and
foundry furnaces) that process hazardous waste for recovery of economically
significant amounts of the precious metals gold, silver, platinum, palladium,
iridium, osmium, rhodium, ruthenium, or any combination of these metals are
conditionally exempt from regulation under this Subpart, except for Section
726.212. To be exempt from Sections 726.202 through 726.211, an owner or
operator shall:
264
1)
Provide a one-time written notice to the Agency indicating the following:
A)
The owner or operator claims exemption under this Section,
B)
The hazardous waste is burned for legitimate recovery of precious
metal, and
C)
The owner or operator will comply with the sampling and analysis
and recordkeeping requirements of this Section;
2)
Sample and analyze the hazardous waste, as necessary, to document that
the waste is burned for recovery of economically significant amounts of
precious metal, using procedures specified by Test Methods for
Evaluating Solid Waste, Physical/Chemical Methods, SW-846,
incorporated by reference in 35 Ill. Adm. Code 720.111, or alternative
methods that meet or exceed the SW-846 method performance
capabilities. If SW-846 does not prescribe a method for a particular
determination, the owner or operator shall use the best available method;
and
3)
Maintain, at the facility for at least three years, records to document that
all hazardous wastes burned are burned for recovery of economically
significant amounts of precious metal.
h) An owner or operator of a lead recovery furnace that processes hazardous waste
for recovery of lead and which is subject to regulation under the Secondary Lead
Smelting NESHAP of 40 CFR 63, subpart X, is conditionally exempt from
regulation under this Subpart, except for Section 726.201. To become exempt,
an owner or operator shall provide a one-time notice to the Agency identifying
each hazardous waste burned and specifying that the owner or operator claims
an exemption under this subsection (h). The notice also must state that the waste
burned has a total concentration of non-metal compounds listed in 35 Ill. Adm.
Code 721.Appendix H of less than 500 ppm by weight, as fired and as provided
in subsection (d)(2)(A) of this Section, or is listed in Appendix K to this Part.
gi)
Abbreviations and definitions. The following definitions and abbreviations are
used in this Subpart:
“APCS” means air pollution control system.
“BIF” means boiler or industrial furnace.
“Carcinogenic metals” means arsenic, beryllium, cadmium, and
chromium.
265
“CO” means carbon monoxide.
“Continuous monitor” is a monitor that continuously samples the
regulated parameter without interruption, that evaluates the detector
response at least once each 15 seconds, and that computes and records
the average value at least every 60 seconds.
“DRE” means destruction or removal efficiency.
“cu m” or “m
3
” means cubic meters.
“E” means “ten to the power”. For example, “XE-Y” means “X times
ten to the -Y power”.
“Feed rates” are measured as specified in Section 726.202(e)(6).
“Good engineering practice stack height” is as defined by 40 CFR
51.100(ii), incorporated by reference in 35 Ill. Adm. Code 720.111.
“HC” means hydrocarbon.
“HCl” means hydrogen chloride gas.
“Hourly rolling average” means the arithmetic mean of the 60 most
recent one-minute average values recorded by the continuous monitoring
system.
“K” means Kelvin.
“kVA” means kilovolt amperes.
“MEI” means maximum exposed individual.
“MEI location” means the point with the maximum annual average off-
site (unless on-site is required) ground level concentration.
“Noncarcinogenic metals” means antimony, barium, lead, mercury,
thallium, and silver.
“One hour block average” means the arithmetic mean of the one minute
averages recorded during the 60-minute period beginning at one minute
after the beginning of preceding clock hour.
“PIC” means product of incomplete combustion.
266
“PM” means particulate matter.
“POHC” means principal organic hazardous constituent.
“ppmv” means parts per million by volume.
“QA/QC” means quality assurance and quality control.
“Rolling average for the selected averaging period” means the arithmetic
mean of one hour block averages for the averaging period.
“RAC” means reference air concentration, the acceptable ambient level
for the noncarcinogenic metals for purposes of this Subpart. RACs are
specified in Appendix D of this Part.
“RSD” means risk-specific dose, the acceptable ambient level for the
carcinogenic metals for purposes of this Subpart. RSDs are specified in
Appendix E of this Part.
“SSU” means “Saybolt Seconds Universal”, a unit of viscosity measured
by ASTM D 88-87 or D 2161-87, incorporated by reference in 35 Ill.
Adm. Code 720.111.
“TCLP test” means the toxicity characteristic leaching procedure of 35
Ill. Adm. Code 721.124.
“TESH” means terrain-adjusted effective stack height (in meters).
“Tier I”. See Section 726.206(b).
“Tier II”. See Section 726.206(c).
“Tier III”. See Section 726.206(d).
“Toxicity equivalence” is estimated, pursuant to Section 726.204(e),
using “Procedures for Estimating the Toxicity Equivalence of Chlorinated
Dibenzo-p-Dioxin and Dibenzofuran Congeners,” incorporated by
reference in Appendix I of this Part.
“mg” means microgram.
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
Section 726.201
Management prior to Burning
267
a)
Generators. Generators of hazardous waste that is burned in a BIF are subject to
35 Ill. Adm. Code 722.
b)
Transporters. Transporters of hazardous waste that is burned in a BIF are
subject to 35 Ill. Adm. Code 723.
c)
Storage and treatment facilities.
1)
Owners and operators of facilities An owner or operator of a facility that
store stores or treats hazardous waste that is burned in a BIF are is
subject to the applicable provisions of 35 Ill. Adm. Code 724.Subparts A
through L, 35 Ill. Adm. Code 725.Subparts A through L 724 and 725
and 35 Ill. Adm. Code 702 and 703, except as provided by subsection
(c)(2), below of this Section. These standards apply to storage and
treatment by the burner as well as to any storage or treatment facilities
facility operated by intermediaries an intermediary (processors, blenders,
distributorsa processor, blender, distributor, etc.) between the generator
and the burner.
2)
Owners and operators of facilities An owner or operator of a facility that
burn burns, in an on-site BIF exempt from regulation under the small
quantity burner provisions of Section 726.208, hazardous waste that they
generate are it generates is exempt from regulation under 35 Ill. Adm.
Code 724.Subparts A through L, 35 Ill. Adm. Code 725.Subparts A
through L 724 and 725 and 35 Ill. Adm. Code 702 and 703 applicable to
storage units for those storage units that store mixtures of hazardous
waste and the primary fuel to the BIF in tanks that feed the fuel mixture
directly to the burner. Storage of hazardous waste prior to mixing with
the primary fuel is subject to regulation as prescribed in subsection (c)(1),
above of this Section.
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
Section 726.205
Standards to control PM
a)
A BIF burning hazardous waste must not emit PM in excess of 180 mg/dry
standard cu m (0.08 grains/dry standard cubic foot) after correction to a stack
gas concentration of 7% oxygen, using procedures prescribed in 40 CFR 60,
Appendix A, methods 1 through 5, (incorporated by reference in 35 Ill. Adm.
Code 720.111), and incorporated by reference in Appendix I (“eye”) of this
Part.
b)
An owner or operator meeting the requirements of Section 726.209(b) for the
low risk waste exemption is exempt from the PM standard.
268
c) Oxygen correction.
1) Measured pollutant levels must be corrected for the amount of oxygen in
the stack gas according to the formula:
(
)
P
P
14
E - Y
c
m
=
×
Where:
P
c
is the corrected concentration of the pollutant in the stack
gas,
P
m
is the measured concentration of the pollutant in the stack
gas,
E is the oxygen concentration on a dry basis in the
combustion air fed to the device, and
Y is the measured oxygen concentration on a dry basis in the
stack.
2) For devices that feed normal combustion air, E will equal 21 percent. For
devices that feed oxygen-enriched air for combustion (that is, air with an
oxygen concentration exceeding 21 percent), the value of E will be the
concentration of oxygen in the enriched air.
3) Compliance with all emission standards provided by this Subpart must be
based on correcting to seven percent oxygen using this procedure.
cd)
For the purposes of permit enforcement, compliance with the operating
requirements specified in the permit (under Section 726.202) will be regarded as
compliance with this Section. However, evidence that compliance with those
permit conditions is insufficient to ensure compliance with the requirements of
this Section is “information” justifying modification or revocation and re-issuance
of a permit under 35 Ill. Adm. Code 703.270 et seq.
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
Section 726.212
Regulation of Residues
A residue derived from the burning or processing of hazardous waste in a BIF is not excluded
from the definition of a hazardous waste under 35 Ill. Adm. Code 721.104(b)(4), (b)(7), or
(b)(8) unless the device and the owner or operator meet the following requirements:
269
a)
The device meets the following criteria:
1)
Boilers. Boilers must burn at least 50% coal on a total heat input or mass
basis, whichever results in the greater mass feed rate of coal;
2)
Ore or mineral furnaces. Industrial furnaces subject to 35 Ill. Adm.
Code 721.104(b)(7) must process at least 50% by weight of normal,
nonhazardous raw materials;
3)
Cement kilns. Cement kilns must process at least 50% by weight of
normal cement-production raw materials;
b)
The owner or operator demonstrates that the hazardous waste does not
significantly affect the residue by demonstrating conformance with either of the
following criteria:
1)
Comparison of waste-derived residue with normal residue. The waste-
derived residue must not contain 35 Ill. Adm. Code 721.Appendix H
constituents (toxic constituents) that could reasonably be attributable to the
hazardous waste at concentrations significantly higher than in residue
generated without burning or processing of hazardous waste, using the
following procedure. Toxic compounds that could reasonably be
attributable to burning or processing the hazardous waste (constituents of
concern) include toxic constituents in the hazardous waste, and the
organic compounds listed in 35 Ill. Adm. Code 721.Appendix H that may
be PICs. Sampling and analyses must be in conformance with
procedures prescribed in “Test Methods for Evaluating Solid Waste,
Physical/Chemical Methods”, U.S. EPA USEPA Publication SW-846,
incorporated by reference in 35 Ill. Adm. Code 720.111(a). For
polychlorinated dibenzo-p-dioxins and polychlorinated dibenzo-furans
(D/F), analyses must be performed to determine specific congeners and
homologues, and the results converted to 2,3,7,8-TCDD equivalent
values using the procedure specified in section 4.0 of the documents
referenced in Appendix I of this Part.
A)
Normal residue. Concentrations of toxic constituents of concern
in normal residue must be determined based on analyses of a
minimum of 10 samples representing a minimum of 10 days of
operation. Composite samples may be used to develop a sample
for analysis provided that the compositing period does not exceed
24 hours. The upper tolerance limit (at 95% confidence with a
95% proportion of the sample distribution) of the concentration in
the normal residue shall be considered the statistically-derived
concentration in the normal residue. If changes in raw materials
or fuels reduce the statistically-derived concentrations of the toxic
270
constituents of concern in the normal residue, the statistically-
derived concentrations must be revised or statistically-derived
concentrations of toxic constituents in normal residue must be
established for a new mode of operation with the new raw
material or fuel. To determine the upper tolerance limit in the
normal residue, the owner or operator shall use statistical
procedures prescribed in “Statistical Methodology for Bevill
Residue Determinations,” incorporated by reference in Section
726.Appendix I of this Part.
B)
Waste-derived residue. Waste derived residue must be sampled
and analyzed as often as necessary to determine whether the
residue generated during each 24-hour period has concentrations
of toxic constituents that are higher than the concentrations
established for the normal residue under subsection (b)(1)(A)
above of this Section. If so, hazardous waste burning has
significantly affected the residue and the residue is not excluded
from the definition of “hazardous waste”. Concentrations of toxic
constituents in waste-derived residue must be determined based on
analysis of one or more samples obtained over a 24-hour period.
Multiple samples may be analyzed, and multiple samples may be
taken to form a composite sample for analysis provided that the
sampling period does not exceed 24 hours. If more than one
sample is analyzed to characterize waste-derived residues
generated over a 24-hour period, the concentration of each toxic
constituent must be the arithmetic mean of the concentrations in
the samples. No results can be disregarded; or
2)
Comparison of waste-derived residue concentrations with health-based
limits.
A)
Nonmetal constituents. The concentration of each nonmetal toxic
constituent of concern (specified in subsection (b)(1) above of this
Section) in the waste-derived residue must not exceed the health-
based level specified in Section 726.Appendix G of this Part, or
the level of detection (using analytical procedures prescribed in
“Test Methods for Evaluating Solid Waste, Physical/Chemical
Methods”, U.S. EPA USEPA Publication SW-846, incorporated
by reference in 35 Ill. Adm. Code 720.111), whichever is higher.
If a health-based limit for a constituent of concern is not listed in
Section 726.Appendix G of this Part, then a limit of 0.002 mg/kg
or the level of detection (using analytical procedures prescribed in
“Test Methods for Evaluating Solid Waste, Physical/Chemical
Methods”, U.S. EPA USEPA Publication SW-846, incorporated
by reference in 35 Ill. Adm. Code 720.111), whichever is higher,
271
must be used. The levels specified in Section 726.Appendix G of
this Part (and the default level of 0.002 mg/kg or the level of
detection for constituents, as identified in Note 1 of Section
726.Appendix G of this Part) are administratively stayed under the
condition, for those constituents specified in subsection (b)(1)
above of this Section, that the owner or operator complies with
alternative levels defined as the land disposal restriction limits
specified in 35 Ill. Adm. Code 728.143 and 728.Table B for F039
nonwastewaters. In complying with those alternative levels, if an
owner or operator is unable to detect a constituent despite
documenting use of the best good-faith efforts, as defined by
applicable U.S. EPA USEPA guidance and standards, the owner
or operator is deemed to be in compliance for that constituent.
Until U.S. EPA USEPA develops new guidance or standards, the
owner or operator may demonstrate such good-faith efforts by
achieving a detection limit for the constituent that does not exceed
an order of magnitude above (ten times) the level provided by 35
Ill. Adm. Code 728.143 and 728.Table B for F039
nonwastewaters nonwastewater levels for polychlorinated dibenzo-
p-dioxins and polychlorinated dibenzo-furans (D/F), analyses must
be performed for total hexachlorodibenzo-p-dioxins, total
hexachlorodibenzofurans, total pentachlorodibenzo-p-dioxins, total
pentachlorodibenzofurans, total tetrachlorodibenzo-p-dioxins, and
total tetrachlorodibenzofurans;. The stay will remain in effect
until further rulemaking action is taken; and
BOARD NOTE: In a note to corresponding 40 CFR
266.112(b)(2)(i) (1999), as amended at 64 Fed. Reg. 53076 (Sept.
30, 1999), USEPA stated as follows:
The administrative stay, under the condition that the
owner or operator complies with alternative levels
defined as the land disposal restriction limits
specified in 35 Ill. Adm. Code 728.143 for F039
nonwastewaters, remains in effect until further
administrative action is taken and notice is
published in the Federal Register and the Code of
Federal Regulations.
Under Section 3006(b) and (g) of RCRA, 42 USC 6926(b) and
(g), federal amendments do not go into effect in Illinois until the
State of Illinois incorporates them into the State program. This
applies unless the authority under which USEPA adopted the
amendments is the Hazardous and Solid Waste Amendments of
1984 (HSWA), in which case the federal amendments become
272
effective in Illinois on their federal effective date.
B)
Metal constituents. The concentration of metals in an extract
obtained using the TCLP test must not exceed the levels specified
in Section 726.Appendix G of this Part; and
C)
Sampling and analysis. Wastewater-derived residue must be
sampled and analyzed as often as necessary to determine whether
the residue generated during each 24 hour 24-hour period has
concentrations of toxic constituents that are higher than the health-
based levels. Concentrations of concern in the wastewater-
derived residue must be determined based on analysis of one or
more samples obtained over a 24-hour period. Multiple samples
may be analyzed, and multiple samples may be taken to form a
composite for analysis provided that the sampling period does not
exceed 24 hours. If more than one sample is analyzed to
characterize waste-derived residues generated over a 24 hour 24-
hour period, the concentration of each toxic constituent is the
arithmetic mean of the concentrations of the samples. No results
can be disregarded; and
c)
Records sufficient to document compliance with the provisions of this Section
must be retained until closure of the BIF unit. At a minimum, the following must
be recorded:
1)
Levels of constituents in 35 Ill. Adm. Code 721.Appendix H that are
present in waste-derived residues;
2)
If the waste-derived residue is compared with normal residue under
subsection (b)(1) above of this Section:
A)
The levels of constituents in 35 Ill. Adm. Code 721.Appendix H
that are present in normal residues; and
B)
Data and information, including analyses of samples as necessary,
obtained to determine if changes in raw materials or fuels would
reduce the concentration of toxic constituents of concern in the
normal residue.
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
Section 726.Appendix H
Potential PICs for Determination of Exclusion of Waste-Derived
Residues
273
PICs Found in Stack Effluents
Volatiles
Semivolatiles
Benzene
Bis(2-ethylhexyl)phthalate
Toluene
Naphthalene
Carbon tetrachloride
Phenol
Chloroform
Diethyl phthalate
Methylene chloride
Butyl benzyl phthalate
Trichloroethylene
2,4-Dimethylphenol
Tetrachloroethylene
o-Dichlorobenzene
1,1,1-Trichloroethane
m-Dichlorobenzene
Chlorobenzene
p-Dichlorobenzene
cis-1,4-Dichloro-2-butene
Hexachlorobenzene
Bromochloromethane
2,4,6-Trichlorophenol
Bromodichloromethane
Fluoranthene
Bromoform
o-Nitrophenol
Bromomethane
1,2,4-Trichlorobenzene
Methylene bromide
o-Chlorophenol
Methyl ethyl ketone
Pentachlorophenol
Pyrene
Dimethyl phthalate
Mononitrobenzene
2,4-Toluene diisocyanate
Polycholorinated dibenzo-p-dioxins
1
Polycholorinated dibenzo-furans
1
1
Analyses for polychlorinated dibenzo-p-dioxins and polychlorinated dibenzo-furans are
required only for residues collected from areas downstream of the combustion chamber (e.g.,
ductwork, boiler tubes, heat exchange surfaces, air pollution control devices, etc.).
BOARD NOTE: Analysis is not required for those compounds that do not have an established
F039 nonwastewater concentration limit.
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
TITLE 35: ENVIRONMENTAL PROTECTION
SUBTITLE G: WASTE DISPOSAL
CHAPTER I: POLLUTION CONTROL BOARD
SUBCHAPTER c: HAZARDOUS WASTE OPERATING REQUIREMENTS
PART 728
LAND DISPOSAL RESTRICTIONS
274
SUBPART A: GENERAL
Section
728.101
Purpose, Scope, and Applicability
728.102
Definitions
728.103
Dilution Prohibited as a Substitute for Treatment
728.104
Treatment Surface Impoundment Exemption
728.105
Procedures for case-by-case Extensions to an Effective Date
728.106
Petitions to Allow Land Disposal of a Waste Prohibited under Subpart C
728.107
Testing, Tracking, and Recordkeeping Requirements for Generators, Treaters,
and Disposal Facilities
728.108
Landfill and Surface Impoundment Disposal Restrictions (Repealed)
728.109
Special Rules for Characteristic Wastes
SUBPART B: SCHEDULE FOR LAND DISPOSAL PROHIBITION AND
ESTABLISHMENT OF TREATMENT STANDARDS
Section
728.110
First Third (Repealed)
728.111
Second Third (Repealed)
728.112
Third Third (Repealed)
728.113
Newly Listed Wastes
728.114
Surface Impoundment exemptions
SUBPART C: PROHIBITION ON LAND DISPOSAL
Section
728.130
Waste Specific Prohibitions -- Wood Preserving Wastes
728.131
Waste Specific Prohibitions -- Dioxin-Containing Wastes
728.132
Waste Specific Prohibitions -- California List Wastes (Repealed)
728.133
Waste-Specific Prohibitions -- Organobromine Wastes (Repealed)
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)
728.137
Waste Specific Prohibitions -- Ignitable and Corrosive Characteristic Wastes
Whose Treatment Standards Were Vacated
728.138
Waste-Specific Prohibitions: Newly-Identified Organic Toxicity Characteristic
Wastes and Newly-Listed Coke By-Product and Chlorotoluene Production
Wastes
728.139
Waste-Specific Prohibitions: Spent Aluminum Potliners and Carbamate Wastes
SUBPART D: TREATMENT STANDARDS
Section
728.140
Applicability of Treatment Standards
728.141
Treatment Standards Expressed as Concentrations in Waste Extract
728.142
Treatment Standards Expressed as Specified Technologies
728.143
Treatment Standards Expressed as Waste Concentrations
728.144
Adjustment of Treatment Standard
275
728.145
Treatment Standards for Hazardous Debris
728.146
Alternative Treatment Standards Based on HTMR
728.148
Universal Treatment Standards
728.149
Alternative LDR Treatment Standards for Contaminated Soil
SUBPART E: PROHIBITIONS ON STORAGE
Section
728.150
Prohibitions on Storage of Restricted Wastes
728.Appendix A
Toxicity Characteristic Leaching Procedure (TCLP) (Repealed)
728.Appendix B
Treatment Standards (As concentrations in the Treatment Residual
Extract) (Repealed)
728.Appendix C
List of Halogenated Organic Compounds (Repealed)
728.Appendix D
Wastes Excluded from Lab Packs
728.Appendix E
Organic Lab Packs (Repealed)
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.Appendix K
Metal Bearing Wastes Prohibited From Dilution in a Combustion Unit
According to Section 728.103(c)
728.Table A
Constituent Concentrations in Waste Extract (CCWE)
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 E
Standards for Radioactive Mixed Waste
728.Table F
Alternative Treatment Standards for Hazardous Debris
728.Table G
Alternative Treatment Standards Based on HMTR HTMR
728.Table H
Wastes Excluded from CCW Treatment Standards
728.Table I
Generator Paperwork Requirements
728.Table T
Treatment Standards for Hazardous Wastes
728.Table U
Universal Treatment Standards (UTS)
AUTHORITY: Implementing Sections 7.2 and 22.4 and authorized by Section 27 of the
Environmental Protection Act [415 ILCS 5/7.2, 22.4 and 27].
SOURCE: Adopted in R87-5 at 11 Ill. Reg. 19354, effective November 12, 1987; amended in
R87-39 at 12 Ill. Reg. 13046, effective July 29, 1988; amended in R89-1 at 13 Ill. Reg. 18403,
effective November 13, 1989; amended in R89-9 at 14 Ill. Reg. 6232, effective April 16, 1990;
amended in R90-2 at 14 Ill. Reg. 14470, effective August 22, 1990; amended in R90-10 at 14
Ill. Reg. 16508, effective September 25, 1990; amended in R90-11 at 15 Ill. Reg. 9462,
effective June 17, 1991; amended 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,
276
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.
________, effective ______________________.
SUBPART A: GENERAL
Section 728.101
Purpose, Scope, and Applicability
a)
This Part identifies hazardous wastes that are restricted from land disposal and
defines those limited circumstances under which an otherwise prohibited waste
may continue to be land disposed.
b)
Except as specifically provided otherwise in this Part or 35 Ill. Adm. Code 721,
the requirements of this Part apply to persons that generate or transport
hazardous waste and to owners and operators of hazardous waste treatment,
storage, and disposal facilities.
c)
Restricted wastes may continue to be land disposed as follows:
1)
Where persons have been granted an extension to the effective date of a
prohibition under Subpart C or pursuant to Section 728.105, with respect
to those wastes covered by the extension;
2)
Where persons have been granted an exemption from a prohibition
pursuant to a petition under Section 728.106, with respect to those wastes
and units covered by the petition;
3)
A waste that is hazardous only because it exhibits a characteristic of
hazardous waste and that is otherwise prohibited under this Part is not
prohibited if the waste:
A)
Is disposed into a nonhazardous or hazardous waste injection well,
as defined in 35 Ill. Adm. Code 704.106(a); and
B)
Does not exhibit any prohibited characteristic of hazardous waste
identified in 35 Ill. Adm. Code 721.Subpart C at the point of
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injection.
4)
A waste that is hazardous only because it exhibits a characteristic of
hazardous waste and which is otherwise prohibited under this Part is not
prohibited if the waste meets any of the following criteria, unless the
waste is subject to a specified method of treatment other than DEACT in
Section 728.140 or is D003 reactive cyanide:
A)
Any of the following is true of either treatment or management of
the waste:
i)
The waste is managed in a treatment system which
subsequently discharges to waters of the U.S. United
States pursuant to a permit issued under 35 Ill. Adm. Code
309;
ii)
The waste is treated for purposes of the pretreatment
requirements of 35 Ill. Adm. Code 307 and 310; or
iii)
The waste is managed in a zero discharge system engaged
in Clean Water Act (CWA)-equivalent treatment, as
defined in Section 728.137(a); and
B)
The waste no longer exhibits a prohibited characteristic of
hazardous waste at the point of land disposal (i.e., placement in a
surface impoundment).
d)
This Part does not affect the availability of a waiver under Section 121(d)(4) of
the Comprehensive Environmental Response, Compensation, and Liability Act of
1980 (CERCLA) (42 U.S.C. USC §§ 9601 et seq.).
e)
The following hazardous wastes are not subject to any provision of this Part:
1)
Waste generated by small quantity generators of less than 100 kg of non-
acute hazardous waste or less than 1 kg of acute hazardous waste per
month, as defined in 35 Ill. Adm. Code 721.105;
2)
Waste pesticide that a farmer disposes of pursuant to 35 Ill. Adm. Code
722.170;
3)
Waste identified or listed as hazardous after November 8, 1984, for
which USEPA has not promulgated a land disposal prohibition or
treatment standard; or
4)
De minimis losses of waste that exhibits a characteristic of hazardous
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waste to wastewaters are not considered to be prohibited waste and are
defined as losses from normal material handling operations (e.g., spills
from the unloading or transfer of materials from bins or other containers
or leaks from pipes, valves, or other devices used to transfer materials);
minor leaks of process equipment, storage tanks, or containers; leaks
from well-maintained pump packings and seals; sample purgings; relief
device discharges; discharges from safety showers and rinsing and
cleaning of personal safety equipment; rinsate from empty containers or
from containers that are rendered empty by that rinsing; and laboratory
waste that does not exceed one percent of the total flow of wastewater
into the facility’s headworks on an annual basis, or with a combined
annualized average concentration not exceeding one part per million
(ppm) in the headworks of the facility’s wastewater treatment or
pretreatment facility.; or
5)
Land disposal prohibitions for hazardous characteristic wastes do not
apply to laboratory wastes displaying the characteristic of ignitability
(D001), corrosivity (D002), or organic toxicity (D012 through D043) that
are mixed with other plant wastewaters at facilities whose ultimate
discharge is subject to regulation under the CWA (including wastewaters
at facilities that have eliminated the discharge of wastewater), provided
that the annualized flow of laboratory wastewater into the facility’s
headworks does not exceed one percent or that the laboratory wastes’
combined annualized average concentration does not exceed one part per
million in the facility’s headworks.
f)
A universal waste handler or universal waste transporter (as defined in 35 Ill.
Adm. Code 720.110) is exempt from Sections 728.107 and 728.150 for the
hazardous wastes listed below. Such a handler or transporter is subject to
regulation under 35 Ill. Adm. Code 733.
1)
Batteries, as described in 35 Ill. Adm. Code 733.102;
2)
Pesticides, as described in 35 Ill. Adm. Code 733.103;
3)
Thermostats, as described in 35 Ill. Adm. Code 733.104; and
4)
Mercury-containing lampsLamps, as described in 35 Ill. Adm. Code
733.107 733.105.
BOARD NOTE: Subsection (f)(4) of this Section was added pursuant to
Section 22.23a of the Act [415 ILCS 5/22.23a] (see P.A. 90-502,
effective August 19, 1997).
g)
This Part is cumulative with the land disposal restrictions of 35 Ill. Adm. Code
279
729. The Environmental Protection Agency (Agency) shall not issue a
wastestream authorization pursuant to 35 Ill. Adm. Code 709 or Section 22.6 or
39(h) of the Environmental Protection Act [415 ILCS 5/22.6 or 39(h)] unless the
waste meets the requirements of this Part as well as 35 Ill. Adm. Code 729.
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
Section 728.102
Definitions
When used in this Part, the following terms have the meanings given below. All other terms
have the meanings given under 35 Ill. Adm. Code 702.110, 720.110, or 721.102 through
721.104.
“Agency” means the Illinois Environmental Protection Agency.
“Board” means the Illinois Pollution Control Board.
“CERCLA” means the Comprehensive Environmental Response, Compensation,
and Liability Act of 1980 (42 USC 9601 et seq.)
“Debris” means solid material exceeding a 60 mm particle size that is intended
for disposal and that is: a manufactured object; plant or animal matter; or natural
geologic material. However, the following materials are not debris: any
material for which a specific treatment standard is provided in Subpart D of this
Part, namely lead acid batteries, cadmium batteries, and radioactive lead solids;
process residuals, such as smelter slag and residues from the treatment of waste,
wastewater, sludges, or air emission residues; and intact containers of hazardous
waste that are not ruptured and that retain at least 75 percent of their original
volume. A mixture of debris that has not been treated to the standards provided
by Section 728.145 of this Part and other material is subject to regulation as
debris if the mixture is comprised primarily of debris, by volume, based on
visual inspection.
“End-of-pipe” refers to the point where effluent is discharged to the
environment.
“Halogenated organic compounds” or “HOCs” means those compounds having
a carbon-halogen bond that are listed under Appendix C of this Part.
“Hazardous constituent or constituents” means those constituents listed in 35 Ill.
Adm. Code 721.Appendix H.
“Hazardous debris” means debris that contains a hazardous waste listed in 35 Ill.
Adm. Code 721.Subpart D or that exhibits a characteristic of hazardous waste
identified in 35 Ill. Adm. Code 721.Subpart C. Any deliberate mixing of
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prohibited waste with debris that changes its treatment classification (i.e., from
waste to hazardous debris) is not allowed under the dilution prohibition in
Section 728.103.
“Inorganic metal-bearing waste” is one for which USEPA has established
treatment standards for metal hazardous constituents that does not otherwise
contain significant organic or cyanide content, as described in Section
728.103(b)(1), and which is specifically listed in Appendix K of this Part.
“Land disposal” means placement in or on the land, except in a corrective action
management unit or staging pile, and “land disposal” includes, but is not limited
to, placement in a landfill, surface impoundment, waste pile, injection well, land
treatment facility, salt dome formation, salt bed formation, underground mine or
cave, or placement in a concrete vault or bunker intended for disposal purposes.
“Nonwastewaters” are wastes that do not meet the criteria for “wastewaters” in
this Section.
“Polychlorinated biphenyls” or “PCBs” are halogenated organic compounds
defined in accordance with 40 CFR 761.3, incorporated by reference in 35 Ill.
Adm. Code 720.111.
“ppm” means parts per million.
“RCRA corrective action” means corrective action taken under 35 Ill. Adm.
Code 724.200 or 725.193, 40 CFR 264.100 or 265.93 (1996), or similar
regulations in other States states with RCRA programs authorized by USEPA
pursuant to 40 CFR 271 (1996).
“Soil” means unconsolidated earth material composing the superficial geologic
strata (material overlying bedrock), consisting of clay, silt, sand, or gravel size
particles, as classified by the U.S. United States Natural Resources Conservation
Service, or a mixture of such materials with liquids, sludges, or solids that is
inseparable by simple mechanical removal processes and which is made up
primarily of soil by volume based on visual inspection. Any deliberate mixing of
prohibited waste with debris that changes its treatment classification (i.e., from
waste to hazardous debris) is not allowed under the dilution prohibition in
Section 728.103.
“Stormwater impoundments” are surface impoundments that receive wet weather
flow and which receive process waste only during wet weather events.
“Underlying hazardous constituent” means any constituent listed in Table U of
this Part, “Universal Treatment Standards (UTS)”, except fluoride, selenium,
sulfides, vanadium, and zinc, that can reasonably be expected to be present at the
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point of generation of the hazardous waste at a concentration above the
constituent-specific UTS treatment standard.
“USEPA” or “U.S. EPA” means the United States Environmental Protection
Agency.
“Wastewaters” are wastes that contain less than 1 percent by weight total organic
carbon (TOC) and less than 1 percent by weight total suspended solids (TSS).
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
Section 728.107
Testing, Tracking, and Recordkeeping Requirements for Generators,
Treaters, and Disposal Facilities
a)
Requirements for generators:
1)
A generator of a hazardous waste shall determine if the waste has to be
treated before it can be land disposed. This is done by determining if the
hazardous waste meets the treatment standards in Section 728.140,
728.145, or 728.149. This determination can be made in either of two
ways: testing the waste or using knowledge of the waste. If the
generator tests the waste, testing determines the total concentration of
hazardous constituents or the concentration of hazardous constituents in
an extract of the waste obtained using SW-846 Method 1311 (the Toxicity
Characteristic Leaching Procedure), incorporated by reference in 35 Ill.
Adm. Code 720.111, depending on whether the treatment standard for
the waste is expressed as a total concentration or concentration of
hazardous constituent in the waste extract. In addition, some hazardous
wastes must be treated by particular treatment methods before they can be
land disposed and some soils are contaminated by such hazardous
wastes. These treatment standards are also found in Section 728.140 and
Table T of this Part, and are described in detail in Table C of this Part.
These wastes and soils contaminated with such wastes do not need to be
tested (however, if they are in a waste mixture, other wastes with
concentration level treatment standards must be tested). If a generator
determines that it is managing a waste or soil contaminated with a waste
that displays a hazardous characteristic of ignitability, corrosivity,
reactivity, or toxicity, the generator shall comply with the special
requirements of Section 728.109 in addition to any applicable
requirements in this Section.
2)
If the waste or contaminated soil does not meet the treatment standard, the
generator shall send a one-time written notice to each treatment or storage
facility receiving the waste with the initial shipment of waste to each
treatment or storage facility, and the generator shall place a copy of the
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one-time notice in the file. The notice must include the information in
column “728.107(a)(2)” of the Generator Paperwork Requirements Table
in Table I of this Part. No further notification is necessary until such time
that the waste or facility changes, in which case a new notification must
be sent and a copy placed in the generator’s file.
A)
For contaminated soil, the following certification statement should
be included, signed by an authorized representative:
I certify under penalty of law that I personally have
examined this contaminated soil and it (does/does not)
contain listed hazardous waste and (does/does not) exhibit
a characteristic of hazardous waste and requires treatment
to meet the soil treatment standards as provided by 35 Ill.
Adm. Code 728.149(c).
B)
This subsection (a)(2)(B) corresponds with 40 CFR 268.7(a)(2)(ii),
which is marked “reserved” by USEPA. This statement
maintains structural consistency with USEPA rules.
3)
If the waste or contaminated soil meets the treatment standard at the
original point of generation:
A)
With the initial shipment of waste to each treatment, storage, or
disposal facility, the generator shall send a one-time written notice
to each treatment, storage, or disposal facility receiving the waste,
and place a copy in its own file. The notice must include the
information indicated in column “728.107(a)(3)” of the Generator
Paperwork Requirements Table in Table I of this Part and the
following certification statement, signed by an authorized
representative:
I certify under penalty of law that I personally have
examined and am familiar with the waste through analysis
and testing or through knowledge of the waste to support
this certification that the waste complies with the treatment
standards specified in 35 Ill. Adm. Code 728.Subpart D. I
believe that the information I submitted is true, accurate,
and complete. I am aware that there are significant
penalties for submitting a false certification, including the
possibility of a fine and imprisonment.
B)
For contaminated soil, with the initial shipment of wastes to each
treatment, storage, or disposal facility, the generator must send a
one-time written notice to each facility receiving the waste and
283
place a copy in the file. The notice must include the information
in the column headed “(a)(3)” in Table I of this Part.
C) If the waste changes, the generator shall send a new notice and
certification to the receiving facility and place a copy in its files.
A generator of hazardous debris excluded from the definition of
hazardous waste under 35 Ill. Adm. Code 721.103(f) is not
subject to these requirements.
4)
For reporting, tracking and recordkeeping when exceptions allow certain
wastes or contaminated soil that do not meet the treatment standards to be
land disposed, there are certain exemptions from the requirement that
hazardous wastes or contaminated soil meet treatment standards before
they can be land disposed. These include, but are not limited to, case-by-
case extensions under Section 728.105, disposal in a no-migration unit
under Section 728.106, or a national capacity variance or case-by-case
capacity variance under Subpart C of this Part. If a generator’s waste is
so exempt, then with the initial shipment of waste, the generator shall
send a one-time written notice to each land disposal facility receiving the
waste. The notice must include the information indicated in column
“728.107(a)(4)” of the Generator Paperwork Requirements Table in
Table I of this Part. If the waste changes, the generator shall send a new
notice to the receiving facility, and place a copy in its file.
5)
If a generator is managing and treating prohibited waste or contaminated
soil in tanks, containers, or containment buildings regulated under 35 Ill.
Adm. Code 722.134 to meet applicable LDR treatment standards found at
Section 728.140, the generator shall develop and follow a written waste
analysis plan that describes the procedures it will carry out to comply
with the treatment standards. (Generators treating hazardous debris
under the alternative treatment standards of Table F of this Part,
however, are not subject to these waste analysis requirements.) The plan
must be kept on site in the generator’s records, and the following
requirements must be met:
A)
The waste analysis plan must be based on a detailed chemical and
physical analysis of a representative sample of the prohibited
wastes being treated, and contain all information necessary to treat
the wastes in accordance with the requirements of this Part,
including the selected testing frequency;
B)
Such plan must be kept in the facility’s on-site files and made
available to inspectors; and
C)
Wastes shipped off-site pursuant to this subsection (a)(5) of this
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Section must comply with the notification requirements of
subsection (a)(3) of this Section.
6)
If a generator determines that the waste or contaminated soil is restricted
based solely on its knowledge of the waste, all supporting data used to
make this determination must be retained on-site in the generator’s files.
If a generator determines that the waste is restricted based on testing this
waste or an extract developed using SW-846 Method 1311 (the Toxicity
Characteristic Leaching Procedure), incorporated by reference in 35 Ill.
Adm. Code 720.111, and all waste analysis data must be retained on-site
in the generator’s files.
7)
If a generator determines that it is managing a prohibited waste which is
excluded from the definition of hazardous or solid waste or which is
exempt from Subtitle C regulation under 35 Ill. Adm. Code 721.102
through 721.106 subsequent to the point of generation (including
deactivated characteristic hazardous wastes that are managed in
wastewater treatment systems subject to the CWA, as specified at 35 Ill.
Adm. Code 721.104(a)(2); that are CWA-equivalent; or that are managed
in an underground injection well regulated under 35 Ill. Adm. Code
730), the generator shall place a one-time notice stating such generation,
subsequent exclusion from the definition of hazardous or solid waste or
exemption from RCRA Subtitle C regulation, and the disposition of the
waste in the generating facility’s on-site file.
8)
A generator shall retain a copy of all notices, certifications, waste analysis
data, and other documentation produced pursuant to this Section on-site
for at least three years from the date that the waste that is the subject of
such documentation was last sent to on-site or off-site treatment, storage,
or disposal. The three year record retention period is automatically
extended during the course of any unresolved enforcement action
regarding the regulated activity or as requested by the Agency. The
requirements of this subsection (a)(8) apply to solid wastes even when the
hazardous characteristic is removed prior to disposal, or when the waste
is excluded from the definition of hazardous or solid waste under 35 Ill.
Adm. Code 721.102 through 721.106, or exempted from RCRA Subtitle
C regulation, subsequent to the point of generation.
9)
If a generator is managing a lab pack containing hazardous wastes and
wishes to use the alternative treatment standard for lab packs found at
Section 728.142(c), the generator shall fulfill the following conditions:
A)
With the initial shipment of waste to a treatment facility, the
generator shall submit a notice that provides the information in
column “Section 728.107(a)(9)” in the Generator Paperwork
285
Requirements Table of Table I of this Part and the following
certification. The certification, which must be signed by an
authorized representative and must be placed in the generator’s
files, must say the following:
I certify under penalty of law that I personally have
examined and am familiar with the waste and that the lab
pack contains only wastes that have not been excluded
under 35 Ill. Adm. Code 728.Appendix D and that this lab
pack will be sent to a combustion facility in compliance
with the alternative treatment standards for lab packs at 35
Ill. Adm. Code 728.142(c). I am aware that there are
significant penalties for submitting a false certification,
including the possibility of fine or imprisonment.
B)
No further notification is necessary until such time as the wastes in
the lab pack change, or the receiving facility changes, in which
case a new notice and certification must be sent and a copy placed
in the generator’s file.
C)
If the lab pack contains characteristic hazardous wastes (D001-
D043), underlying hazardous constituents (as defined in Section
728.102(i)) need not be determined.
D)
The generator shall also comply with the requirements in
subsections (a)(6) and (a)(7) of this Section.
10)
Small quantity generators with tolling agreements pursuant to 35 Ill.
Adm. Code 722.120(e) shall comply with the applicable notification and
certification requirements of subsection (a) of this Section for the initial
shipment of the waste subject to the agreement. Such generators shall
retain on-site a copy of the notification and certification, together with the
tolling agreement, for at least three years after termination or expiration
of the agreement. The three-year record retention period is automatically
extended during the course of any unresolved enforcement action
regarding the regulated activity or as requested by the Agency.
b)
The owner or operator of a treatment facility shall test its wastes according to the
frequency specified in its waste analysis plan, as required by 35 Ill. Adm. Code
724.113 (for permitted TSDs) or 725.113 (for interim status facilities). Such
testing must be performed as provided in subsections (b)(1), (b)(2), and (b)(3) of
this Section.
1)
For wastes or contaminated soil with treatment standards expressed in the
waste extract (TCLP), the owner or operator of the treatment facility shall
286
test an extract of the treatment residues using SW-846 Method 1311 (the
Toxicity Characteristic Leaching Procedure), incorporated by reference in
35 Ill. Adm. Code 720.111, to assure that the treatment residues extract
meets the applicable treatment standards.
2)
For wastes or contaminated soil with treatment standards expressed as
concentrations in the waste, the owner or operator of the treatment
facility shall test the treatment residues (not an extract of such residues) to
assure that the treatment residues meet the applicable treatment standards.
3)
A one-time notice must be sent with the initial shipment of waste or
contaminated soil to the land disposal facility. A copy of the notice must
be placed in the treatment facility’s file.
A)
No further notification is necessary until such time that the waste
or receiving facility changes, in which case a new notice must be
sent and a copy placed in the treatment facility’s file.
B)
The one-time notice must include the requirements indicated in the
following table:
Treatment Facility Paperwork Requirements Table
Required information
Section
728.107(b)
1. USEPA hazardous waste number and
manifest number of first shipment.
ü
2. The waste is subject to the LDRs. The
constituents of concern for F001 through
F005 and F039 waste and underlying
hazardous constituents in characteristic
wastes, unless the waste will be treated and
monitored for all constituents. If all
constituents will be treated and monitored,
there is no need to put them all on the LDR
notice.
ü
3. The notice must include the applicable
wastewater/ nonwastewater category (see
Section Section 728.102(d) and (f)) and sub-
divisions made within a waste code based on
waste-specific criteria (such as D003 reactive
cyanide).
ü
4. Waste analysis data (when available).
ü
287
5. For contaminated soil subject to LDRs as
provided in Section 728.149(a), the
constituents subject to treatment as described
in Section 728.149(d) and the following
statement, “this contaminated soil (does/does
not) contain listed hazardous waste and
(does/does not) exhibit a characteristic of
hazardous waste and (is subject to/complies
with) the soil treatment standards as
provided by Section 728.149(c).
ü
6. A certification is needed (see applicable
section for exact wording).
ü
4)
The owner or operator of a treatment facility shall submit a certification
signed by an authorized representative with the initial shipment of waste
or treatment residue of a restricted waste to the land disposal facility.
The certification must state as follows:
I certify under penalty of law that I have personally examined and
am familiar with the treatment technology and operation of the
treatment process used to support this certification. Based on my
inquiry of those individuals immediately responsible for obtaining
this information, I believe that the treatment process has been
operated and maintained properly so as to comply with the
treatment standards specified in 35 Ill. Adm. Code 728.140
without impermissible dilution of the prohibited waste. I am
aware there are significant penalties for submitting a false
certification, including the possibility of fine and imprisonment.
A certification is also necessary for contaminated soil and it must state:
I certify under penalty of law that I have personally examined and
am familiar with the treatment technology and operation of the
treatment process used to support this certification and believe that
it has been maintained and operated properly so as to comply with
treatment standards specified in 35 Ill. Adm. Code 728.149
without impermissible dilution of the prohibited wastes. I am
aware there are significant penalties for submitting a false
certification, including the possibility of fine and imprisonment.
A)
A copy of the certification must be placed in the treatment
facility’s on-site files. If the waste or treatment residue changes,
or the receiving facility changes, a new certification must be sent
to the receiving facility, and a copy placed in the treatment
facility’s file.
288
B)
Debris excluded from the definition of hazardous waste under 35
Ill. Adm. Code 721.103(e) (i.e., debris treated by an extraction or
destruction technology listed in Table F of this Part and debris that
the Agency has determined does not contain hazardous waste) is
subject to the notification and certification requirements of
subsection (d) of this Section rather than the certification
requirements of this subsection (b)(4).
C)
For wastes with organic constituents having treatment standards
expressed as concentration levels, if compliance with the treatment
standards is based in part or in whole on the analytical detection
limit alternative specified in Section 728.140(d), the certification
must be signed by an authorized representative and must state the
following:
I certify under penalty of law that I have personally
examined and am familiar with the treatment technology
and operation of the treatment process used to support this
certification. Based on my inquiry of those individuals
immediately responsible for obtaining this information, I
believe that the nonwastewater organic constituents have
been treated by combustion units as specified in 35 Ill.
Adm. Code 728.Table C. I have been unable to detect the
nonwastewater organic constituents, despite having used
best good faith efforts to analyze for such constituents. I
am aware that there are significant penalties for submitting
a false certification, including the possibility of fine and
imprisonment.
D)
For characteristic wastes that are subject to the treatment standards
in Section 728.140 and Table T of this Part (other than those
expressed as a required method of treatment) or Section 728.149
and which contain underlying hazardous constituents as defined in
35 Ill. Adm. Code 728.102(i); if these wastes are treated on-site to
remove the hazardous characteristic; and that are then sent off-site
for treatment of underlying hazardous constituents, the
certification must state the following:
I certify under penalty of law that the waste has been
treated in accordance with the requirements of 35 Ill.
Adm. Code 728.140 and Table T of Section 728.149 of
that Part to remove the hazardous characteristic. This
decharacterized waste contains underlying hazardous
constituents that require further treatment to meet
289
treatment standards. I am aware that there are significant
penalties for submitting a false certification, including the
possibility of fine and imprisonment.
E)
For characteristic wastes that contain underlying hazardous
constituents as defined in Section 728.102(i) that are treated on-
site to remove the hazardous characteristic and to treat underlying
hazardous constituents to levels in Section 728.148 and Table U
of this Part universal treatment standards, the certification must
state the following:
I certify under penalty of law that the waste has been
treated in accordance with the requirements of 35 Ill.
Adm. Code 728.140 and Table T of that Part to remove
the hazardous characteristic and that underlying hazardous
constituents, as defined in 35 Ill. Adm. Code 728.102(i),
have been treated on-site to meet the universal treatment
standards of 35 Ill. Adm. Code 728.148 and Table U of
that Part universal treatment standards. I am aware that
there are significant penalties for submitting a false
certification, including the possibility of fine and
imprisonment.
5)
If the waste or treatment residue will be further managed at a different
treatment, storage, or disposal facility, the treatment, storage, or disposal
facility sending the waste or treatment residue off-site must comply with
the notice and certification requirements applicable to generators under
this Section.
6)
Where the wastes are recyclable materials used in a manner constituting
disposal subject to the provisions of 35 Ill. Adm. Code 726.120(b),
regarding treatment standards and prohibition levels, the owner or
operator of a treatment facility (i.e., the recycler) is not required to notify
the receiving facility pursuant to subsection (b)((3)) of this Section. With
each shipment of such wastes the owner or operator of the recycling
facility shall submit a certification described in subsection (b)((4) of this
Section and a notice that includes the information listed in subsection
(b)((3) of this Section (except the manifest number) to the Agency. The
recycling facility also shall keep records of the name and location of each
entity receiving the hazardous waste-derived product.
c)
Except where the owner or operator is disposing of any waste that is a
recyclable material used in a manner constituting disposal pursuant to 35 Ill.
Adm. Code 726.120(b), the owner or operator of any land disposal facility
disposing any waste subject to restrictions under this Part shall:
290
1)
Maintain in its files copies of the notice and certifications specified in
subsection (a) or (b) of this Section.
2)
Test the waste or an extract of the waste or treatment residue developed
using SW-846 Method 1311 (the Toxicity Characteristic Leaching
Procedure), incorporated by reference in 35 Ill. Adm. Code 720.111), to
assure that the waste or treatment residue is in compliance with the
applicable treatment standards set forth in Subpart D of this Part. Such
testing must be performed according to the frequency specified in the
facility’s waste analysis plan as required by 35 Ill. Adm. Code 724.113
or 35 Ill. Adm. Code 725.113.
3)
Where the owner or operator is disposing of any waste that is subject to
the prohibitions under Section 728.133(f) but not subject to the
prohibitions set forth in Section 728.132, the owner or operator shall
ensure that such waste is the subject of a certification according to the
requirements of Section 728.108 prior to disposal in a landfill or surface
impoundment unit, and that such disposal is in accordance with the
requirements of Section 728.105(h)(2). The same requirement applies to
any waste that is subject to the prohibitions under Section 728.133(f) and
also is subject to the statutory prohibitions in the codified prohibitions in
Section 728.139 or Section 728.132.
4)
Where the owner or operator is disposing of any waste that is a
recyclable material used in a manner constituting disposal subject to the
provisions of 35 Ill. Adm. Code 726.120(b), the owner or operator is not
subject to subsections (c)(1) through (c)(3) of this Section with respect to
such waste.
d)
A generator or treater that first claims that hazardous debris is excluded from the
definition of hazardous waste under 35 Ill. Adm. Code 721.103(e) (i.e., debris
treated by an extraction or destruction technology provided by Table F of this
Part, and debris that has been delisted) is subject to the following notification and
certification requirements:
1)
A one-time notification must be submitted to the Agency including the
following information:
A)
The name and address of the RCRA Subtitle D (municipal solid
waste landfill) facility receiving the treated debris;
B)
A description of the hazardous debris as initially generated,
including the applicable USEPA hazardous waste numbers; and
291
C)
For debris excluded under 35 Ill. Adm. Code 721.103(e)(1), the
technology from Table F of this Part used to treat the debris.
2)
The notification must be updated if the debris is shipped to a different
facility and, for debris excluded under 35 Ill. Adm. Code 721.102(e)(1),
if a different type of debris is treated or if a different technology is used
to treat the debris.
3)
For debris excluded under 35 Ill. Adm. Code 721.103(e)(1), the owner
or operator of the treatment facility shall document and certify compliance
with the treatment standards of Table F of this Part, as follows:
A)
Records must be kept of all inspections, evaluations, and analyses
of treated debris that are made to determine compliance with the
treatment standards;
B)
Records must be kept of any data or information the treater
obtains during treatment of the debris that identifies key operating
parameters of the treatment unit; and
C)
For each shipment of treated debris, a certification of compliance
with the treatment standards must be signed by an authorized
representative and placed in the facility’s files. The certification
must state the following:
I certify under penalty of law that the debris has been
treated in accordance with the requirements of 35 Ill.
Adm. Code 728.145. I am aware that there are significant
penalties for making a false certification, including the
possibility of fine and imprisonment.
e)
A generator or treater that first receives a determination from USEPA or the
Agency that a given contaminated soil subject to LDRs, as provided in Section
728.149(a), no longer contains a listed hazardous waste and generators and
treaters that first determine that a contaminated soil subject to LDRs, as provided
in Section 728.149(a), no longer exhibits a characteristic of hazardous waste
shall do the following:
1)
Prepare a one-time only documentation of these determinations including
all supporting information; and
2)
Maintain that information in the facility files and other records for a
minimum of three years.
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
292
Section 728.109
Special Rules for Characteristic Wastes
a)
The initial generator of a solid waste shall determine each USEPA hazardous
waste number (waste code) applicable to the waste in order to determine the
applicable treatment standards under Subpart D of this Part. For purposes of this
Part, the waste must carry the waste code for any applicable listing under 35 Ill.
Adm. Code 721.Subpart D. In addition, the waste must carry one or more of
the waste codes under 35 Ill. Adm. Code 721.Subpart C where the waste
exhibits a characteristic, except in the case when the treatment standard for the
listed waste operates in lieu of the treatment standard for the characteristic waste,
as specified in subsection (b) of this Section. If the generator determines that its
waste displays a characteristic of hazardous waste (and the waste is not D001
nonwastewaters treated by CMBST, RORGS, or POLYM of Section 728.Table
C), the generator shall determine the underlying hazardous constituents (as
defined at Section 728.102(i)) in the characteristic waste.
b)
Where a prohibited waste is both listed under 35 Ill. Adm. Code 721.Subpart D
and exhibits a characteristic under 35 Ill. Adm. Code 721.Subpart C, the
treatment standard for the waste code listed in 35 Ill. Adm. Code 721.Subpart D
will operate in lieu of the standard for the waste code under 35 Ill. Adm. Code
721.Subpart C, provided that the treatment standard for the listed waste includes
a treatment standard for the constituent that causes the waste to exhibit the
characteristic. Otherwise, the waste must meet the treatment standards for all
applicable listed and characteristic waste codes.
c)
In addition to any applicable standards determined from the initial point of
generation, no prohibited waste that exhibits a characteristic under 35 Ill. Adm.
Code 721.Subpart C shall be land disposed unless the waste complies with the
treatment standards under Subpart D of this Part.
d)
A waste that exhibits a characteristic is also subject to Section 728.107
requirements, except that once the waste is no longer hazardous, a one-time
notification and certification must be placed in the generator’s or treater’s files
and sent to the Agency, except for those facilities described in subsection (f) of
this Section. The notification and certification that is placed in the generator’s or
treater’s files must be updated if the process or operation generating the waste
changes or if the RCRA Subtitle D (municipal solid waste landfill) facility
receiving the waste changes. However, the generator or treater need only notify
the Agency on an annual basis if such changes occur. Such notification and
certification should be sent to the Agency by the end of the year, but no later
than December 31.
1)
The notification must include the following information:
293
A)
The name and address of the RCRA Subtitle D (municipal solid
waste landfill) facility receiving the waste shipment; and
B)
A description of the waste as initially generated, including the
applicable USEPA hazardous waste numbers, the treatability
group(s) groups, and the underlying hazardous constituents (as
defined in Section 728.102(i)), unless the waste will be treated and
monitored for all underlying hazardous constituents. If all
underlying hazardous constituents will be treated and monitored,
there is no requirement to list any of the underlying hazardous
constituents on the notice.
2)
The certification must be signed by an authorized representative and must
state the language found in Section 728.107(b)(4). If treatment removes
the characteristic but does not meet standards applicable to underlying
hazardous constituents, then the certification found in Section
728.107(b)(4)(D) applies.
3)
For a characteristic waste whose ultimate disposal will be into a Class I
nonhazardous waste injection well, and for which compliance with the
treatment standards set forth in Sections 728.148 and 728.Table U for
underlying hazardous constituents is achieved through pollution
prevention that meets the criteria set forth at 35 Ill. Adm. Code
738.101(d), the following information must also be included:
A)
A description of the pollution prevention mechanism and when it
was implemented, if already complete;
B)
The mass of each underlying hazardous constituent before
pollution prevention;
C)
The mass of each underlying hazardous constituent that must be
removed, adjusted to reflect variations in mass due to normal
operating conditions; and
D)
The mass reduction of each underlying hazardous constituent that
is achieved.
e)
For a decharacterized waste managed on-site in a wastewater treatment system
subject to the federal Clean Water Act (CWA) or zero-dischargers engaged in
CWA-equivalent treatment, compliance with the treatment standards set forth in
Sections 728.148 and 728.Table D must be monitored quarterly, unless the
treatment is aggressive biological treatment, in which case compliance must be
monitored annually. Monitoring results must be kept in on-site files for 5 years.
294
f)
For a decharacterized waste managed on-site in a wastewater treatment system
subject to the federal Clean Water Act (CWA) for which all underlying
hazardous constituents (as defined in Section 728.102) are addressed by a CWA
permit, this compliance must be documented and this documentation must be kept
in on-site files.
g)
For a characteristic waste whose ultimate disposal will be into a Class I
nonhazardous waste injection well that qualifies for the de minimis exclusion
described in Section 728.101, information supporting that qualification must be
kept in on-site files.
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
SUBPART C: PROHIBITION ON LAND DISPOSAL
Section 728.133
Waste-Specific Prohibitions -- Organobromine Wastes (Repealed)
a) The waste specified in 35 Ill. Adm. Code 721.132 as USEPA hazardous waste
number K140 and in 35 Ill. Adm. Code 721.133 as USEPA hazardous waste
number U408 are prohibited from land disposal. In addition, soils and debris
contaminated with these wastes, radioactive wastes mixed with these hazardous
wastes, and soils and debris contaminated with these radioactive mixed wastes
are prohibited from land disposal.
b) The requirements of subsection (a) of this Section do not apply if:
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 the 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 that has met treatment standards in Section 728.140 and
Table T of this Part or, in the alternative, the treatment standards in
Section 728.145; or
5) USEPA has granted an extension to the effective date of a prohibition, as
described in Section 728.105, with respect to those wastes covered by the
extension.
295
c) 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 shall test a sample of the waste extract or the entire
waste, depending on whether the treatment standards are expressed as
concentrations in the waste extract or in the waste, or the generator may use
knowledge of the waste. If the waste contains constituents 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: Repealed at 24 Ill. Reg. ________, effective ______________________)
SUBPART D: TREATMENT STANDARDS
Section 728.140
Applicability of Treatment Standards
a)
A prohibited waste identified in Table T of this Part, “Treatment Standards for
Hazardous Wastes”, may be land disposed only if it meets the requirements
found in that Table. For each waste, Table T of this Part identifies one of three
types of treatment standard requirements:
1)
All hazardous constituents in the waste or in the treatment residue must
be at or below the values found in Table T of this Part for that waste
(“total waste standards”);
2)
The hazardous constituents in the extract of the waste or in the extract of
the treatment residue must be at or below the values found in Table T of
this Part (“waste extract standards”); or
3)
The waste must be treated using the technology specified in Table T of
this Part (“technology standard”), which is described in detail in Table C
of this Part, “Technology Codes and Description of Technology-Based
Standards”.
b)
For wastewaters, compliance with concentration level standards is based on
maximums for any one day, except for D004 through D011 wastes for which the
previously promulgated treatment standards based on grab samples remain in
effect. For all nonwastewaters, compliance with concentration level standards is
based on grab sampling. For wastes covered by the waste extract standards, the
test Method 1311, the Toxicity Characteristic Leaching Procedure, found in
“Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”,
USEPA Publication SW-846, incorporated by reference in Section 35 Ill. Adm.
Code 720.111, must be used to measure compliance. An exception is made for
D004 and D008, for which either of two test methods may be used: Method
296
1311 or Method 1310, the Extraction Procedure Toxicity Test, found in “Test
Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA
Publication SW-846, incorporated by reference in Section 35 Ill. Adm. Code
720.111. For wastes covered by a technology standard, the wastes may be land
disposed after being treated using that specified technology or an equivalent
treatment technology approved by the Agency pursuant to Section 728.142(b).
c)
When wastes with differing treatment standards for a constituent of concern are
combined for purposes of treatment, the treatment residue must meet the lowest
treatment standard for the constituent of concern.
d)
Notwithstanding the prohibitions specified in subsection (a) of this Section,
treatment and disposal facilities may demonstrate (and certify pursuant to 35 Ill.
Adm. Code 728.107(b)(5)) compliance with the treatment standards for organic
constituents specified by a footnote in Table T of this Part, provided the
following conditions are satisfied:
1)
The treatment standards for the organic constituents were established
based on incineration in units operated in accordance with the technical
requirements of 35 Ill. Adm. Code 724.Subpart O, or based on
combustion in fuel substitution units operating in accordance with
applicable technical requirements;
2)
The treatment or disposal facility has used the methods referenced in
subsection (d)(1) of this Section to treat the organic constituents; and
3)
The treatment or disposal facility may demonstrate compliance with
organic constituents if good-faith analytical efforts achieve detection limits
for the regulated organic constituents that do not exceed the treatment
standards specified in this Section and Table T of this Part by an order of
magnitude.
e)
For a characteristic waste (USEPA hazardous waste number D001 through
D043) that is subject to treatment standards set forth in Table T of this Part,
“Treatment Standards for Hazardous Wastes”, and the waste is not managed in a
wastewater treatment system that is either regulated under the Clean Water Act
(CWA) or one that is CWA-equivalent or the waste is injected into a Class I non-
hazardous deep injection well, all underlying hazardous constituents (as defined
in Section 728.102) must meet the universal treatment standards, set forth in
Table U of this Part prior to land disposal, as defined in Section 728.102.
f)
The treatment standards for USEPA hazardous waste numbers F001 through
F005 nonwastewater constituents carbon disulfide, cyclohexanone, or methanol
apply to wastes that contain only one, two, or three of these constituents.
Compliance is measured for these constituents in the waste extract from test
297
Method 1311, the Toxicity Characteristic Leaching Procedure found in “Test
Methods for Evaluating Solid Waste, Physical/Chemical Methods”, USEPA
Publication SW-846, incorporated by reference in Section 35 Ill. Adm. Code
720.111. If the waste contains any of these three constituents along with any of
the other 25 constituents found in USEPA hazardous waste numbers F001
through F005, then compliance with treatment standards for carbon disulfide,
cyclohexanone, or methanol are not required.
g)
This subsection corresponds with 40 CFR 268.40(g), added at 61 Fed. Reg.
43927 (Aug. 26, 1996), which has expired. This statement maintains structural
consistency with the federal rules.
h)
Prohibited USEPA hazardous waste numbers D004 through D011, mixed
radioactive wastes, and mixed radioactive listed wastes containing metal
constituents that were previously treated by stabilization to the treatment
standards in effect at that time and then put into storage do not have to be re-
treated to meet treatment standards in this Section prior to land disposal.
i)
Zinc micronutrient fertilizers that are produced for the use of the general public
and which are produced from or contain recycled characteristic hazardous wastes
(D004 through D011) are subject to the applicable treatment standards set forth
in 40 CFR 268.41 (1990) (1999), incorporated by reference in 35 Ill. Adm.
Code 720.111(b).
BOARD NOTE: USEPA added 40 CFR 268.40(i) at 63 Fed. Reg. 46331
(Aug. 31, 1998) to stay the Phase IV land disposal restrictions (LDRs) as they
apply to zinc-containing fertilizers while it develops a more comprehensive set of
regulations applicable to use of hazardous waste in making fertilizers. To effect
the stay, USEPA applied the 1990 LDR standards to the affected materials.
j)
The treatment standards for the wastes specified in 35 Ill. Adm. Code 721.133 as
USEPA hazardous waste numbers P185, P191, P192, P197, U364, U394, and
U395 may be satisfied by either meeting the constituent concentrations presented
in Table T of this Part, “Treatment Standards for Hazardous Wastes,” or by
treating the waste by the following technologies: combustion, as defined by the
technology code CMBST at Table C, for nonwastewaters,; 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.
BOARD NOTE: USEPA added a second 40 CFR 268.40(i) at 63 Fed. Reg.
46415 (Sep. 4, 1998) to indefinitely extend the alternative treatment standards for
seven carbamate wastes. The Board has incorporated this later-adopted duplicate
subsection (i) as subsection (j).
298
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
Section 728.149
Alternative LDR Treatment Standards for Contaminated Soil
a)
Applicability. An owner or operator shall comply with LDRs prior to placing
soil that exhibits a characteristic of hazardous waste or which exhibited a
characteristic of hazardous waste at the time it was generated into a land disposal
unit. The following chart describes whether an owner or operator must comply
with LDRs prior to placing soil contaminated by listed hazardous waste into a
land disposal unit:
If the LDRs
And if the LDRs
And if
Then the owner
or operator
Applied to the
listed waste when
it contaminated
the soil*.
Apply to the listed
waste now.
—
Must comply with
LDRs.
Did not apply to
the listed waste
when it 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.
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.
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
299
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.
1)
All soils. Prior to land disposal, all constituents subject to treatment must
be treated as follows:
A)
For non-metals except carbon disulfide, cyclohexanone, and
methanol, treatment must achieve 90 percent reduction in total
constituent concentrations, except as provided by subsection
(c)(1)(C) of this Section.
B)
For metals and carbon disulfide, cyclohexanone, and methanol,
treatment must achieve 90 percent reduction in constituent
concentrations as measured in leachate from the treated media
(tested according to the TCLP) or 90 percent reduction in total
constituent concentrations (when a metal removal treatment
technology is used), except as provided by subsection (c)(1)(C) of
this Section.
C)
When treatment of any constituent subject to treatment to a 90
percent reduction standard would result in a concentration less
than 10 times the universal treatment standard for that constituent,
treatment to achieve constituent concentrations less than 10 times
the universal treatment standard is not required. The universal
treatment standards are identified in Table U of this Part.
2)
Soils that exhibit the characteristic of ignitability, corrosivity or
reactivity. In addition to the treatment required by subsection (c)(1) of
this Section, prior to land disposal, soils that exhibit the characteristic of
ignitability, corrosivity, or reactivity must be treated to eliminate these
characteristics.
3)
Soils that contain nonanalyzable constituents. In addition to the treatment
requirements of subsections (c)(1) and (c)(2) of this Section, prior to land
disposal, the following treatment is required for soils that contain
nonanalyzable constituents:
A)
For soil that contains only analyzable and nonanalyzable organic
constituents, treatment of the analyzable organic constituents to the
300
levels specified in subsections (c)(1) and (c)(2) of this Section; or
B)
For soil that contains only nonanalyzable constituents, treatment
by the methods specified in Section 728.142 for the waste
contained in the soil.
d)
Constituents subject to treatment. When applying the soil treatment standards in
subsection (c) of this Section, constituents subject to treatment are any
constituents listed in Table U of this Part universal treatment standards that are
reasonably expected to be present in any given volume of contaminated soil,
except fluoride, selenium, sulfides, vanadium and zinc, and are present at
concentrations greater than ten times the universal treatment standard.
e)
Management of treatment residuals. Treatment residuals from treating
contaminated soil identified by subsection (a) of this Section as needing to comply
with LDRs must be managed as follows:
1)
Soil residuals are subject to the treatment standards of this Section;
2)
Non-soil residuals are subject to the following requirements:
A)
For soils contaminated by listed hazardous waste, the RCRA
Subtitle C standards applicable to the listed hazardous waste; and
B)
For soils that exhibit a characteristic of hazardous waste, if the
non-soil residual also exhibits a characteristic of hazardous waste,
the treatment standards applicable to the characteristic hazardous
waste.
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
Section 728.Table T
Treatment Standards for Hazardous Wastes
Note: The treatment standards that heretofore appeared in tables in Sections 728.141, 728.142,
and 728.143 have been consolidated into this table.
Waste Code
Waste Description and Treatment or Regulatory 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
301
D001
9
Ignitable Characteristic Wastes, except for the 35 Ill. Adm. Code 721.121(a)(1) High TOC
Subcategory.
NA
NA
DEACT and meet
Section 728.148
standards
8
;
8
or
RORGS; or
CMBST
DEACT and meet
Section 728.148
standards
8
;
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
NA
RORGS; CMBST;
or POLYM
D002
9
Corrosive Characteristic Wastes.
NA
NA
DEACT and meet
Section 728.148
standards
8
DEACT and meet
Section 728.148
standards
8
D002, D004, D005, D006, D007, D008, D009, D010, D011
Radioactive high level wastes generated during the reprocessing of fuel rods.
(Note: This subcategory consists of nonwastewaters only.)
Corrosivity (pH)
NA
NA
HLVIT
Arsenic
7440-38-2
NA
HLVIT
Barium
7440-39-3
NA
HLVIT
Cadmium
7440-43-9
NA
HLVIT
Chromium (Total)
7440-47-3
NA
HLVIT
Lead
7439-92-1
NA
HLVIT
Mercury
7439-97-6
NA
HLVIT
Selenium
7782-49-2
NA
HLVIT
Silver
7440-22-4
NA
HLVIT
D003
9
Reactive Sulfides Subcategory based on 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
NA
DEACT and meet
Section 728.148
standards
8
DEACT and meet
Section 728.148
standards
8
302
D003
9
Unexploded ordnance and other explosive devices that have been the subject of an emergency
response.
NA
NA
DEACT
DEACT
D003
9
Other Reactives Subcategory based on 35 Ill. Adm. Code 721.123(a)(1).
NA
NA
DEACT and meet
Section 728.148
standards
8
DEACT and meet
Section 728.148
standards
8
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
D006
9
Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for cadmium based
on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
Cadmium
7440-43-9
0.69 and meet
Section 728.148
standards
8
0.11 mg/l TCLP
and meet Section
728.148 standards
8
303
D006
9
Cadmium-Containing Batteries Subcategory
(Note: This subcategory consists of nonwastewaters only.)
Cadmium
7440-43-9
NA
RTHRM
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.
Chromium (Total)
7440-47-3
2.77 and meet
Section 728.148
standards
8
0.60 mg/l TCLP
and meet Section
728.148 standards
8
D008
9
Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for lead based on
the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
Lead
7439-92-1
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
7439-92-1
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
MACRO
D009
9
Nonwastewaters that exhibit, or are expected to exhibit, the characteristic of toxicity for
mercury based on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method
1311; and contain greater than or equal to 260 mg/kg total mercury that also contain organics
and are not incinerator residues. (High Mercury-Organic Subcategory)
Mercury
7439-97-6
NA
IMERC; or
RMERC
304
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 are inorganic,
including incinerator residues and residues from RMERC. (High Mercury-Inorganic
Subcategory)
Mercury
7439-97-6
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
NA
AMLGM
D009
9
Hydraulic oil contaminated with Mercury Radioactive Materials Subcategory.
(Note: This subcategory consists of nonwastewaters only.)
Mercury
7439-97-6
NA
IMERC
305
D010
9
Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for selenium based
on the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
Selenium
7782-49-2
0.82
5.7 mg/l TCLP
and meet Section
728.148 standards
8
D011
9
Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for silver based on
the toxicity characteristic leaching procedure (TCLP) in SW-846 Method 1311.
Silver
7440-22-4
0.43
0.14 mg/l TCLP
and meet Section
728.148 standards
8
D012
9
Wastes that are TC for Endrin based on the toxicity characteristic leaching procedure (TCLP) in
SW-846 Method 1311.
Endrin
72-20-8
BIODG; or
CMBST
0.13 and meet
Section 728.148
standards
8
Endrin aldehyde
7421-93-4
BIODG; or
CMBST
0.13 and meet
Section 728.148
standards
8
D013
9
Wastes that are TC for Lindane based on the toxicity characteristic leaching procedure (TCLP)
in SW-846 Method 1311.
α
-BHC
319-84-6
CARBN; or
CMBST
0.066 and meet
Section 728.148
standards
8
β
-BHC
319-85-7
CARBN; or
CMBST
0.066 and meet
Section 728.148
standards
8
δ
-BHC
319-86-8
CARBN; or
CMBST
0.066 and meet
Section 728.148
standards
8
χ
-BHC (Lindane)
58-89-9
CARBN; or
CMBST
0.066 and meet
Section 728.148
standards
8
306
D014
9
Wastes that are TC for Methoxychlor based on the toxicity characteristic leaching procedure
(TCLP) in SW-846 Method 1311.
Methoxychlor
72-43-5
WETOX or
CMBST
0.18 and meet
Section 728.148
standards
8
D015
9
Wastes that are TC for Toxaphene based on the toxicity characteristic leaching procedure
(TCLP) in SW-846 Method 1311.
Toxaphene
8001-35-2
BIODG or
CMBST
2.6 and meet
Section 728.148
standards
8
D016
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)
94-75-7
CHOXD; BIODG;
or CMBST
10 and meet
Section 728.148
standards
8
D017
9
Wastes that are TC for 2,4,5-TP (Silvex) based on the toxicity characteristic leaching procedure
(TCLP) in SW-846 Method 1311.
2,4,5-TP (Silvex)
93-72-1
CHOXD or
CMBST
7.9 and meet
Section 728.148
standards
8
D018
9
Wastes that are TC for Benzene based on the toxicity characteristic leaching procedure (TCLP)
in SW-846 Method 1311.
Benzene
71-43-2
0.14 and meet
Section 728.148
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
0.057 and meet
Section 728.148
standards
8
6.0 and meet
Section 728.148
standards
8
307
D020
9
Wastes that are TC for Chlordane based on the toxicity characteristic leaching procedure
(TCLP) in SW-846 Method 1311.
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
D021
9
Wastes that are TC for Chlorobenzene based on the toxicity characteristic leaching procedure
(TCLP) in SW-846 Method 1311.
Chlorobenzene
108-90-7
0.057 and meet
Section 728.148
standards
8
6.0 and meet
Section 728.148
standards
8
D022
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
Wastes that are TC for o-Cresol based on the toxicity characteristic leaching procedure (TCLP)
in SW-846 Method 1311.
o-Cresol
95-48-7
0.11 and meet
Section 728.148
standards
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.
m-Cresol
(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
Wastes that are TC for p-Cresol based on the toxicity characteristic leaching procedure (TCLP)
in SW-846 Method 1311.
p-Cresol
(difficult to distinguish from m-
cresol)
106-44-5
0.77 and meet
Section 728.148
standards
8
5.6 and meet
Section 728.148
standards
8
308
D026
9
Wastes that are TC for Cresols (Total) based on the toxicity characteristic leaching procedure
(TCLP) in SW-846 Method 1311.
Cresol-mixed isomers (Cresylic
acid)
(sum of o-, m-, and p-cresol
concentrations)
1319-77-3
0.88 and meet
Section 728.148
standards
8
11.2 and meet
Section 728.148
standards
8
D027
9
Wastes that are TC for p-Dichlorobenzene based on the toxicity characteristic leaching
procedure (TCLP) in SW-846 Method 1311.
p-Dichlorobenzene (1,4-
Dichlorobenzene)
106-46-7
0.090 and meet
Section 728.148
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.
1,2-Dichloroethane
107-06-2
0.21 and meet
Section 728.148
standards
8
6.0 and meet
Section 728.148
standards
8
D029
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
75-35-4
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
0.32 and meet
Section 728.148
standards
8
140 and meet
Section 728.148
standards
8
D031
9
Wastes that are TC for Heptachlor based on the toxicity characteristic leaching procedure
(TCLP) in SW-846 Method 1311.
Heptachlor
76-44-8
0.0012 and meet
Section 728.148
standards
8
0.066 and meet
Section 728.148
standards
8
Heptachlor epoxide
1024-57-3
0.016 and meet
Section 728.148
standards
8
0.066 and meet
Section 728.148
standards
8
309
D032
9
Wastes that are TC for Hexachlorobenzene based on the toxicity characteristic leaching
procedure (TCLP) in SW-846 Method 1311.
Hexachlorobenzene
118-74-1
0.055 and meet
Section 728.148
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
0.055 and meet
Section 728.148
standards
8
5.6 and meet
Section 728.148
standards
8
D034
9
Wastes that are TC for Hexachloroethane based on the toxicity characteristic leaching procedure
(TCLP) in SW-846 Method 1311.
Hexachloroethane
67-72-1
0.055 and meet
Section 728.148
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
0.28 and meet
Section 728.148
standards
8
36 and meet
Section 728.148
standards
8
D036
9
Wastes that are TC for Nitrobenzene based on the toxicity characteristic leaching procedure
(TCLP) in SW-846 Method 1311.
Nitrobenzene
98-95-3
0.068 and meet
Section 728.148
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.
Pentachlorophenol
87-86-5
0.089 and meet
Section 728.148
standards
8
7.4 and meet
Section 728.148
standards
8
D038
9
Wastes that are TC for Pyridine based on the toxicity characteristic leaching procedure (TCLP)
310
in SW-846 Method 1311.
Pyridine
110-86-1
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
0.056 and meet
Section 728.148
standards
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
0.27 and meet
Section 728.148
standards
8
6.0 and meet
Section 728.148
standards
8
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,
311
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
Acetone
67-64-1
0.28
160
Benzene
71-43-2
0.14
10
n-Butyl alcohol
71-36-3
5.6
2.6
Carbon disulfide
75-15-0
3.8
NA
Carbon tetrachloride
56-23-5
0.057
6.0
Chlorobenzene
108-90-7
0.057
6.0
o-Cresol
95-48-7
0.11
5.6
m-Cresol
(difficult to distinguish from p-
cresol)
108-39-4
0.77
5.6
p-Cresol
(difficult to distinguish from m-
cresol)
106-44-5
0.77
5.6
Cresol-mixed isomers (Cresylic
acid)
(sum of o-, m-, and p-cresol
concentrations)
1319-77-3
0.88
11.2
Cyclohexanone
108-94-1
0.36
NA
o-Dichlorobenzene
95-50-1
0.088
6.0
Ethyl acetate
141-78-6
0.34
33
Ethyl benzene
100-41-4
0.057
10
Ethyl ether
60-29-7
0.12
160
Isobutyl alcohol
78-83-1
5.6
170
Methanol
67-56-1
5.6
NA
Methylene chloride
75-9-2
0.089
30
Methyl ethyl ketone
78-93-3
0.28
36
Methyl isobutyl ketone
108-10-1
0.14
33
Nitrobenzene
98-95-3
0.068
14
Pyridine
110-86-1
0.014
16
Tetrachloroethylene
127-18-4
0.056
6.0
Toluene
108-88-3
0.080
10
1,1,1-Trichloroethane
71-55-6
0.054
6.0
1,1,2-Trichloroethane
79-00-5
0.054
6.0
1,1,2-Trichloro-1,2,2-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)
1330-20-7
0.32
30
312
F001, F002, F003, F004 & F005
F003 and F005 solvent wastes that contain any combination of one or more of the following
three solvents as the only listed F001 through F005 solvents: carbon disulfide, cyclohexanone,
or methanol. (Formerly Section 728.141(c))
Carbon disulfide
75-15-0
3.8
4.8 mg/l TCLP
Cyclohexanone
108-94-1
0.36
0.75 mg/l TCLP
Methanol
67-56-1
5.6
0.75 mg/l TCLP
F001, F002, F003, F004 & F005
F005 solvent waste containing 2-Nitropropane as the only listed F001 through F005 solvent.
2-Nitropropane
79-46-9
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
F001, F002, F003, F004 & F005
F005 solvent waste containing 2-Ethoxyethanol as the only listed F001 through F005 solvent.
2-Ethoxyethanol
110-80-5
BIODG; or
CMBST
CMBST
F006
Wastewater treatment sludges from electroplating operations except from the following
processes: (1) Sulfuric acid anodizing of aluminum; (2) tin plating on carbon steel; (3) zinc
plating (segregated basis) on carbon steel; (4) aluminum or zinc-aluminum plating on carbon
steel; (5) cleaning or stripping associated with tin, zinc, and aluminum plating on carbon steel;
and (6) chemical etching and milling of aluminum.
Cadmium
7440-43-9
0.69
0.11 mg/l TCLP
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Cyanides (Total)
7
57-12-5
1.2
590
Cyanides (Amenable)
7
57-12-5
0.86
30
Lead
7439-92-1
0.69
0.75 mg/l TCLP
Nickel
7440-02-0
3.98
11 mg/l TCLP
Silver
7440-22-4
NA
0.14 mg/l TCLP
F007
Spent cyanide plating bath solutions from electroplating operations.
Cadmium
7440-43-9
NA
0.11 mg/l TCLP
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Cyanides (Total)
7
57-12-5
1.2
590
Cyanides (Amenable)
7
57-12-5
0.86
30
Lead
7439-92-1
0.69
0.75 mg/l TCLP
Nickel
7440-02-0
3.98
11 mg/l TCLP
Silver
7440-22-4
NA
0.14 mg/l TCLP
313
F008
Plating bath residues from the bottom of plating baths from electroplating operations where
cyanides are used in the process.
Cadmium
7440-43-9
NA
0.11 mg/l TCLP
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Cyanides (Total)
7
57-12-5
1.2
590
Cyanides (Amenable)
7
57-12-5
0.86
30
Lead
7439-92-1
0.69
0.75 mg/l TCLP
Nickel
7440-02-0
3.98
11 mg/l TCLP
Silver
7440-22-4
NA
0.14 mg/l TCLP
F009
Spent stripping and cleaning bath solutions from electroplating operations where cyanides are
used in the process.
Cadmium
7440-43-9
NA
0.11 mg/l TCLP
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Cyanides (Total)
7
57-12-5
1.2
590
Cyanides (Amenable)
7
57-12-5
0.86
30
Lead
7439-92-1
0.69
0.75 mg/l TCLP
Nickel
7440-02-0
3.98
11 mg/l TCLP
Silver
7440-22-4
NA
0.14 mg/l TCLP
F010
Quenching bath residues from oil baths from metal heat treating 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
7440-43-9
NA
0.11 mg/l TCLP
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Cyanides (Total)
7
57-12-5
1.2
590
Cyanides (Amenable)
7
57-12-5
0.86
30
Lead
7439-92-1
0.69
0.75 mg/l TCLP
Nickel
7440-02-0
3.98
11 mg/l TCLP
Silver
7440-22-4
NA
0.14 mg/l TCLP
F012
Quenching wastewater treatment sludges from metal heat treating operations where cyanides are
used in the process.
Cadmium
7440-43-9
NA
0.11 mg/l TCLP
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Cyanides (Total)
7
57-12-5
1.2
590
Cyanides (Amenable)
7
57-12-5
0.86
30
314
Lead
7439-92-1
0.69
0.75 mg/l TCLP
Nickel
7440-02-0
3.98
11 mg/l TCLP
Silver
7440-22-4
NA
0.14 mg/l TCLP
F019
Wastewater treatment sludges from the chemical conversion coating of aluminum except from
zirconium phosphating in aluminum can washing when such phosphating is an exclusive
conversion coating process.
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Cyanides (Total)
7
57-12-5
1.2
590
Cyanides (Amenable)
7
57-12-5
0.86
30
F020, F021, F022, F023, F026
Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the
production or manufacturing use (as a reactant, chemical intermediate, or component in a
formulating process) of: (1) tri- or tetrachlorophenol, or of intermediates used to produce their
pesticide derivatives, excluding wastes from the production of Hexachlorophene from highly
purified 2,4,5-trichlorophenol (i.e., F020); (2) pentachlorophenol, or of intermediates used to
produce its derivatives (i.e., F021); (3) tetra-, penta-, or hexachlorobenzenes under alkaline
conditions (i.e., F022) and wastes (except wastewater and spent carbon from hydrogen chloride
purification) from the production of materials on equipment previously used for the production
or manufacturing use (as a reactant, chemical intermediate, or component in a formulating
process) of: (1) tri- or tetrachlorophenols, excluding wastes from equipment used only for the
production of Hexachlorophene from highly purified 2,4,5-trichlorophenol (F023) or (2) tetra-,
penta-, or hexachlorobenzenes under alkaline conditions (i.e., F026).
HxCDDs (All Hexachloro-
dibenzo-p-dioxins)
NA
0.000063
0.001
HxCDFs (All Hexachloro-
dibenzofurans)
NA
0.000063
0.001
PeCDDs (All Pentachloro-
dibenzo-p-dioxins)
NA
0.000063
0.001
PeCDFs (All Pentachloro-
dibenzofurans)
NA
0.000035
0.001
Pentachlorophenol
87-86-5
0.089
7.4
TCDDs (All Tetrachloro-
dibenzo-p-dioxins)
NA
0.000063
0.001
TCDFs (All Tetrachloro-
dibenzofurans)
NA
0.000063
0.001
2,4,5-Trichlorophenol
95-95-4
0.18
7.4
2,4,6-Trichlorophenol
88-06-2
0.035
7.4
2,3,4,6-Tetrachlorophenol
58-90-2
0.030
7.4
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
315
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
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
bis(2-Ethylhexyl) phthalate
117-81-7
0.28
28
Hexachloroethane
67-72-1
0.055
30
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Nickel
7440-02-0
3.98
11 mg/l TCLP
F025
Condensed light ends from the production of certain chlorinated aliphatic hydrocarbons by free
radical catalyzed processes. These chlorinated aliphatic hydrocarbons are those having carbon
chain lengths ranging from one up to and including five, with varying amounts and positions of
chlorine substitution. F025--Light Ends Subcategory.
Carbon tetrachloride
56-23-5
0.057
6.0
Chloroform
67-66-3
0.046
6.0
1,2-Dichloroethane
107-06-2
0.21
6.0
1,1-Dichloroethylene
75-35-4
0.025
6.0
Methylene chloride
75-9-2
0.089
30
1,1,2-Trichloroethane
79-00-5
0.054
6.0
Trichloroethylene
79-01-6
0.054
6.0
Vinyl chloride
75-01-4
0.27
6.0
F025
Spent filters and filter aids, and spent desiccant wastes from the production of certain
chlorinated aliphatic hydrocarbons by free radical catalyzed processes. These chlorinated
aliphatic hydrocarbons are those having carbon chain lengths ranging from one to and including
five, with varying amounts and positions of chlorine substitution. F025--Spent Filters/Aids and
Desiccants Subcategory.
Carbon tetrachloride
56-23-5
0.057
6.0
Chloroform
67-66-3
0.046
6.0
Hexachlorobenzene
118-74-1
0.055
10
Hexachlorobutadiene
87-68-3
0.055
5.6
Hexachloroethane
67-72-1
0.055
30
Methylene chloride
75-9-2
0.089
30
1,1,2-Trichloroethane
79-00-5
0.054
6.0
316
Trichloroethylene
79-01-6
0.054
6.0
Vinyl chloride
75-01-4
0.27
6.0
F027
Discarded unused formulations containing tri-, tetra-, or pentachlorophenol or discarded unused
formulations containing compounds derived from these chlorophenols. (This listing does not
include formulations containing hexachlorophene synthesized from prepurified 2,4,5-trichloro-
phenol as the sole component.)
HxCDDs (All Hexachloro-
dibenzo-p-dioxins)
NA
0.000063
0.001
HxCDFs (All Hexachloro-
dibenzofurans)
NA
0.000063
0.001
PeCDDs (All Pentachloro-
dibenzo-p-dioxins)
NA
0.000063
0.001
PeCDFs (All Pentachloro-
dibenzofurans)
NA
0.000035
0.001
Pentachlorophenol
87-86-5
0.089
7.4
TCDDs (All Tetrachloro-
dibenzo-p-dioxins)
NA
0.000063
0.001
TCDFs (All Tetrachloro-
dibenzofurans)
NA
0.000063
0.001
2,4,5-Trichlorophenol
95-95-4
0.18
7.4
2,4,6-Trichlorophenol
88-06-2
0.035
7.4
2,3,4,6-Tetrachlorophenol
58-90-2
0.030
7.4
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
0.001
HxCDFs (All Hexachloro-
dibenzofurans)
NA
0.000063
0.001
PeCDDs (All Pentachloro-
dibenzo-p-dioxins)
NA
0.000063
0.001
PeCDFs (All Pentachloro-
dibenzofurans)
NA
0.000035
0.001
Pentachlorophenol
87-86-5
0.089
7.4
TCDDs (All Tetrachloro-
dibenzo-p-dioxins)
NA
0.000063
0.001
TCDFs (All Tetrachloro-
dibenzofurans)
NA
0.000063
0.001
2,4,5-Trichlorophenol
95-95-4
0.18
7.4
2,4,6-Trichlorophenol
88-06-2
0.035
7.4
2,3,4,6-Tetrachlorophenol
58-90-2
0.030
7.4
317
F032
Wastewaters (except those that have not come into contact with process contaminants), process
residuals, preservative drippage, and spent formulations from wood preserving processes
generated at plants that currently use or have previously used chlorophenolic formulations
(except potentially cross-contaminated wastes that have had the F032 waste code deleted in
accordance with 35 Ill. Adm. Code 721.135 or potentially cross-contaminated wastes that are
otherwise currently regulated as hazardous wastes (i.e., F034 or F035), where the generator
does not resume or initiate use of chlorophenolic formulations). This listing does not include
K001 bottom sediment sludge from the treatment of wastewater from wood preserving
processes that use creosote or penta-chlorophenol.
Acenaphthene
83-32-9
0.059
3.4
Anthracene
120-12-7
0.059
3.4
Benz(a)anthracene
56-55-3
0.059
3.4
Benzo(b)fluoranthene (difficult
to distinguish from benzo(k)
fluoranthene)
205-99-2
0.11
6.8
Benzo(k)fluoranthene (difficult
to distinguish from benzo(b)
fluoranthene)
207-08-9
0.11
6.8
Benzo(a)pyrene
50-32-8
0.061
3.4
Chrysene
218-01-9
0.059
3.4
Dibenz(a,h)anthracene
53-70-3
0.055
8.2
2-4-Dimethyl phenol
105-67-9
0.036
14
Fluorene
86-73-7
0.059
3.4
Hexachlorodibenzo-p-dioxins
NA
0.000063 or
CMBST
11
0.001 or CMBST
11
Hexachlorodibenzofurans
NA
0.000063 or
CMBST
11
0.001 or CMBST
11
Indeno (1,2,3-c,d) pyrene
193-39-5
0.0055
3.4
Naphthalene
91-20-3
0.059
5.6
Pentachlorodibenzo-p-dioxins
NA
0.000063 or
CMBST
11
0.001 or CMBST
11
Pentachlorodibenzofurans
NA
0.000035 or
CMBST
11
0.001 or CMBST
11
Pentachlorophenol
87-86-5
0.089
7.4
Phenanthrene
85-01-8
0.059
5.6
Phenol
108-95-2
0.039
6.2
Pyrene
129-00-0
0.067
8.2
Tetrachlorodibenzo-p-dioxins
NA
0.000063 or
CMBST
11
0.001 or CMBST
11
Tetrachlorodibenzofurans
NA
0.000063 or
CMBST
11
0.001 or CMBST
11
2,3,4,6-Tetrachlorophenol
58-90-2
0.030
7.4
2,4,6-Trichlorophenol
88-06-2
0.035
7.4
Arsenic
7440-38-2
1.4
5.0 mg/l TCLP
318
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
F034
Wastewaters (except those that have not come into contact with process contaminants), process
residuals, preservative drippage, and spent formulations from wood preserving processes
generated at plants that use creosote formulations. This listing does not include K001 bottom
sediment sludge from the treatment of wastewater from wood preserving processes that use
creosote or pentachlorophenol.
Acenaphthene
83-32-9
0.059
3.4
Anthracene
120-12-7
0.059
3.4
Benz(a)anthracene
56-55-3
0.059
3.4
Benzo(b)fluoranthene (difficult
to distinguish from
benzo(k)fluoranthene)
205-99-2
0.11
6.8
Benzo(k)fluoranthene (difficult
to distinguish from
benzo(b)fluoranthene)
207-08-9
0.11
6.8
Benzo(a)pyrene
50-32-8
0.061
3.4
Chrysene
218-01-9
0.059
3.4
Dibenz(a,h)anthracene
53-70-3
0.055
8.2
Fluorene
86-73-7
0.059
3.4
Indeno (1,2,3-c,d) pyrene
193-39-5
0.0055
3.4
Naphthalene
91-20-3
0.059
5.6
Phenanthrene
85-01-8
0.059
5.6
Pyrene
129-00-0
0.067
8.2
Arsenic
7440-38-2
1.4
5.0 mg/l TCLP
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
F035
Wastewaters (except those that have not come into contact with process contaminants), process
residuals, preservative drippage, and spent formulations from wood preserving processes that
are generated at plants that use inorganic preservatives containing arsenic or chromium. This
listing does not include K001 bottom sediment sludge from the treatment of wastewater from
wood preserving processes that use creosote or pentachlorophenol.
Arsenic
7440-38-2
1.4
5.0 mg/l TCLP
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
F037
Petroleum refinery primary oil/water/solids separation sludge--Any sludge generated from the
gravitational separation of oil/water/solids during the storage or treatment of process
wastewaters and oily cooling wastewaters from petroleum refineries. Such sludges include, but
are not limited to, those generated in: oil/water/solids separators; tanks, and impoundments;
ditches, and other conveyances; sumps; and stormwater units receiving dry weather flow.
Sludge generated in stormwater units that do not receive dry weather flow, sludges generated
from non-contact once-through cooling waters segregated for treatment from other process or
319
oily cooling waters, sludges generated in aggressive biological treatment units as defined in 35
Ill. Adm. Code 721.131(b)(2) (including sludges generated in one or more additional units after
wastewaters have been treated in aggressive biological treatment units) and K051 wastes are not
included in this listing.
Acenaphthene
83-32-9
0.059
NA
Anthracene
120-12-7
0.059
3.4
Benzene
71-43-2
0.14
10
Benz(a)anthracene
56-55-3
0.059
3.4
Benzo(a)pyrene
50-32-8
0.061
3.4
bis(2-Ethylhexyl) phthalate
117-81-7
0.28
28
Chrysene
218-01-9
0.059
3.4
Di-n-butyl phthalate
84-74-2
0.057
28
Ethylbenzene
100-41-4
0.057
10
Fluorene
86-73-7
0.059
NA
Naphthalene
91-20-3
0.059
5.6
Phenanthrene
85-01-8
0.059
5.6
Phenol
108-95-2
0.039
6.2
Pyrene
129-00-0
0.067
8.2
Toluene
108-88-3
0.080
10
Xylenes-mixed isomers
(sum of o-, m-, and p-xylene
concentrations)
1330-20-7
0.32
30
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Cyanides (Total)
7
57-12-5
1.2
590
Lead
7439-92-1
0.69
NA
Nickel
7440-02-0
NA
11 mg/l TCLP
F038
Petroleum refinery secondary (emulsified) oil/water/solids separation sludge or float generated
from the physical or chemical separation of oil/water/solids in process wastewaters and oily
cooling wastewaters from petroleum refineries. Such wastes include, but are not limited to, all
sludges and floats generated in: induced air floatation (IAF) units, tanks, and impoundments,
and all sludges generated in DAF units. Sludges generated in stormwater units that do not
receive dry weather flow, sludges generated from non-contact once-through cooling waters
segregated for treatment from other process or oily cooling waters, sludges, and floats
generated in aggressive biological treatment units as defined in 35 Ill. Adm. Code 721.131(b)(2)
(including sludges and floats generated in one or more additional units after wastewaters have
been treated in aggressive biological units) and F037, K048, and K051 are not included in this
listing.
Benzene
71-43-2
0.14
10
Benzo(a)pyrene
50-32-8
0.061
3.4
bis(2-Ethylhexyl) phthalate
117-81-7
0.28
28
Chrysene
218-01-9
0.059
3.4
Di-n-butyl phthalate
84-74-2
0.057
28
Ethylbenzene
100-41-4
0.057
10
320
Fluorene
86-73-7
0.059
NA
Naphthalene
91-20-3
0.059
5.6
Phenanthrene
85-01-8
0.059
5.6
Phenol
108-95-2
0.039
6.2
Pyrene
129-00-0
0.067
8.2
Toluene
108-88-3
0.080
10
Xylenes-mixed isomers
(sum of o-, m-, and p-xylene
concentrations)
1330-20-7
0.32
30
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Cyanides (Total)
7
57-12-5
1.2
590
Lead
7439-92-1
0.69
NA
Nickel
7440-02-0
NA
11 mg/l TCLP
F039
Leachate (liquids that have percolated through land disposed wastes) resulting from the disposal
of more than one restricted waste classified as hazardous under Subpart D of this Part.
(Leachate resulting from the disposal of one or more of the following USEPA hazardous wastes
and no other hazardous wastes retains its USEPA hazardous waste numbers: F020, F021,
F022, F026, F027, or F028.).
Acenaphthylene
208-96-8
0.059
3.4
Acenaphthene
83-32-9
0.059
3.4
Acetone
67-64-1
0.28
160
Acetonitrile
75-05-8
5.6
NA
Acetophenone
96-86-2
0.010
9.7
2-Acetylaminofluorene
53-96-3
0.059
140
Acrolein
107-02-8
0.29
NA
Acrylonitrile
107-13-1
0.24
84
Aldrin
309-00-2
0.021
0.066
4-Aminobiphenyl
92-67-1
0.13
NA
Aniline
62-53-3
0.81
14
Anthracene
120-12-7
0.059
3.4
Aramite
140-57-8
0.36
NA
α
-BHC
319-84-6
0.00014
0.066
β
-BHC
319-85-7
0.00014
0.066
δ
-BHC
319-86-8
0.023
0.066
χ
-BHC
58-89-9
0.0017
0.066
Benzene
71-43-2
0.14
10
Benz(a)anthracene
56-55-3
0.059
3.4
Benzo(b)fluoranthene (difficult
to distinguish from benzo(k)-
fluoranthene)
205-99-2
0.11
6.8
Benzo(k)fluoranthene (difficult
to distinguish from benzo(b)-
fluoranthene)
207-08-9
0.11
6.8
321
Benzo(g,h,i)perylene
191-24-2
0.0055
1.8
Benzo(a)pyrene
50-32-8
0.061
3.4
Bromodichloromethane
75-27-4
0.35
15
Methyl bromide (Bromo-
methane)
74-83-9
0.11
15
4-Bromophenyl phenyl ether
101-55-3
0.055
15
n-Butyl alcohol
71-36-3
5.6
2.6
Butyl benzyl phthalate
85-68-7
0.017
28
2-sec-Butyl-4,6-dinitrophenol
(Dinoseb)
88-85-7
0.066
2.5
Carbon disulfide
75-15-0
3.8
NA
Carbon tetrachloride
56-23-5
0.057
6.0
Chlordane (
α
and
χ
isomers)
57-74-9
0.0033
0.26
p-Chloroaniline
106-47-8
0.46
16
Chlorobenzene
108-90-7
0.057
6.0
Chlorobenzilate
510-15-6
0.10
NA
2-Chloro-1,3-butadiene
126-99-8
0.057
NA
Chlorodibromomethane
124-48-1
0.057
15
Chloroethane
75-00-3
0.27
6.0
bis(2-Chloroethoxy)methane
111-91-1
0.036
7.2
bis(2-Chloroethyl)ether
111-44-4
0.033
6.0
Chloroform
67-66-3
0.046
6.0
bis(2-Chloroisopropyl)ether
39638-32-9
0.055
7.2
p-Chloro-m-cresol
59-50-7
0.018
14
Chloromethane (Methyl
chloride)
74-87-3
0.19
30
2-Chloronaphthalene
91-58-7
0.055
5.6
2-Chlorophenol
95-57-8
0.044
5.7
3-Chloropropylene
107-05-1
0.036
30
Chrysene
218-01-9
0.059
3.4
o-Cresol
95-48-7
0.11
5.6
m-Cresol
(difficult to distinguish from p-
cresol)
108-39-4
0.77
5.6
p-Cresol
(difficult to distinguish from m-
cresol)
106-44-5
0.77
5.6
Cyclohexanone
108-94-1
0.36
NA
1,2-Dibromo-3-chloropropane
96-12-8
0.11
15
Ethylene dibromide (1,2-
Dibromoethane)
106-93-4
0.028
15
Dibromomethane
74-95-3
0.11
15
2,4-D (2,4-Dichlorophenoxy-
acetic acid)
94-75-7
0.72
10
o,p'-DDD
53-19-0
0.023
0.087
322
p,p'-DDD
72-54-8
0.023
0.087
o,p'-DDE
3424-82-6
0.031
0.087
p,p'-DDE
72-55-9
0.031
0.087
o,p'-DDT
789-02-6
0.0039
0.087
p,p'-DDT
50-29-3
0.0039
0.087
Dibenz(a,h)anthracene
53-70-3
0.055
8.2
Dibenz(a,e)pyrene
192-65-4
0.061
NA
m-Dichlorobenzene
541-73-1
0.036
6.0
o-Dichlorobenzene
95-50-1
0.088
6.0
p-Dichlorobenzene
106-46-7
0.090
6.0
Dichlorodifluoromethane
75-71-8
0.23
7.2
1,1-Dichloroethane
75-34-3
0.059
6.0
1,2-Dichloroethane
107-06-2
0.21
6.0
1,1-Dichloroethylene
75-35-4
0.025
6.0
trans-1,2-Dichloroethylene
156-60-5
0.054
30
2,4-Dichlorophenol
120-83-2
0.044
14
2,6-Dichlorophenol
87-65-0
0.044
14
1,2-Dichloropropane
78-87-5
0.85
18
cis-1,3-Dichloropropylene
10061-01-5
0.036
18
trans-1,3-Dichloropropylene
10061-02-6
0.036
18
Dieldrin
60-57-1
0.017
0.13
Diethyl phthalate
84-66-2
0.20
28
2-4-Dimethyl phenol
105-67-9
0.036
14
Dimethyl phthalate
131-11-3
0.047
28
Di-n-butyl phthalate
84-74-2
0.057
28
1,4-Dinitrobenzene
100-25-4
0.32
2.3
4,6-Dinitro-o-cresol
534-52-1
0.28
160
2,4-Dinitrophenol
51-28-5
0.12
160
2,4-Dinitrotoluene
121-14-2
0.32
140
2,6-Dinitrotoluene
606-20-2
0.55
28
Di-n-octyl phthalate
117-84-0
0.017
28
Di-n-propylnitrosamine
621-64-7
0.40
14
1,4-Dioxane
123-91-1
12.0
170
Diphenylamine (difficult to
distinguish from diphenylnitros-
amine)
122-39-4
0.92
NA
Diphenylnitrosamine (difficult to
distinguish from diphenylamine)
86-30-6
0.92
NA
1,2-Diphenylhydrazine
122-66-7
0.087
NA
Disulfoton
298-04-4
0.017
6.2
Endosulfan I
939-98-8
0.023
0.066
Endosulfan II
33213-6-5
0.029
0.13
Endosulfan sulfate
1031-07-8
0.029
0.13
Endrin
72-20-8
0.0028
0.13
Endrin aldehyde
7421-93-4
0.025
0.13
323
Ethyl acetate
141-78-6
0.34
33
Ethyl cyanide (Propanenitrile)
107-12-0
0.24
360
Ethyl benzene
100-41-4
0.057
10
Ethyl ether
60-29-7
0.12
160
bis(2-Ethylhexyl) phthalate
117-81-7
0.28
28
Ethyl methacrylate
97-63-2
0.14
160
Ethylene oxide
75-21-8
0.12
NA
Famphur
52-85-7
0.017
15
Fluoranthene
206-44-0
0.068
3.4
Fluorene
86-73-7
0.059
3.4
Heptachlor
76-44-8
0.0012
0.066
Heptachlor epoxide
1024-57-3
0.016
0.066
Hexachlorobenzene
118-74-1
0.055
10
Hexachlorobutadiene
87-68-3
0.055
5.6
Hexachlorocyclopentadiene
77-47-4
0.057
2.4
HxCDDs (All Hexachloro-
dibenzo-p-dioxins)
NA
0.000063
0.001
HxCDFs (All Hexachloro-
dibenzofurans)
NA
0.000063
0.001
Hexachloroethane
67-72-1
0.055
30
Hexachloropropylene
1888-71-7
0.035
30
Indeno (1,2,3-c,d) pyrene
193-39-5
0.0055
3.4
Iodomethane
74-88-4
0.19
65
Isobutyl alcohol
78-83-1
5.6
170
Isodrin
465-73-6
0.021
0.066
Isosafrole
120-58-1
0.081
2.6
Kepone
143-50-8
0.0011
0.13
Methacrylonitrile
126-98-7
0.24
84
Methanol
67-56-1
5.6
NA
Methapyrilene
91-80-5
0.081
1.5
Methoxychlor
72-43-5
0.25
0.18
3-Methylcholanthrene
56-49-5
0.0055
15
4,4-Methylene bis(2-chloro-
aniline)
101-14-4
0.50
30
Methylene chloride
75-09-2
0.089
30
Methyl ethyl ketone
78-93-3
0.28
36
Methyl isobutyl ketone
108-10-1
0.14
33
Methyl methacrylate
80-62-6
0.14
160
Methyl methansulfonate
66-27-3
0.018
NA
Methyl parathion
298-00-0
0.014
4.6
Naphthalene
91-20-3
0.059
5.6
2-Naphthylamine
91-59-8
0.52
NA
p-Nitroaniline
100-01-6
0.028
28
Nitrobenzene
98-95-3
0.068
14
5-Nitro-o-toluidine
99-55-8
0.32
28
324
p-Nitrophenol
100-02-7
0.12
29
N-Nitrosodiethylamine
55-18-5
0.40
28
N-Nitrosodimethylamine
62-75-9
0.40
NA
N-Nitroso-di-n-butylamine
924-16-3
0.40
17
N-Nitrosomethylethylamine
10595-95-6
0.40
2.3
N-Nitrosomorpholine
59-89-2
0.40
2.3
N-Nitrosopiperidine
100-75-4
0.013
35
N-Nitrosopyrrolidine
930-55-2
0.013
35
Parathion
56-38-2
0.014
4.6
Total PCBs
(sum of all PCB isomers, or all
Aroclors)
1336-36-3
0.10
10
Pentachlorobenzene
608-93-5
0.055
10
PeCDDs (All Pentachloro-
dibenzo-p-dioxins)
NA
0.000063
0.001
PeCDFs (All Pentachloro-
dibenzofurans)
NA
0.000035
0.001
Pentachloronitrobenzene
82-68-8
0.055
4.8
Pentachlorophenol
87-86-5
0.089
7.4
Phenacetin
62-44-2
0.081
16
Phenanthrene
85-01-8
0.059
5.6
Phenol
108-95-2
0.039
6.2
Phorate
298-02-2
0.021
4.6
Phthalic anhydride
85-44-9
0.055
NA
Pronamide
23950-58-5
0.093
1.5
Pyrene
129-00-0
0.067
8.2
Pyridine
110-86-1
0.014
16
Safrole
94-59-7
0.081
22
Silvex (2,4,5-TP)
93-72-1
0.72
7.9
2,4,5-T
93-76-5
0.72
7.9
1,2,4,5-Tetrachlorobenzene
95-94-3
0.055
14
TCDDs (All Tetrachloro-
dibenzo-p-dioxins)
NA
0.000063
0.001
TCDFs (All Tetrachloro-
dibenzofurans)
NA
0.000063
0.001
1,1,1,2-Tetrachloroethane
630-20-6
0.057
6.0
1,1,2,2-Tetrachloroethane
79-34-6
0.057
6.0
Tetrachloroethylene
127-18-4
0.056
6.0
2,3,4,6-Tetrachlorophenol
58-90-2
0.030
7.4
Toluene
108-88-3
0.080
10
Toxaphene
8001-35-2
0.0095
2.6
Bromoform (Tribromomethane)
75-25-2
0.63
15
1,2,4-Trichlorobenzene
120-82-1
0.055
19
1,1,1-Trichloroethane
71-55-6
0.054
6.0
1,1,2-Trichloroethane
79-00-5
0.054
6.0
325
Trichloroethylene
79-01-6
0.054
6.0
Trichloromonofluoromethane
75-69-4
0.020
30
2,4,5-Trichlorophenol
95-95-4
0.18
7.4
2,4,6-Trichlorophenol
88-06-2
0.035
7.4
1,2,3-Trichloropropane
96-18-4
0.85
30
1,1,2-Trichloro-1,2,2-trifluoro-
ethane
76-13-1
0.057
30
tris(2,3-Dibromopropyl)
phosphate
126-72-7
0.11
NA
Vinyl chloride
75-01-4
0.27
6.0
Xylenes-mixed isomers
(sum of o-, m-, and p-xylene
concentrations)
1330-20-7
0.32
30
Antimony
7440-36-0
1.9
1.15 mg/l TCLP
Arsenic
7440-38-2
1.4
5.0 mg/l TCLP
Barium
7440-39-3
1.2
21 mg/l TCLP
Beryllium
7440-41-7
0.82
NA
Cadmium
7440-43-9
0.69
0.11 mg/l TCLP
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Cyanides (Total)
7
57-12-5
1.2
590
Cyanides (Amenable)
7
57-12-5
0.86
NA
Fluoride
16964-48-8
35
NA
Lead
7439-92-1
0.69
0.75 mg/l TCLP
Mercury
7439-97-6
0.15
0.025 mg/l TCLP
Nickel
7440-02-0
3.98
11 mg/l TCLP
Selenium
7782-49-2
0.82
5.7 mg/l TCLP
Silver
7440-22-4
0.43
0.14 mg/l TCLP
Sulfide
8496-25-8
14
NA
Thallium
7440-28-0
1.4
NA
Vanadium
7440-62-2
4.3
NA
K001
Bottom sediment sludge from the treatment of wastewaters from wood preserving processes that
use creosote or pentachlorophenol.
Naphthalene
91-20-3
0.059
5.6
Pentachlorophenol
87-86-5
0.089
7.4
Phenanthrene
85-01-8
0.059
5.6
Pyrene
129-00-0
0.067
8.2
Toluene
108-88-3
0.080
10
Xylenes-mixed isomers
(sum of o-, m-, and p-xylene
concentrations)
1330-20-7
0.32
30
Lead
7439-92-1
0.69
0.75 mg/l TCLP
326
K002
Wastewater treatment sludge from the production of chrome yellow and orange pigments.
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Lead
7439-92-1
0.69
0.75 mg/l TCLP
K003
Wastewater treatment sludge from the production of molybdate orange pigments.
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Lead
7439-92-1
0.69
0.75 mg/l TCLP
K004
Wastewater treatment sludge from the production of zinc yellow pigments.
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Lead
7439-92-1
0.69
0.75 mg/l TCLP
K005
Wastewater treatment sludge from the production of chrome green pigments.
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Lead
7439-92-1
0.69
0.75 mg/l TCLP
Cyanides (Total)
7
57-12-5
1.2
590
K006
Wastewater treatment sludge from the production of chrome oxide green pigments (anhydrous).
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Lead
7439-92-1
0.69
0.75 mg/l TCLP
K006
Wastewater treatment sludge from the production of chrome oxide green pigments (hydrated).
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Lead
7439-92-1
0.69
NA
K007
Wastewater treatment sludge from the production of iron blue pigments.
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Lead
7439-92-1
0.69
0.75 mg/l TCLP
Cyanides (Total)
7
57-12-5
1.2
590
K008
Oven residue from the production of chrome oxide green pigments.
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Lead
7439-92-1
0.69
0.75 mg/l TCLP
K009
Distillation bottoms from the production of acetaldehyde from ethylene.
Chloroform
67-66-3
0.046
6.0
327
K010
Distillation side cuts from the production of acetaldehyde from ethylene.
Chloroform
67-66-3
0.046
6.0
K011
Bottom stream from the wastewater stripper in the production of acrylonitrile.
Acetonitrile
75-05-8
5.6
38
Acrylonitrile
107-13-1
0.24
84
Acrylamide
79-06-1
19
23
Benzene
71-43-2
0.14
10
Cyanide (Total)
57-12-5
1.2
590
K013
Bottom stream from the acetonitrile column in the production of acrylonitrile.
Acetonitrile
75-05-8
5.6
38
Acrylonitrile
107-13-1
0.24
84
Acrylamide
79-06-1
19
23
Benzene
71-43-2
0.14
10
Cyanide (Total)
57-12-5
1.2
590
K014
Bottoms from the acetonitrile purification column in the production of acrylonitrile.
Acetonitrile
75-05-8
5.6
38
Acrylonitrile
107-13-1
0.24
84
Acrylamide
79-06-1
19
23
Benzene
71-43-2
0.14
10
Cyanide (Total)
57-12-5
1.2
590
K015
Still bottoms from the distillation of benzyl chloride.
Anthracene
120-12-7
0.059
3.4
Benzal chloride
98-87-3
0.055
6.0
Benzo(b)fluoranthene (difficult
to distinguish from benzo(k)-
fluoranthene)
205-99-2
0.11
6.8
Benzo(k)fluoranthene (difficult
to distinguish from benzo(b)-
fluoranthene)
207-08-9
0.11
6.8
Phenanthrene
85-01-8
0.059
5.6
Toluene
108-88-3
0.080
10
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Nickel
7440-02-0
3.98
11 mg/l TCLP
328
K016
Heavy ends or distillation residues from the production of carbon tetrachloride.
Hexachlorobenzene
118-74-1
0.055
10
Hexachlorobutadiene
87-68-3
0.055
5.6
Hexachlorocyclopentadiene
77-47-4
0.057
2.4
Hexachloroethane
67-72-1
0.055
30
Tetrachloroethylene
127-18-4
0.056
6.0
K017
Heavy ends (still bottoms) from the purification column in the production of epichlorohydrin.
bis(2-Chloroethyl)ether
111-44-4
0.033
6.0
1,2-Dichloropropane
78-87-5
0.85
18
1,2,3-Trichloropropane
96-18-4
0.85
30
K018
Heavy ends from the fractionation column in ethyl chloride production.
Chloroethane
75-00-3
0.27
6.0
Chloromethane
74-87-3
0.19
NA
1,1-Dichloroethane
75-34-3
0.059
6.0
1,2-Dichloroethane
107-06-2
0.21
6.0
Hexachlorobenzene
118-74-1
0.055
10
Hexachlorobutadiene
87-68-3
0.055
5.6
Hexachloroethane
67-72-1
0.055
30
Pentachloroethane
76-01-7
NA
6.0
1,1,1-Trichloroethane
71-55-6
0.054
6.0
K019
Heavy ends from the distillation of ethylene dichloride in ethylene dichloride production.
bis(2-Chloroethyl)ether
111-44-4
0.033
6.0
Chlorobenzene
108-90-7
0.057
6.0
Chloroform
67-66-3
0.046
6.0
p-Dichlorobenzene
106-46-7
0.090
NA
1,2-Dichloroethane
107-06-2
0.21
6.0
Fluorene
86-73-7
0.059
NA
Hexachloroethane
67-72-1
0.055
30
Naphthalene
91-20-3
0.059
5.6
Phenanthrene
85-01-8
0.059
5.6
1,2,4,5-Tetrachlorobenzene
95-94-3
0.055
NA
Tetrachloroethylene
127-18-4
0.056
6.0
1,2,4-Trichlorobenzene
120-82-1
0.055
19
1,1,1-Trichloroethane
71-55-6
0.054
6.0
K020
Heavy ends from the distillation of vinyl chloride in vinyl chloride monomer production.
1,2-Dichloroethane
107-06-2
0.21
6.0
329
1,1,2,2-Tetrachloroethane
79-34-6
0.057
6.0
Tetrachloroethylene
127-18-4
0.056
6.0
K021
Aqueous spent antimony catalyst waste from fluoromethanes production.
Carbon tetrachloride
56-23-5
0.057
6.0
Chloroform
67-66-3
0.046
6.0
Antimony
7440-36-0
1.9
1.15 mg/l TCLP
K022
Distillation bottom tars from the production of phenol or acetone from cumene.
Toluene
108-88-3
0.080
10
Acetophenone
96-86-2
0.010
9.7
Diphenylamine (difficult to
distinguish from diphenylnitros-
amine)
122-39-4
0.92
13
Diphenylnitrosamine (difficult to
distinguish from diphenylamine)
86-30-6
0.92
13
Phenol
108-95-2
0.039
6.2
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Nickel
7440-02-0
3.98
11 mg/l TCLP
K023
Distillation light ends from the production of phthalic anhydride from naphthalene.
Phthalic anhydride (measured as
Phthalic acid or Terephthalic
acid)
100-21-0
0.055
28
Phthalic anhydride (measured as
Phthalic acid or Terephthalic
acid)
85-44-9
0.055
28
K024
Distillation bottoms from the production of phthalic anhydride from naphthalene.
Phthalic anhydride (measured as
Phthalic acid or Terephthalic
acid)
100-21-0
0.055
28
Phthalic anhydride (measured as
Phthalic acid or Terephthalic
acid)
85-44-9
0.055
28
K025
Distillation bottoms from the production of nitrobenzene by the nitration of benzene.
NA
NA
LLEXT fb SSTRP
fb CARBN; or
CMBST
CMBST
330
K026
Stripping still tails from the production of methyl ethyl pyridines.
NA
NA
CMBST
CMBST
K027
Centrifuge and distillation residues from the toluene diisocyanate production.
NA
NA
CARBN; or
CMBST
CMBST
K028
Spent catalyst from the hydrochlorinator reactor in the production of 1,1,1-trichloroethane.
1,1-Dichloroethane
75-34-3
0.059
6.0
trans-1,2-Dichloroethylene
156-60-5
0.054
30
Hexachlorobutadiene
87-68-3
0.055
5.6
Hexachloroethane
67-72-1
0.055
30
Pentachloroethane
76-01-7
NA
6.0
1,1,1,2-Tetrachloroethane
630-20-6
0.057
6.0
1,1,2,2-Tetrachloroethane
79-34-6
0.057
6.0
Tetrachloroethylene
127-18-4
0.056
6.0
1,1,1-Trichloroethane
71-55-6
0.054
6.0
1,1,2-Trichloroethane
79-00-5
0.054
6.0
Cadmium
7440-43-9
0.69
NA
Chromium(Total)
7440-47-3
2.77
0.60 mg/l TCLP
Lead
7439-92-1
0.69
0.75 mg/l TCLP
Nickel
7440-02-0
3.98
11 mg/l TCLP
K029
Waste from the product steam stripper in the production of 1,1,1-trichloroethane.
Chloroform
67-66-3
0.046
6.0
1,2-Dichloroethane
107-06-2
0.21
6.0
1,1-Dichloroethylene
75-35-4
0.025
6.0
1,1,1-Trichloroethane
71-55-6
0.054
6.0
Vinyl chloride
75-01-4
0.27
6.0
K030
Column bodies or heavy ends from the combined production of trichloroethylene and
perchloroethylene.
o-Dichlorobenzene
95-50-1
0.088
NA
p-Dichlorobenzene
106-46-7
0.090
NA
Hexachlorobutadiene
87-68-3
0.055
5.6
Hexachloroethane
67-72-1
0.055
30
Hexachloropropylene
1888-71-7
NA
30
Pentachlorobenzene
608-93-5
NA
10
Pentachloroethane
76-01-7
NA
6.0
331
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
isomers)
57-74-9
0.0033
0.26
Heptachlor
76-44-8
0.0012
0.066
Heptachlor epoxide
1024-57-3
0.016
0.066
K033
Wastewater and scrub water from the chlorination of cyclopentadiene in the production of
chlordane.
Hexachlorocyclopentadiene
77-47-4
0.057
2.4
K034
Filter solids from the filtration of hexachlorocyclopentadiene in the production of chlordane.
Hexachlorocyclopentadiene
77-47-4
0.057
2.4
K035
Wastewater treatment sludges generated in the production of creosote.
Acenaphthene
83-32-9
NA
3.4
Anthracene
120-12-7
NA
3.4
Benz(a)anthracene
56-55-3
0.059
3.4
Benzo(a)pyrene
50-32-8
0.061
3.4
Chrysene
218-01-9
0.059
3.4
o-Cresol
95-48-7
0.11
5.6
m-Cresol
(difficult to distinguish from p-
cresol)
108-39-4
0.77
5.6
p-Cresol
(difficult to distinguish from m-
cresol)
106-44-5
0.77
5.6
Dibenz(a,h)anthracene
53-70-3
NA
8.2
Fluoranthene
206-44-0
0.068
3.4
Fluorene
86-73-7
NA
3.4
Indeno(1,2,3-cd)pyrene
193-39-5
NA
3.4
Naphthalene
91-20-3
0.059
5.6
Phenanthrene
85-01-8
0.059
5.6
Phenol
108-95-2
0.039
6.2
332
Pyrene
129-00-0
0.067
8.2
K036
Still bottoms from toluene reclamation distillaiton in the production of disulfoton.
Disulfoton
298-04-4
0.017
6.2
K037
Wastewater treatment sludges from the production of disulfoton.
Disulfoton
298-04-4
0.017
6.2
Toluene
108-88-3
0.080
10
K038
Wastewater from the washing and stripping of phorate production.
Phorate
298-02-2
0.021
4.6
K039
Filter cake from the filtration of diethylphosphorodithioic acid in the production of phorate.
NA
NA
CARBN; or
CMBST
CMBST
K040
Wastewater treatment sludge from the production of phorate.
Phorate
298-02-2
0.021
4.6
K041
Wastewater treatment sludge from the production of toxaphene.
Toxaphene
8001-35-2
0.0095
2.6
K042
Heavy ends or distillation residues from the distillation of tetrachlorobenzene in the production
of 2,4,5-T.
o-Dichlorobenzene
95-50-1
0.088
6.0
p-Dichlorobenzene
106-46-7
0.090
6.0
Pentachlorobenzene
608-93-5
0.055
10
1,2,4,5-Tetrachlorobenzene
95-94-3
0.055
14
1,2,4-Trichlorobenzene
120-82-1
0.055
19
K043
2,6-Dichlorophenol waste from the production of 2,4-D.
2,4-Dichlorophenol
120-83-2
0.044
14
2,6-Dichlorophenol
187-65-0
0.044
14
2,4,5-Trichlorophenol
95-95-4
0.18
7.4
2,4,6-Trichlorophenol
88-06-2
0.035
7.4
2,3,4,6-Tetrachlorophenol
58-90-2
0.030
7.4
Pentachlorophenol
87-86-5
0.089
7.4
333
Tetrachloroethylene
127-18-4
0.056
6.0
HxCDDs (All Hexachloro-
dibenzo-p-dioxins)
NA
0.000063
0.001
HxCDFs (All Hexachloro-
dibenzofurans)
NA
0.000063
0.001
PeCDDs (All Pentachloro-
dibenzo-p-dioxins)
NA
0.000063
0.001
PeCDFs (All Pentachloro-
dibenzofurans)
NA
0.000035
0.001
TCDDs (All Tetrachloro-
dibenzo-p-dioxins)
NA
0.000063
0.001
TCDFs (All Tetrachloro-
dibenzofurans)
NA
0.000063
0.001
K044
Wastewater treatment sludges from the manufacturing and processing of explosives.
NA
NA
DEACT
DEACT
K045
Spent carbon from the treatment of wastewater containing explosives.
NA
NA
DEACT
DEACT
K046
Wastewater treatment sludges from the manufacturing, formulation and loading of lead-based
initiating compounds.
Lead
7439-92-1
0.69
0.75 mg/l TCLP
K047
Pink or red water from TNT operations.
NA
NA
DEACT
DEACT
K048
Dissolved air flotation (DAF) float from the petroleum refining industry.
Benzene
71-43-2
0.14
10
Benzo(a)pyrene
50-32-8
0.061
3.4
bis(2-Ethylhexyl) phthalate
117-81-7
0.28
28
Chrysene
218-01-9
0.059
3.4
Di-n-butyl phthalate
84-74-2
0.057
28
Ethylbenzene
100-41-4
0.057
10
Fluorene
86-73-7
0.059
NA
Naphthalene
91-20-3
0.059
5.6
Phenanthrene
85-01-8
0.059
5.6
Phenol
108-95-2
0.039
6.2
Pyrene
129-00-0
0.067
8.2
Toluene
108-88-33
0.080
10
334
Xylenes-mixed isomers
(sum of o-, m-, and p-xylene
concentrations)
1330-20-7
0.32
30
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Cyanides (Total)
7
57-12-5
1.2
590
Lead
7439-92-1
0.69
NA
Nickel
7440-02-0
NA
11 mg/l TCLP
K049
Slop oil emulsion solids from the petroleum refining industry.
Anthracene
120-12-7
0.059
3.4
Benzene
71-43-2
0.14
10
Benzo(a)pyrene
50-32-8
0.061
3.4
bis(2-Ethylhexyl) phthalate
117-81-7
0.28
28
Carbon disulfide
75-15-0
3.8
NA
Chrysene
2218-01-9
0.059
3.4
2,4-Dimethylphenol
105-67-9
0.036
NA
Ethylbenzene
100-41-4
0.057
10
Naphthalene
91-20-3
0.059
5.6
Phenanthrene
85-01-8
0.059
5.6
Phenol
108-95-2
0.039
6.2
Pyrene
129-00-0
0.067
8.2
Toluene
108-88-3
0.080
10
Xylenes-mixed isomers
(sum of o-, m-, and p-xylene
concentrations)
1330-20-7
0.32
30
Cyanides (Total)
7
57-12-5
1.2
590
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Lead
7439-92-1
0.69
NA
Nickel
7440-02-0
NA
11 mg/l TCLP
K050
Heat exchanger bundle cleaning sludge from the petroleum refining industry.
Benzo(a)pyrene
50-32-8
0.061
3.4
Phenol
108-95-2
0.039
6.2
Cyanides (Total)
7
57-12-5
1.2
590
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Lead
7439-92-1
0.69
NA
Nickel
7440-02-0
NA
11 mg/l TCLP
K051
API separator sludge from the petroleum refining industry.
Acenaphthene
83-32-9
0.059
NA
Anthracene
120-12-7
0.059
3.4
Benz(a)anthracene
56-55-3
0.059
3.4
335
Benzene
71-43-2
0.14
10
Benzo(a)pyrene
50-32-8
0.061
3.4
bis(2-Ethylhexyl) phthalate
117-81-7
0.28
28
Chrysene
2218-01-9
0.059
3.4
Di-n-butyl phthalate
105-67-9
0.057
28
Ethylbenzene
100-41-4
0.057
10
Fluorene
86-73-7
0.059
NA
Naphthalene
91-20-3
0.059
5.6
Phenanthrene
85-01-8
0.059
5.6
Phenol
108-95-2
0.039
6.2
Pyrene
129-00-0
0.067
8.2
Toluene
108-88-3
0.08
10
Xylenes-mixed isomers
(sum of o-, m-, and p-xylene
concentrations)
1330-20-7
0.32
30
Cyanides (Total)
7
57-12-5
1.2
590
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Lead
7439-92-1
0.69
NA
Nickel
7440-02-0
NA
11 mg/l TCLP
K052
Tank bottoms (leaded) from the petroleum refining industry.
Benzene
71-43-2
0.14
10
Benzo(a)pyrene
50-32-8
0.061
3.4
o-Cresol
95-48-7
0.11
5.6
m-Cresol
(difficult to distinguish from p-
cresol)
108-39-4
0.77
5.6
p-Cresol
(difficult to distinguish from m-
cresol)
106-44-5
0.77
5.6
2,4-Dimethylphenol
105-67-9
0.036
NA
Ethylbenzene
100-41-4
0.057
10
Naphthalene
91-20-3
0.059
5.6
Phenanthrene
85-01-8
0.059
5.6
Phenol
108-95-2
0.039
6.2
Toluene
108-88-3
0.08
10
Xylenes-mixed isomers
(sum of o-, m-, and p-xylene
concentrations)
1330-20-7
0.32
30
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Cyanides (Total)
7
57-12-5
1.2
590
Lead
7439-92-1
0.69
NA
Nickel
7440-02-0
NA
11 mg/l TCLP
336
K060
Ammonia still lime sludge from coking operations.
Benzene
71-43-2
0.14
10
Benzo(a)pyrene
50-32-8
0.061
3.4
Naphthalene
91-20-3
0.059
5.6
Phenol
108-95-2
0.039
6.2
Cyanides (Total)
7
57-12-5
1.2
590
K061
Emission control dust or sludge from the primary production of steel in electric furnaces.
Antimony
7440-36-0
NA
1.15 mg/l TCLP
Arsenic
7440-38-2
NA
5.0 mg/l TCLP
Barium
7440-39-3
NA
21 mg/l TCLP
Beryllium
7440-41-7
NA
1.22 mg/l TCLP
Cadmium
7440-43-9
0.69
0.11 mg/l TCLP
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Lead
7439-92-1
0.69
0.75 mg/l TCLP
Mercury
7439-97-6
NA
0.025 mg/l TCLP
Nickel
7440-02-0
3.98
11 mg/l TCLP
Selenium
7782-49-2
NA
5.7 mg/l TCLP
Silver
7440-22-4
NA
0.14 mg/l TCLP
Thallium
7440-28-0
NA
0.20 mg/l TCLP
Zinc
7440-66-6
NA
4.3 mg/l TCLP
K062
Spent pickle liquor generated by steel finishing operations of facilities within the iron and steel
industry (SIC Codes 331 and 332).
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Lead
7439-92-1
0.69
0.75 mg/l TCLP
Nickel
7440-02-0
3.98
NA
K069
Emission control dust or sludge from secondary lead smelting. - Calcium sulfate (Low Lead)
Subcategory
Cadmium
7440-43-9
0.69
0.11 mg/l TCLP
Lead
7439-92-1
0.69
0.75 mg/l TCLP
K069
Emission control dust or sludge from secondary lead smelting. - Non-Calcium sulfate (High
Lead) Subcategory
NA
NA
NA
RLEAD
337
K071
K071 (Brine purification muds from the mercury cell process in chlorine production, where
separately prepurified brine is not used) nonwastewaters that are residues from RMERC.
Mercury
7439-97-6
NA
0.20 mg/l TCLP
K071
K071 (Brine purification muds from the mercury cell process in chlorine production, where
separately prepurified brine is not used) nonwastewaters that are not residues from RMERC.
Mercury
7439-97-6
NA
0.025 mg/l TCLP
K071
All K071 wastewaters.
Mercury
7439-97-6
0.15
NA
K073
Chlorinated hydrocarbon waste from the purification step of the diaphragm cell process using
graphite anodes in chlorine production.
Carbon tetrachloride
56-23-5
0.057
6.0
Chloroform
67-66-3
0.046
6.0
Hexachloroethane
67-72-1
0.055
30
Tetrachloroethylene
127-18-4
0.056
6.0
1,1,1-Trichloroethane
71-55-6
0.054
6.0
K083
Distillation bottoms from aniline production.
Aniline
62-53-3
0.81
14
Benzene
71-43-2
0.14
10
Cyclohexanone
108-94-1
0.36
NA
Diphenylamine
(difficult to distinguish from
diphenylnitrosamine)
122-39-4
0.92
13
Diphenylnitrosamine (difficult to
distinguish from diphenylamine)
86-30-6
0.92
13
Nitrobenzene
98-95-3
0.068
14
Phenol
108-95-2
0.039
6.2
Nickel
7440-02-0
3.98
11 mg/l TCLP
K084
Wastewater treatment sludges generated during the production of veterinary pharmaceuticals
from arsenic or organo-arsenic compounds.
Arsenic
7440-38-2
1.4
5.0 mg/l TCLP
K085
Distillation or fractionation column bottoms from the production of chlorobenzenes.
Benzene
71-43-2
0.14
10
338
Chlorobenzene
108-90-7
0.057
6.0
m-Dichlorobenzene
541-73-1
0.036
6.0
o-Dichlorobenzene
95-50-1
0.088
6.0
p-Dichlorobenzene
106-46-7
0.090
6.0
Hexachlorobenzene
118-74-1
0.055
10
Total PCBs
(sum of all PCB isomers, or all
Aroclors)
1336-36-3
0.10
10
Pentachlorobenzene
608-93-5
0.055
10
1,2,4,5-Tetrachlorobenzene
95-94-3
0.055
14
1,2,4-Trichlorobenzene
120-82-1
0.055
19
K086
Solvent wastes and sludges, caustic washes and sludges, or water washes and sludges from
cleaning tubs and equipment used in the formulation of ink from pigments, driers, soaps, and
stabilizers containing chromium and lead.
Acetone
67-64-1
0.28
160
Acetophenone
96-86-2
0.010
9.7
bis(2-Ethylhexyl) phthalate
117-81-7
0.28
28
n-Butyl alcohol
71-36-3
5.6
2.6
Butylbenzyl phthalate
85-68-7
0.017
28
Cyclohexanone
108-94-1
0.36
NA
o-Dichlorobenzene
95-50-1
0.088
6.0
Diethyl phthalate
84-66-2
0.20
28
Dimethyl phthalate
131-11-3
0.047
28
Di-n-butyl phthalate
84-74-2
0.057
28
Di-n-octyl phthalate
117-84-0
0.017
28
Ethyl acetate
141-78-6
0.34
33
Ethylbenzene
100-41-4
0.057
10
Methanol
67-56-1
5.6
NA
Methyl ethyl ketone
78-93-3
0.28
36
Methyl isobutyl ketone
108-10-1
0.14
33
Methylene chloride
75-09-2
0.089
30
Naphthalene
91-20-3
0.059
5.6
Nitrobenzene
98-95-3
0.068
14
Toluene
108-88-3
0.080
10
1,1,1-Trichloroethane
71-55-6
0.054
6.0
Trichloroethylene
79-01-6
0.054
6.0
Xylenes-mixed isomers
(sum of o-, m-, and p-xylene
concentrations)
1330-20-7
0.32
30
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Cyanides (Total)
7
57-12-5
1.2
590
Lead
7439-92-1
0.69
0.75 mg/l TCLP
339
K087
Decanter tank tar sludge from coking operations.
Acenaphthylene
208-96-8
0.059
3.4
Benzene
71-43-2
0.14
10
Chrysene
218-01-9
0.059
3.4
Fluoranthene
206-44-0
0.068
3.4
Indeno(1,2,3-cd)pyrene
193-39-5
0.0055
3.4
Naphthalene
91-20-3
0.059
5.6
Phenanthrene
85-01-8
0.059
5.6
Toluene
108-88-3
0.080
10
Xylenes-mixed isomers
(sum of o-, m-, and p-xylene
concentrations)
1330-20-7
0.32
30
Lead
7439-92-1
0.69
0.75 mg/l TCLP
K088
Spent potliners from primary aluminum reduction.
Acenaphthene
83-32-9
0.059
3.4
Anthracene
120-12-7
0.059
3.4
Benz(a)anthracene
56-55-3
0.059
3.4
Benzo(a)pyrene
50-32-8
0.061
3.4
Benzo(b)fluoranthene
205-99-2
0.11
6.8
Benzo(k)fluoranthene
207-08-9
0.11
6.8
Benzo(g,h,i)perylene
191-24-2
0.0055
1.8
Chrysene
218-01-9
0.059
3.4
Dibenz(a,h)anthracene
53-70-3
0.055
8.2
Fluoranthene
206-44-0
0.068
3.4
Indeno(1,2,3-c,d)pyrene
193-39-5
0.0055
3.4
Phenanthrene
85-01-8
0.059
5.6
Pyrene
129-00-0
0.067
8.2
Antimony
7440-36-0
1.9
1.15 mg/l TCLP
Arsenic
7440-38-2
1.4
26.1 mg/l TCLP
Barium
7440-39-3
1.2
21 mg/l TCLP
Beryllium
7440-41-7
0.82
1.22 mg/l TCLP
Cadmium
7440-43-9
0.69
0.11 mg/l TCLP
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Lead
7439-92-1
0.69
0.75 mg/l TCLP
Mercury
7439-97-6
0.15
0.025 mg/l TCLP
Nickel
7440-02-0
3.98
11 mg/l TCLP
Selenium
7782-49-2
0.82
5.7 mg/l TCLP
Silver
7440-22-4
0.43
0.14 mg/l TCLP
Cyanide (Total)
7
57-12-5
1.2
590
Cyanide (Amenable)
7
57-12-5
0.86
30
Fluoride
16984-48-8
35
48 mg/l TCLPNA
340
K093
Distillation light ends from the production of phthalic anhydride from ortho-xylene.
Phthalic anhydride (measured as
Phthalic acid or Terephthalic
acid)
100-21-0
0.055
28
Phthalic anhydride (measured as
Phthalic acid or Terephthalic
acid)
85-44-9
0.055
28
K094
Distillation bottoms from the production of phthalic anhydride from ortho-xylene.
Phthalic anhydride (measured as
Phthalic acid or Terephthalic
acid)
100-21-0
0.055
28
Phthalic anhydride (measured as
Phthalic acid or Terephthalic
acid)
85-44-9
0.055
28
K095
Distillation bottoms from the production of 1,1,1-trichloroethane.
Hexachloroethane
67-72-1
0.055
30
Pentachloroethane
76-01-7
0.055
6.0
1,1,1,2-Tetrachloroethane
630-20-6
0.057
6.0
1,1,2,2-Tetrachloroethane
79-34-6
0.057
6.0
Tetrachloroethylene
127-18-4
0.056
6.0
1,1,2-Trichloroethane
79-00-5
0.054
6.0
Trichloroethylene
79-01-6
0.054
6.0
K096
Heavy ends from the heavy ends column from the production of 1,1,1-trichloroethane.
m-Dichlorobenzene
541-73-1
0.036
6.0
Pentachloroethane
76-01-7
0.055
6.0
1,1,1,2-Tetrachloroethane
630-20-6
0.057
6.0
1,1,2,2-Tetrachloroethane
79-34-6
0.057
6.0
Tetrachloroethylene
127-18-4
0.056
6.0
1,2,4-Trichlorobenzene
120-82-1
0.055
19
1,1,2-Trichloroethane
79-00-5
0.054
6.0
Trichloroethylene
79-01-6
0.054
6.0
K097
Vacuum stripper discharge from the chlordane chlorinator in the production of chlordane.
Chlordane (
α
and
χ
isomers)
57-74-9
0.0033
0.26
Heptachlor
76-44-8
0.0012
0.066
Heptachlor epoxide
1024-57-3
0.016
0.066
Hexachlorocyclopentadiene
77-47-4
0.057
2.4
341
K098
Untreated process wastewater from the production of toxaphene.
Toxaphene
8001-35-2
0.0095
2.6
K099
Untreated wastewater from the production of 2,4-D.
2,4-Dichlorophenoxyacetic acid
94-75-7
0.72
10
HxCDDs (All Hexachloro-
dibenzo-p-dioxins)
NA
0.000063
0.001
HxCDFs (All Hexachloro-
dibenzofurans)
NA
0.000063
0.001
PeCDDs (All Pentachloro-
dibenzo-p-dioxins)
NA
0.000063
0.001
PeCDFs (All Pentachloro-
dibenzofurans)
NA
0.000035
0.001
TCDDs (All Tetrachloro-
dibenzo-p-dioxins)
NA
0.000063
0.001
TCDFs (All Tetrachloro-
dibenzofurans)
NA
0.000063
0.001
K100
Waste leaching solution from acid leaching of emission control dust or sludge from secondary
lead smelting.
Cadmium
7440-43-9
0.69
0.11 mg/l TCLP
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Lead
7439-92-1
0.69
0.75 mg/l TCLP
K101
Distillation tar residues from the distillation of aniline-based compounds in the production of
veterinary pharmaceuticals from arsenic or organo-arsenic compounds.
o-Nitroaniline
88-74-4
0.27
14
Arsenic
7440-38-2
1.4
5.0 mg/l TCLP
Cadmium
7440-43-9
0.69
NA
Lead
7439-92-1
0.69
NA
Mercury
7439-97-6
0.15
NA
K102
Residue from the use of activated carbon for decolorization in the production of veterinary
pharmaceuticals from arsenic or organo-arsenic compounds.
o-Nitrophenol
88-75-5
0.028
13
Arsenic
7440-38-2
1.4
5.0 mg/l TCLP
Cadmium
7440-43-9
0.69
NA
Lead
7439-92-1
0.69
NA
Mercury
7439-97-6
0.15
NA
342
K103
Process residues from aniline extraction from the production of aniline.
Aniline
62-53-3
0.81
14
Benzene
71-43-2
0.14
10
2,4-Dinitrophenol
51-28-5
0.12
160
Nitrobenzene
98-95-3
0.068
14
Phenol
108-95-2
0.039
6.2
K104
Combined wastewater streams generated from nitrobenzene or aniline production.
Aniline
62-53-3
0.81
14
Benzene
71-43-2
0.14
10
2,4-Dinitrophenol
51-28-5
0.12
160
Nitrobenzene
98-95-3
0.068
14
Phenol
108-95-2
0.039
6.2
Cyanides (Total)
7
57-12-5
1.2
590
K105
Separated aqueous stream from the reactor product washing step in the production of chloro-
benzenes.
Benzene
71-43-2
0.14
10
Chlorobenzene
108-90-7
0.057
6.0
2-Chlorophenol
95-57-8
0.044
5.7
o-Dichlorobenzene
95-50-1
0.088
6.0
p-Dichlorobenzene
106-46-7
0.090
6.0
Phenol
108-95-2
0.039
6.2
2,4,5-Trichlorophenol
95-95-4
0.18
7.4
2,4,6-Trichlorophenol
88-06-2
0.035
7.4
K106
K106 (wastewater treatment sludge from the mercury cell process in chlorine production)
nonwastewaters that contain greater than or equal to 260 mg/kg total mercury.
Mercury
7439-97-6
NA
RMERC
K106
K106 (wastewater treatment sludge from the mercury cell process in chlorine production)
nonwastewaters that contain less than 260 mg/kg total mercury that are residues from RMERC.
Mercury
7439-97-6
NA
0.20 mg/l TCLP
K106
Other K106 nonwastewaters that contain less than 260 mg/kg total mercury and are not residues
from RMERC.
Mercury
7439-97-6
NA
0.025 mg/l TCLP
343
K106
All K106 wastewaters.
Mercury
7439-97-6
0.15
NA
K107
Column bottoms from product separation from the production of 1,1-dimethylhydrazine
(UDMH) from carboxylic acid hydrazides.
NA
NA
CMBST; or
CHOXD fb
CARBN; or
BIODG fb
CARBN
CMBST
K108
Condensed column overheads from product separation and condensed reactor vent gases from
the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.
NA
NA
CMBST; or
CHOXD fb
CARBN; or
BIODG fb
CARBN
CMBST
K109
Spent filter cartridges from product purification from the production of 1,1-dimethylhydrazine
(UDMH) from carboxylic acid hydrazides.
NA
NA
CMBST; or
CHOXD fb
CARBN; or
BIODG fb
CARBN
CMBST
K110
Condensed column overheads from intermediate separation from the production of 1,1-
dimethylhydrazine (UDMH) from carboxylic acid hydrazides.
NA
NA
CMBST; or
CHOXD fb
CARBN; or
BIODG fb
CARBN
CMBST
K111
Product washwaters from the production of dinitrotoluene via nitration of toluene
2,4-Dinitrotoluene
121-1-1
0.32
140
2,6-Dinitrotoluene
606-20-2
0.55
28
344
K112
Reaction by-product water from the drying column in the production of toluenediamine via
hydrogenation of dinitrotoluene.
NA
NA
CMBST; or
CHOXD fb
CARBN; or
BIODG fb
CARBN
CMBST
K113
Condensed liquid light ends from the purification of toluenediamine in the production of
toluenediamine via hydrogenation of dinitrotoluene.
NA
NA
CARBN; or
CMBST
CMBST
K114
Vicinals from the purification of toluenediamine in the production of toluenediamine via hydro-
genation of dinitrotoluene.
NA
NA
CARBN; or
CMBST
CMBST
K115
Heavy ends from the purification of toluenediamine in the production of toluenediamine via
hydrogenation of dinitrotoluene.
Nickel
7440-02-0
3.98
11 mg/l TCLP
NA
NA
CARBN; or
CMBST
CMBST
K116
Organic condensate from the solvent recovery column in the production of toluene diisocyanate
via phosgenation of toluenediamine.
NA
NA
CARBN; or
CMBST
CMBST
K117
Wastewater from the reactor vent gas scrubber in the production of ethylene dibromide via
bromination of ethene.
Methyl bromide (Bromo-
methane)
74-83-9
0.11
15
Chloroform
67-66-3
0.046
6.0
Ethylene dibromide (1,2-
Dibromoethane)
106-93-4
0.028
15
K118
Spent absorbent solids from purification of ethylene dibromide in the production of ethylene
345
dibromide via bromination of ethene.
Methyl bromide (Bromo-
methane)
74-83-9
0.11
15
Chloroform
67-66-3
0.046
6.0
Ethylene dibromide (1,2-
Dibromoethane)
106-93-4
0.028
15
K123
Process wastewater (including supernates, filtrates, and washwaters) from the production of
ethylenebisdithiocarbamic acid and its salts.
NA
NA
CMBST; or
CHOXD fb
(BIODG or
CARBN)
CMBST
K124
Reactor vent scrubber water from the production of ethylenebisdithiocarbamic acid and its salts.
NA
NA
CMBST; or
CHOXD fb
(BIODG or
CARBN)
CMBST
K125
Filtration, evaporation, and centrifugation solids from the production of ethylenebisdithio-
carbamic acid and its salts.
NA
NA
CMBST; or
CHOXD fb
(BIODG or
CARBN)
CMBST
K126
Baghouse dust and floor sweepings in milling and packaging operations from the production or
formulation of ethylenebisdithiocarbamic acid and its salts.
NA
NA
CMBST; or
CHOXD fb
(BIODG or
CARBN)
CMBST
K131
Wastewater from the reactor and spent sulfuric acid from the acid dryer from the production of
methyl bromide.
Methyl bromide (Bromo-
methane)
74-83-9
0.11
15
346
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
0.11
15
Chloroform
67-66-3
0.046
6.0
Ethylene dibromide (1,2-
Dibromoethane)
106-93-4
0.028
15
K140
Floor sweepings, off-specification product, and spent filter media from the production of 2,4,6-
tribromophenol.
2,4,6-Tribromophenol
118-79-6
0.035
7.4
K141
Process residues from the recovery of coal tar, including, but not limited to, collecting sump
residues from the production of coke or the recovery of coke by-products produced from coal.
This listing does not include K087 (decanter tank tar sludge from coking operations).
Benzene
71-43-2
0.14
10
Benz(a)anthracene
56-55-3
0.059
3.4
Benzo(a)pyrene
50-2-8
0.061
3.4
Benzo(b)fluoranthene (difficult
to distinguish from benzo(k)-
fluoranthene)
205-99-2
0.11
6.8
Benzo(k)fluoranthene (difficult
to distinguish from benzo(b)-
fluoranthene)
207-08-9
0.11
6.8
Chrysene
218-01-9
0.059
3.4
Dibenz(a,h)anthracene
53-70-3
0.055
8.2
Indeno(1,2,3-cd)pyrene
193-39-5
0.0055
3.4
K142
Tar storage tank residues from the production of coke from coal or from the recovery of coke
by-products produced from coal.
Benzene
71-43-2
0.14
10
Benz(a)anthracene
56-55-3
0.059
3.4
Benzo(a)pyrene
50-32-8
0.061
3.4
Benzo(b)fluoranthene (difficult
to distinguish from benzo(k)-
fluoranthene)
205-99-2
0.11
6.8
347
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
Ideno(1,2,3-cd)pyrene
Indeno(1,2,3-cd)pyrene
193-39-5
0.0055
3.4
K143
Process residues from the recovery of light oil, including, but not limited to, those generated in
stills, decanters, and wash oil recovery units from the recovery of coke by-products produced
from coal.
Benzene
71-43-2
0.14
10
Benz(a)anthracene
56-55-3
0.059
3.4
Benzo(a)pyrene
50-32-8
0.061
3.4
Benzo(b)fluoranthene (difficult
to distinguish from benzo(k)-
fluoranthene)
205-99-2
0.11
6.8
Benzo(k)fluoranthene (difficult
to distinguish from benzo(b)-
fluoranthene)
207-08-9
0.11
6.8
Chrysene
218-01-9
0.059
3.4
K144
Wastewater sump residues from light oil refining, including, but not limited to, intercepting or
contamination sump sludges from the recovery of coke by-products produced from coal.
Benzene
71-43-2
0.14
10
Benz(a)anthracene
56-55-3
0.059
3.4
Benzo(a)pyrene
50-32-8
0.061
3.4
Benzo(b)fluoranthene (difficult
to distinguish from benzo(k)-
fluoranthene)
205-99-2
0.11
6.8
Benzo(k)fluoranthene (difficult
to distinguish from benzo(b)-
fluoranthene)
207-08-9
0.11
6.8
Chrysene
218-01-9
0.059
3.4
Dibenz(a,h)anthracene
53-70-3
0.055
8.2
K145
Residues from naphthalene collection and recovery operations from the recovery of coke by-
products produced from coal.
Benzene
71-43-2
0.14
10
Benz(a)anthracene
56-55-3
0.059
3.4
Benzo(a)pyrene
50-32-8
0.061
3.4
Chrysene
218-01-9
0.059
3.4
348
Dibenz(a,h)anthracene
53-70-3
0.055
8.2
Naphthalene
91-20-3
0.059
5.6
K147
Tar storage tank residues from coal tar refining.
Benzene
71-43-2
0.14
10
Benz(a)anthracene
56-55-3
0.059
3.4
Benzo(a)pyrene
50-32-8
0.061
3.4
Benzo(b)fluoranthene (difficult
to distinguish from benzo(k)-
fluoranthene)
205-99-2
0.11
6.8
Benzo(k)fluoranthene (difficult
to distinguish from benzo(b)-
fluoranthene)
207-08-9
0.11
6.8
Chrysene
218-01-9
0.059
3.4
Dibenz(a,h)anthracene
53-70-3
0.055
8.2
Indeno(1,2,3-cd)pyrene
193-39-5
0.0055
3.4
K148
Residues from coal tar distillation, including, but not limited to, still bottoms.
Benz(a)anthracene
56-55-3
0.059
3.4
Benzo(a)pyrene
50-32-8
0.061
3.4
Benzo(b)fluoranthene (difficult
to distinguish from benzo(k)-
fluoranthene)
205-99-2
0.11
6.8
Benzo(k)fluoranthene (difficult
to distinguish from benzo(b)-
fluoranthene)
207-08-9
0.11
6.8
Chrysene
218-01-9
0.059
3.4
Dibenz(a,h)anthracene
53-70-3
0.055
8.2
Indeno(1,2,3-cd)pyrene
193-39-5
0.0055
3.4
K149
Distillation bottoms from the production of
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
0.057
6.0
Chloroform
67-66-3
0.046
6.0
Chloromethane
74-87-3
0.19
30
p-Dichlorobenzene
106-46-7
0.090
6.0
Hexachlorobenzene
118-74-1
0.055
10
Pentachlorobenzene
608-93-5
0.055
10
1,2,4,5-Tetrachlorobenzene
95-94-3
0.055
14
Toluene
108-88-3
0.080
10
349
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.
Carbon tetrachloride
56-23-5
0.057
6.0
Chloroform
67-66-3
0.046
6.0
Chloromethane
74-87-3
0.19
30
p-Dichlorobenzene
106-46-7
0.090
6.0
Hexachlorobenzene
118-74-1
0.055
10
Pentachlorobenzene
608-93-5
0.055
10
1,2,4,5-Tetrachlorobenzene
95-94-3
0.055
14
1,1,2,2- Tetrachloroethane
79-34-5
0.057
6.0
Tetrachloroethylene
127-18-4
0.056
6.0
1,2,4-Trichlorobenzene
120-82-1
0.055
19
K151
Wastewater treatment sludges, excluding neutralization and biological sludges, generated during
the treatment of wastewaters from the production of
α
- (or methyl-) chlorinated toluenes, ring-
chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional
groups.
Benzene
71-43-2
0.14
10
Carbon tetrachloride
56-23-5
0.057
6.0
Chloroform
67-66-3
0.046
6.0
Hexachlorobenzene
118-74-1
0.055
10
Pentachlorobenzene
608-93-5
0.055
10
1,2,4,5-Tetrachlorobenzene
95-94-3
0.055
14
Tetrachloroethylene
127-18-4
0.056
6.0
Toluene
108-88-3
0.080
10
K156
Organic waste (including heavy ends, still bottoms, light ends, spent solvents, filtrates, and
decantates) from the production of carbamates and carbamoyl oximes.
10
Acetonitrile
75-05-8
5.6
1.8
Acetophenone
96-86-2
0.010
9.7
Aniline
62-53-3
0.81
14
Benomyl
17804-35-2
0.056
1.4
Benzene
71-43-2
0.14
10
Carbaryl
63-25-21
0.006
0.14
Carbenzadim
10605-21-7
0.056
1.4
Carbofuran
1563-66-2
0.006
0.14
Carbosulfan
55285-14-8
0.028
1.4
Chlorobenzene
108-90-7
0.057
6.0
Chloroform
67-66-3
0.046
6.0
o-Dichlorobenzene
95-50-1
0.088
6.0
350
Methomyl
16752-77-5
0.028
0.14
Methylene chloride
75-09-2
0.089
30
Methyl ethyl ketone
78-93-3
0.28
36
Naphthalene
91-20-3
0.059
5.6
Phenol
108-95-2
0.039
6.2
Pyridine
110-86-1
0.014
16
Toluene
108-88-3
0.080
10
Triethylamine
121-44-8
0.081
1.5
K157
Wastewaters (including scrubber waters, condenser waters, washwaters, and separation waters)
from the production of carbamates and carbamoyl oximes.
Carbon tetrachloride
56-23-5
0.057
6.0
Chloroform
67-66-3
0.046
6.0
Chloromethane
74-87-3
0.19
30
Methomyl
16752-77-5
0.028
0.14
Methylene chloride
75-09-2
0.089
30
Methyl ethyl ketone
78-93-3
0.28
36
Pyridine
110-86-1
0.014
16
Triethylamine
121-44-8
0.081
1.5
K158
Baghouse dusts and filter/separation solids from the production of carbamates and carbamoyl
oximes.
Benomyl
17804-35-2
0.056
1.4
Benzene
71-43-2
0.14
10
Carbenzadim
10605-21-7
0.056
1.4
Carbofuran
1563-66-2
0.006
0.14
Carbosulfan
55285-14-8
0.028
1.4
Chloroform
67-66-3
0.046
6.0
Methylene chloride
75-09-2
0.089
30
Phenol
108-95-2
0.039
6.2
K159
Organics from the treatment of thiocarbamate wastes.
10
Benzene
71-43-2
0.14
10
Butylate
2008-41-5
0.042
1.4
EPTC (Eptam)
759-94-4
0.042
1.4
Molinate
2212-67-1
0.042
1.4
Pebulate
1114-71-2
0.042
1.4
Vernolate
1929-77-7
0.042
1.4
351
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
5.0
11
Carbon disulfide
75-15-0
3.8
4.8
11
Dithiocarbamates (total)
137-30-4
0.028
28
Lead
7439-92-1
0.69
0.75
11
Nickel
7440-02-0
3.98
11
11
Selenium
7782-49-2
0.82
5.7
11
K169
Crude oil tank sediment from petroleum refining operations.
Benz(a)anthracene
56-55-3
0.059
3.4
Benzene
71-43-2
0.14
10
Benzo(g,h,i)perylene
191-24-2
0.0055
1.8
Chrysene
218-01-9
0.059
3.4
Ethyl benzene
100-41-4
0.057
10
Fluorene
86-73-7
0.059
3.4
Naphthalene
91-20-3
0.059
5.6
Phenanthrene
81-05-8
0.059
5.6
Pyrene
129-00-0
0.067
8.2
Toluene (Methyl Benzene)
108-88-3
0.080
10
Xylene(s) Xylenes (Total)
1330-20-7
0.32
30
K170
Clarified slurry oil sediment from petroleum refining operations.
Benz(a)anthracene
56-55-3
0.059
3.4
Benzene
71-43-2
0.14
10
Benzo(g,h,i)perylene
191-24-2
0.0055
1.8
Chrysene
218-01-9
0.059
3.4
Dibenz(a,h)anthracene
53-70-3
0.055
8.2
Ethyl benzene
100-41-4
0.057
10
Fluorene
86-73-7
0.059
3.4
Indeno(1,2,3,-cd)pyrene
193-39-5
0.0055
3.4
Naphthalene
91-20-3
0.059
5.6
Phenanthrene
81-05-8
0.059
5.6
Pyrene
129-00-0
0.067
8.2
Toluene (Methyl Benzene)
108-88-3
0.080
10
Xylene(s) Xylenes (Total
1330-20-7
0.32
30
K171
Spent hydrotreating catalyst from petroleum refining operations, including guard beds used to
desulfurize feeds to other catalytic reactors. (This listing does not include inert support media.)
Benz(a)anthracene
56-55-3
0.059
3.4
352
Benzene
71-43-2
0.14
10
Chrysene
218-01-9
0.059
3.4
Ethyl benzene
100-41-4
0.057
10
Naphthalene
91-20-3
0.059
5.6
Phenanthrene
81-05-8
0.059
5.6
Pyrene
129-00-0
0.067
8.2
Toluene (Methyl Benzene)
108-88-3
0.080
10
Xylene(s) Xylenes (Total)
1330-20-7
0.32
30
Arsenic
7740-38-2
1.4
5 mg/L mg/l
TCLP
Nickel
7440-02-0
3.98
11.0 mg/L mg/l
TCLP
Vanadium
7440-62-2
4.3
1.6 mg/L mg/l
TCLP
Reactive sulfides
NA
DEACT
DEACT
K172
Spent hydrorefining catalyst from petroleum refining operations, including guard beds used to
desulfurize feeds to other catalytic reactors. (This listing does not include inert support media.)
Benzene
71-43-2
0.14
10
Ethyl benzene
100-41-4
0.057
10
Toluene (Methyl Benzene)
108-88-3
0.080
10
Xylene(s) Xylenes (Total)
1330-20-7
0.32
30
Antimony
7740-36-0
1.9
1.15 mg/L mg/l
TCLP
Arsenic
7740-38-2
1.4
5 mg/L mg/l
TCLP
Nickel
7440-02-0
3.98
11.0 mg/L mg/l
TCLP
Vanadium
7440-62-2
4.3
1.6 mg/L mg/l
TCLP
Reactive Sulfides
NA
DEACT
DEACT
P001
Warfarin, & salts, when present at concentrations greater than 0.3 percent
Warfarin
81-81-2
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
353
P002
1-Acetyl-2-thiourea
1-Acetyl-2-thiourea
591-08-2
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
P003
Acrolein
Acrolein
107-02-8
0.29
CMBST
P004
Aldrin
Aldrin
309-00-2
0.021
0.066
P005
Allyl alcohol
Allyl alcohol
107-18-6
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
P006
Aluminum phosphide
Aluminum phosphide
20859-73-8
CHOXD;
CHRED; or
CMBST
CHOXD;
CHRED; or
CMBST
P007
5-Aminomethyl-3-isoxazolol
5-Aminomethyl-3-isoxazolol
2763-96-4
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
P008
4-Aminopyridine
4-Aminopyridine
504-24-5
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
354
P009
Ammonium picrate
Ammonium picrate
131-74-8
CHOXD;
CHRED;
CARBN; BIODG;
or CMBST
CHOXD;
CHRED; or
CMBST
P010
Arsenic acid
Arsenic
7440-38-2
1.4
5.0 mg/l TCLP
P011
Arsenic pentoxide
Arsenic
7440-38-2
1.4
5.0 mg/l TCLP
P012
Arsenic trioxide
Arsenic
7440-38-2
1.4
5.0 mg/l TCLP
P013
Barium cyanide
Barium
7440-39-3
NA
21 mg/l TCLP
Cyanides (Total)
7
57-12-5
1.2
590
Cyanides (Amenable)
7
57-12-5
0.86
30
P014
Thiophenol (Benzene thiol)
Thiophenol (Benzene thiol)
108-98-5
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
P015
Beryllium dust
Beryllium
7440-41-7
RMETL;or
RTHRM
RMETL; or
RTHRM
P016
Dichloromethyl ether (Bis(chloromethyl)ether)
Dichloromethyl ether
542-88-1
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
355
P017
Bromoacetone
Bromoacetone
598-31-2
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
P018
Brucine
Brucine
357-57-3
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
P020
2-sec-Butyl-4,6-dinitrophenol (Dinoseb)
2-sec-Butyl-4,6-dinitrophenol
(Dinoseb)
88-85-7
0.066
2.5
P021
Calcium cyanide
Cyanides (Total)
7
57-12-5
1.2
590
Cyanides (Amenable)
7
57-12-5
0.86
30
P022
Carbon disulfide
Carbon disulfide
75-15-0
3.8
CMBST
Carbon disulfide; alternate
6
standard for nonwastewaters
only
75-15-0
NA
4.8 mg/l TCLP
P023
Chloroacetaldehyde
Chloroacetaldehyde
107-20-0
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
P024
p-Chloroaniline
p-Chloroaniline
106-47-8
0.46
16
356
P026
1-(o-Chlorophenyl)thiourea
1-(o-Chlorophenyl)thiourea
5344-82-1
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
P027
3-Chloropropionitrile
3-Chloropropionitrile
542-76-7
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
P028
Benzyl chloride
Benzyl chloride
100-44-7
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
P029
Copper cyanide
Cyanides (Total)
7
57-12-5
1.2
590
Cyanides (Amenable)
7
57-12-5
0.86
30
P030
Cyanides (soluble salts and complexes)
Cyanides (Total)
7
57-12-5
1.2
590
Cyanides (Amenable)
7
57-12-5
0.86
30
P031
Cyanogen
Cyanogen
460-19-5
CHOXD;
WETOX; or
CMBST
CHOXD;
WETOX; or
CMBST
P033
Cyanogen chloride
Cyanogen chloride
506-77-4
CHOXD;
WETOX; or
CMBST
CHOXD;
WETOX; or
CMBST
357
P034
2-Cyclohexyl-4,6-dinitrophenol
2-Cyclohexyl-4,6-dinitrophenol
131-89-5
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
P036
Dichlorophenylarsine
Arsenic
7440-38-2
1.4
5.0 mg/l TCLP
P037
Dieldrin
Dieldrin
60-57-1
0.017
0.13
P038
Diethylarsine
Arsenic
7440-38-2
1.4
5.0 mg/l TCLP
P039
Disulfoton
Disulfoton
298-04-4
0.017
6.2
P040
O,O-Diethyl-O-pyrazinyl-phosphorothioate
O,O-Diethyl-O-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
358
P044
Dimethoate
Dimethoate
60-51-5
CARBN; or
CMBST
CMBST
P045
Thiofanox
Thiofanox
39196-18-4
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
P046
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
51-28-5
0.12
160
P049
Dithiobiuret
Dithiobiuret
541-53-7
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
P050
Endosulfan
Endosulfan I
939-98-8
0.023
0.066
Endosulfan II
33213-6-5
0.029
0.13
359
Endosulfan sulfate
1031-07-8
0.029
0.13
P051
Endrin
Endrin
72-20-8
0.0028
0.13
Endrin aldehyde
7421-93-4
0.025
0.13
P054
Aziridine
Aziridine
151-56-4
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
P056
Fluorine
Fluoride (measured in
wastewaters only)
16964-48-8
35
ADGAS fb
NEUTR
P057
Fluoroacetamide
Fluoroacetamide
640-19-7
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
P058
Fluoroacetic acid, sodium salt
Fluoroacetic acid, sodium salt
62-74-8
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
P059
Heptachlor
Heptachlor
76-44-8
0.0012
0.066
Heptachlor epoxide
1024-57-3
0.016
0.066
P060
Isodrin
Isodrin
465-73-6
0.021
0.066
360
P062
Hexaethyl tetraphosphate
Hexaethyl tetraphosphate
757-58-4
CARBN; or
CMBST
CMBST
P063
Hydrogen cyanide
Cyanides (Total)
7
57-12-5
1.2
590
Cyanides (Amenable)
7
57-12-5
0.86
30
P064
Isocyanic acid, ethyl ester
Isocyanic acid, ethyl ester
624-83-9
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
P065
P065 (mercury fulminate) nonwastewaters, regardless of their total mercury content, that are
not incinerator residues or are not residues from RMERC.
Mercury
7439-97-6
NA
IMERC
P065
P065 (mercury fulminate) nonwastewaters that are either incinerator residues or are residues
from RMERC; and contain greater than or equal to 260 mg/kg total mercury.
Mercury
7339-97-6
NA
RMERC
P065
P065 (mercury fulminate) nonwastewaters that are residues from RMERC and contain less than
260 mg/kg total mercury.
Mercury
7439-97-6
NA
0.20 mg/l TCLP
P065
P065 (mercury fulminate) nonwastewaters that are incinerator residues and contain less than
260 mg/kg total mercury.
Mercury
7439-97-6
NA
0.025 mg/l TCLP
P065
All P065 (mercury fulminate) wastewaters.
Mercury
7439-97-6
0.15
NA
361
P066
Methomyl
Methomyl
16752-77-5
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
P067
2-Methyl-aziridine
2-Methyl-aziridine
75-55-8
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
P068
Methyl hydrazine
Methyl hydrazine
60-34-4
CHOXD;
CHRED;
CARBN; BIODG;
or CMBST
CHOXD;
CHRED, or
CMBST
P069
2-Methyllactonitrile
2-Methyllactonitrile
75-86-5
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
P070
Aldicarb
Aldicarb
116-06-3
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
P071
Methyl parathion
Methyl parathion
298-00-0
0.014
4.6
P072
1-Naphthyl-2-thiourea
1-Naphthyl-2-thiourea
86-88-4
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
362
P073
Nickel carbonyl
Nickel
7440-02-0
3.98
11 mg/l TCLP
P074
Nickel cyanide
Cyanides (Total)
7
57-12-5
1.2
590
Cyanides (Amenable)
7
57-12-5
0.86
30
Nickel
7440-02-0
3.98
11 mg/l TCLP
P075
Nicotine and salts
Nicotine and salts
54-11-5
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
P076
Nitric oxide
Nitric oxide
10102-43-9
ADGAS
ADGAS
P077
p-Nitroaniline
p-Nitroaniline
100-01-6
0.028
28
P078
Nitrogen dioxide
Nitrogen dioxide
10102-44-0
ADGAS
ADGAS
P081
Nitroglycerin
Nitroglycerin
55-63-0
CHOXD;
CHRED;
CARBN; BIODG
or CMBST
CHOXD;
CHRED; or
CMBST
P082
N-Nitrosodimethylamine
N-Nitrosodimethylamine
62-75-9
0.40
2.3
363
P084
N-Nitrosomethylvinylamine
N-Nitrosomethylvinylamine
4549-40-0
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
P085
Octamethylpyrophosphoramide
Octamethylpyrophosphoramide
152-16-9
CARBN; or
CMBST
CMBST
P087
Osmium tetroxide
Osmium tetroxide
20816-12-0
RMETL; or
RTHRM
RMETL; or
RTHRM
P088
Endothall
Endothall
145-73-3
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
P089
Parathion
Parathion
56-38-2
0.014
4.6
P092
P092 (phenyl mercuric acetate) nonwastewaters, regardless of their total mercury content, that
are not incinerator residues or are not residues from RMERC.
Mercury
7439-97-6
NA
IMERC; or
RMERC
P092
P092 (phenyl mercuric acetate) nonwastewaters that are either incinerator residues or are
residues from RMERC; and still contain greater than or equal to 260 mg/kg total mercury.
Mercury
7439-97-6
NA
RMERC
P092
P092 (phenyl mercuric acetate) nonwastewaters that are residues from RMERC and contain less
than 260 mg/kg total mercury.
Mercury
7439-97-6
NA
0.20 mg/l TCLP
364
P092
P092 (phenyl mercuric acetate) nonwastewaters that are incinerator residues and contain less
than 260 mg/kg total mercury.
Mercury
7439-97-6
NA
0.025 mg/l TCLP
P092
All P092 (phenyl mercuric acetate) wastewaters.
Mercury
7439-97-6
0.15
NA
P093
Phenylthiourea
Phenylthiourea
103-85-5
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
P094
Phorate
Phorate
298-02-2
0.021
4.6
P095
Phosgene
Phosgene
75-44-5
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
P096
Phosphine
Phosphine
7803-51-2
CHOXD;
CHRED; or
CMBST
CHOXD;
CHRED; or
CMBST
P097
Famphur
Famphur
52-85-7
0.017
15
P098
Potassium cyanide.
Cyanides (Total)
7
57-12-5
1.2
590
Cyanides (Amenable)
7
57-12-5
0.86
30
P099
Potassium silver cyanide
Cyanides (Total)
7
57-12-5
1.2
590
365
Cyanides (Amenable)
7
57-12-5
0.86
30
Silver
7440-22-4
0.43
0.14 mg/l TCLP
P101
Ethyl cyanide (Propanenitrile)
Ethyl cyanide (Propanenitrile)
107-12-0
0.24
360
P102
Propargyl alcohol
Propargyl alcohol
107-19-7
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
P103
Selenourea
Selenium
7782-49-2
0.82
5.7 mg/l TCLP
P104
Silver cyanide
Cyanides (Total)
7
57-12-5
1.2
590
Cyanides (Amenable)
7
57-12-5
0.86
30
Silver
7440-22-4
0.43
0.14 mg/l TCLP
P105
Sodium azide
Sodium azide
26628-22-8
CHOXD;
CHRED;
CARBN; BIODG;
or CMBST
CHOXD;
CHRED; or
CMBST
P106
Sodium cyanide
Cyanides (Total)
7
57-12-5
1.2
590
Cyanides (Amenable)
7
57-12-5
0.86
30
P108
Strychnine and salts
Strychnine and salts
57-24-9
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
366
P109
Tetraethyldithiopyrophosphate
Tetraethyldithiopyrophosphate
3689-24-5
CARBN; or
CMBST
CMBST
P110
Tetraethyl lead
Lead
7439-92-1
0.69
0.75 mg/l TCLP
P111
Tetraethylpyrophosphate
Tetraethylpyrophosphate
107-49-3
CARBN; or
CMBST
CMBST
P112
Tetranitromethane
Tetranitromethane
509-14-8
CHOXD;
CHRED;
CARBN; BIODG;
or CMBST
CHOXD;
CHRED; or
CMBST
P113
Thallic oxide
Thallium (measured in
wastewaters only)
7440-28-0
1.4
RTHRM; or
STABL
P114
Thallium selenite
Selenium
7782-49-2
0.82
5.7 mg/l TCLP
P115
Thallium (I) sulfate
Thallium (measured in
wastewaters only)
7440-28-0
1.4
RTHRM; or
STABL
P116
Thiosemicarbazide
Thiosemicarbazide
79-19-6
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
367
P118
Trichloromethanethiol
Trichloromethanethiol
75-70-7
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
P119
Ammonium vanadate
Vanadium (measured in
wastewaters only)
7440-62-2
4.3
STABL
P120
Vanadium pentoxide
Vanadium (measured in
wastewaters only)
7440-62-2
4.3
STABL
P121
Zinc cyanide
Cyanides (Total)
7
57-12-5
1.2
590
Cyanides (Amenable)
7
57-12-5
0.86
30
P122
Zinc phosphide Zn
3
P
2
, when present at concentrations greater than 10 percent
Zinc Phosphide
1314-84-7
CHOXD;
CHRED; or
CMBST
CHOXD;
CHRED; or
CMBST
P123
Toxaphene
Toxaphene
8001-35-2
0.0095
2.6
P127
Carbofuran
Carbofuran
1563-66-2
0.006
0.14
P128
Mexacarbate
Mexacarbate
315-18-4
0.056
1.4
P185
Tirpate
10
Tirpate
26419-73-8
0.056
0.28
368
P188
Physostigimine salicylate
Physostigmine salicylate
57-64-7
0.056
1.4
P189
Carbosulfan
Carbosulfan
55285-14-8
0.028
1.4
P190
Metolcarb
Metolcarb
1129-41-5
0.056
1.4
P191
Dimetilan
10
Dimetilan
644-64-4
0.056
1.4
P192
Isolan
10
Isolan
119-38-0
0.056
1.4
P194
Oxamyl
Oxamyl
23135-22-0
0.056
0.28
P196
Manganese dimethyldithiocarbamates (total)
Dithiocarbamates (total)
NA
0.028
28
P197
Formparanate
10
Formparanate
17702-57-7
0.056
1.4
P198
Formetanate hydrochloride
Formetanate hydrochloride
23422-53-9
0.056
1.4
P199
Methiocarb
Methiocarb
2032-65-7
0.056
1.4
P201
Promecarb
Promecarb
2631-37-0
0.056
1.4
369
P202
m-Cumenyl methylcarbamate
m-Cumenyl methylcarbamate
64-00-6
0.056
1.4
P203
Aldicarb sulfone
Aldicarb sulfone
1646-88-4
0.056
0.28
P204
Physostigmine
Physostigmine
57-47-6
0.056
1.4
P205
Ziram
Dithiocarbamates (total)
NA
0.028
28
U001
Acetaldehyde
Acetaldehyde
75-07-0
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U002
Acetone
Acetone
67-64-1
0.28
160
U003
Acetonitrile
Acetonitrile
75-05-8
5.6
CMBST
Acetonitrile; alternate
6
standard
for nonwastewaters only
75-05-8
NA
38
U004
Acetophenone
Acetophenone
98-86-2
0.010
9.7
U005
2-Acetylaminofluorene
2-Acetylaminofluorene
53-96-3
0.059
140
370
U006
Acetyl chloride
Acetyl chloride
75-36-5
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U007
Acrylamide
Acrylamide
79-06-1
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U008
Acrylic acid
Acrylic acid
79-10-7
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U009
Acrylonitrile
Acrylonitrile
107-13-1
0.24
84
U010
Mitomycin C
Mitomycin C
50-07-7
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U011
Amitrole
Amitrole
61-82-5
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U012
Aniline
Aniline
62-53-3
0.81
14
371
U014
Auramine
Auramine
492-80-8
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U015
Azaserine
Azaserine
115-02-6
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U016
Benz(c)acridine
Benz(c)acridine
225-51-4
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U017
Benzal chloride
Benzal chloride
98-87-3
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U018
Benz(a)anthracene
Benz(a)anthracene
56-55-3
0.059
3.4
U019
Benzene
Benzene
71-43-2
0.14
10
U020
Benzenesulfonyl chloride
Benzenesulfonyl chloride
98-09-9
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
372
U021
Benzidine
Benzidine
92-87-5
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U022
Benzo(a)pyrene
Benzo(a)pyrene
50-32-8
0.061
3.4
U023
Benzotrichloride
Benzotrichloride
98-07-7
CHOXD;
CHRED;
CARBN; BIODG;
or CMBST
CHOXD;
CHRED; or
CMBST
U024
bis(2-Chloroethoxy)methane
bis(2-Chloroethoxy)methane
111-91-1
0.036
7.2
U025
bis(2-Chloroethyl)ether
bis(2-Chloroethyl)ether
111-44-4
0.033
6.0
U026
Chlornaphazine
Chlornaphazine
494-03-1
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U027
bis(2-Chloroisopropyl)ether
bis(2-Chloroisopropyl)ether
39638-32-9
0.055
7.2
U028
bis(2-Ethylhexyl)phthalate
bis(2-Ethylhexyl)phthalate
117-81-7
0.28
28
U029
Methyl bromide (Bromomethane)
Methyl bromide (Bromo-
methane)
74-83-9
0.11
15
373
U030
4-Bromophenyl phenyl ether
4-Bromophenyl phenyl ether
101-55-3
0.055
15
U031
n-Butyl alcohol
n-Butyl alcohol
71-36-3
5.6
2.6
U032
Calcium chromate
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
U033
Carbon oxyfluoride
Carbon oxyfluoride
353-50-4
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U034
Trichloroacetaldehyde (Chloral)
Trichloroacetaldehyde (Chloral)
75-87-6
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U035
Chlorambucil
Chlorambucil
305-03-3
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U036
Chlordane
Chlordane (
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
374
U039
p-Chloro-m-cresol
p-Chloro-m-cresol
59-50-7
0.018
14
U041
Epichlorohydrin (1-Chloro-2,3-epoxypropane)
Epichlorohydrin (1-Chloro-2,3-
epoxypropane)
106-89-8
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U042
2-Chloroethyl vinyl ether
2-Chloroethyl vinyl ether
110-75-8
0.062
CMBST
U043
Vinyl chloride
Vinyl chloride
75-01-4
0.27
6.0
U044
Chloroform
Chloroform
67-66-3
0.046
6.0
U045
Chloromethane (Methyl chloride)
Chloromethane (Methyl
chloride)
74-87-3
0.19
30
U046
Chloromethyl methyl ether
Chloromethyl methyl ether
107-30-2
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U047
2-Chloronaphthalene
2-Chloronaphthalene
91-58-7
0.055
5.6
U048
2-Chlorophenol
2-Chlorophenol
95-57-8
0.044
5.7
375
U049
4-Chloro-o-toluidine hydrochloride
4-Chloro-o-toluidine hydro-
chloride
3165-93-3
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U050
Chrysene
Chrysene
218-01-9
0.059
3.4
U051
Creosote
Naphthalene
91-20-3
0.059
5.6
Pentachlorophenol
87-86-5
0.089
7.4
Phenanthrene
85-01-8
0.059
5.6
Pyrene
129-00-0
0.067
8.2
Toluene
108-88-3
0.080
10
Xylenes-mixed isomers
(sum of o-, m-, and p-xylene
concentrations)
1330-20-7
0.32
30
Lead
7439-92-1
0.69
0.75 mg/l TCLP
U052
Cresols (Cresylic acid)
o-Cresol
95-48-7
0.11
5.6
m-Cresol (difficult to distinguish
from p-cresol)
108-39-4
0.77
5.6
p-Cresol (difficult to distinguish
from m-cresol)
106-44-5
0.77
5.6
Cresol-mixed isomers (Cresylic
acid)
(sum of o-, m-, and p-cresol
concentrations)
1319-77-3
0.88
11.2
U053
Crotonaldehyde
Crotonaldehyde
4170-30-3
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
376
U055
Cumene
Cumene
98-82-8
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U056
Cyclohexane
Cyclohexane
110-82-7
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U057
Cyclohexanone
Cyclohexanone
108-94-1
0.36
CMBST
Cyclohexanone; alternate
6
standard for nonwastewaters
only
108-94-1
NA
0.75 mg/l TCLP
U058
Cyclophosphamide
Cyclophosphamide
50-18-0
CARBN; or
CMBST
CMBST
U059
Daunomycin
Daunomycin
20830-81-3
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U060
DDD
o,p'-DDD
53-19-0
0.023
0.087
p,p'-DDD
72-54-8
0.023
0.087
U061
DDT
o,p'-DDT
789-02-6
0.0039
0.087
p,p'-DDT
50-29-3
0.0039
0.087
o,p'-DDD
53-19-0
0.023
0.087
p,p'-DDD
72-54-8
0.023
0.087
o,p'-DDE
3424-82-6
0.031
0.087
377
p,p'-DDE
72-55-9
0.031
0.087
U062
Diallate
Diallate
2303-16-4
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U063
Dibenz(a,h)anthracene
Dibenz(a,h)anthracene
53-70-3
0.055
8.2
U064
Dibenz(a,i)pyrene
Dibenz(a,i)pyrene
189-55-9
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U066
1,2-Dibromo-3-chloropropane
1,2-Dibromo-3-chloropropane
96-12-8
0.11
15
U067
Ethylene dibromide (1,2-Dibromoethane)
Ethylene dibromide (1,2-
Dibromoethane)
106-93-4
0.028
15
U068
Dibromomethane
Dibromomethane
74-95-3
0.11
15
U069
Di-n-butyl phthalate
Di-n-butyl phthalate
84-74-2
0.057
28
U070
o-Dichlorobenzene
o-Dichlorobenzene
95-50-1
0.088
6.0
U071
m-Dichlorobenzene
m-Dichlorobenzene
541-73-1
0.036
6.0
378
U072
p-Dichlorobenzene
p-Dichlorobenzene
106-46-7
0.090
6.0
U073
3,3'-Dichlorobenzidine
3,3'-Dichlorobenzidine
91-94-1
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U074
1,4-Dichloro-2-butene
cis-1,4-Dichloro-2-butene
1476-11-5
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
trans-1,4-Dichloro-2-butene
764-41-0
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U075
Dichlorodifluoromethane
Dichlorodifluoromethane
75-71-8
0.23
7.2
U076
1,1-Dichloroethane
1,1-Dichloroethane
75-34-3
0.059
6.0
U077
1,2-Dichloroethane
1,2-Dichloroethane
107-06-2
0.21
6.0
U078
1,1-Dichloroethylene
1,1-Dichloroethylene
75-35-4
0.025
6.0
U079
1,2-Dichloroethylene
trans-1,2-Dichloroethylene
156-60-5
0.054
30
U080
Methylene chloride
Methylene chloride
75-09-2
0.089
30
379
U081
2,4-Dichlorophenol
2,4-Dichlorophenol
120-83-2
0.044
14
U082
2,6-Dichlorophenol
2,6-Dichlorophenol
87-65-0
0.044
14
U083
1,2-Dichloropropane
1,2-Dichloropropane
78-87-5
0.85
18
U084
1,3-Dichloropropylene
cis-1,3-Dichloropropylene
10061-01-5
0.036
18
trans-1,3-Dichloropropylene
10061-02-6
0.036
18
U085
1,2:3,4-Diepoxybutane
1,2:3,4-Diepoxybutane
1464-53-5
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U086
N,N'-Diethylhydrazine
N,N'-Diethylhydrazine
1615-80-1
CHOXD;
CHRED;
CARBN; BIODG;
or CMBST
CHOXD;
CHRED; or
CMBST
U087
O,O-Diethyl-S-methyldithiophosphate
O,O-Diethyl-S-methyldithio-
phosphate
3288-58-2
CARBN; or
CMBST
CMBST
U088
Diethyl phthalate
Diethyl phthalate
84-66-2
0.20
28
380
U089
Diethyl stilbestrol
Diethyl stilbestrol
56-53-1
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U090
Dihydrosafrole
Dihydrosafrole
94-58-6
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U091
3,3'-Dimethoxybenzidine
3,3'-Dimethoxybenzidine
119-90-4
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U092
Dimethylamine
Dimethylamine
124-40-3
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U093
p-Dimethylaminoazobenzene
p-Dimethylaminoazobenzene
60-11-7
0.13
CMBST
U094
7,12-Dimethylbenz(a)anthracene
7,12-Dimethylbenz(a)anthracene
57-97-6
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U095
3,3'-Dimethylbenzidine
3,3'-Dimethylbenzidine
119-93-7
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
381
U096
α
,
α
-Dimethyl benzyl hydroperoxide
α
,
α
-Dimethyl benzyl hydro-
peroxide
80-15-9
CHOXD;
CHRED;
CARBN; BIODG;
or CMBST
CHOXD;
CHRED; or
CMBST
U097
Dimethylcarbamoyl chloride
Dimethylcarbamoyl chloride
79-44-7
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U098
1,1-Dimethylhydrazine
1,1-Dimethylhydrazine
57-14-7
CHOXD;
CHRED;
CARBN; BIODG;
or CMBST
CHOXD;
CHRED; or
CMBST
U099
1,2-Dimethylhydrazine
1,2-Dimethylhydrazine
540-73-8
CHOXD;
CHRED;
CARBN; BIODG;
or CMBST
CHOXD;
CHRED; or
CMBST
U101
2,4-Dimethylphenol
2,4-Dimethylphenol
105-67-9
0.036
14
U102
Dimethyl phthalate
Dimethyl phthalate
131-11-3
0.047
28
U103
Dimethyl sulfate
Dimethyl sulfate
77-78-1
CHOXD;
CHRED;
CARBN; BIODG;
or CMBST
CHOXD;
CHRED; or
CMBST
382
U105
2,4-Dinitrotoluene
2,4-Dinitrotoluene
121-14-2
0.32
140
U106
2,6-Dinitrotoluene
2,6-Dinitrotoluene
606-20-2
0.55
28
U107
Di-n-octyl phthalate
Di-n-octyl phthalate
117-84-0
0.017
28
U108
1,4-Dioxane
1,4-Dioxane
123-91-1
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
1,4-Dioxane; alternate
6
standard
for nonwastewaters only
123-91-1
12.0
170
U109
1,2-Diphenylhydrazine
1,2-Diphenylhydrazine
122-66-7
CHOXD;
CHRED;
CARBN; BIODG;
or CMBST
CHOXD;
CHRED; or
CMBST
1,2-Diphenylhydrazine;
alternate
6
standard for
wastewaters only
122-66-7
0.087
NA
U110
Dipropylamine
Dipropylamine
142-84-7
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U111
Di-n-propylnitrosamine
Di-n-propylnitrosamine
621-64-7
0.40
14
U112
Ethyl acetate
Ethyl acetate
141-78-6
0.34
33
383
U113
Ethyl acrylate
Ethyl acrylate
140-88-5
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U114
Ethylenebisdithiocarbamic acid salts and esters
Ethylenebisdithiocarbamic acid
111-54-6
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U115
Ethylene oxide
Ethylene oxide
75-21-8
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CHOXD; or
CMBST
Ethylene oxide; alternate
6
standard for wastewaters only
75-21-8
0.12
NA
U116
Ethylene thiourea
Ethylene thiourea
96-45-7
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U117
Ethyl ether
Ethyl ether
60-29-7
0.12
160
U118
Ethyl methacrylate
Ethyl methacrylate
97-63-2
0.14
160
U119
Ethyl methane sulfonate
Ethyl methane sulfonate
62-50-0
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
384
U120
Fluoranthene
Fluoranthene
206-44-0
0.068
3.4
U121
Trichloromonofluoromethane
Trichloromonofluoromethane
75-69-4
0.020
30
U122
Formaldehyde
Formaldehyde
50-00-0
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U123
Formic acid
Formic acid
64-18-6
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U124
Furan
Furan
110-00-9
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U125
Furfural
Furfural
98-01-1
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U126
Glycidylaldehyde
Glycidylaldehyde
765-34-4
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
385
U127
Hexachlorobenzene
Hexachlorobenzene
118-74-1
0.055
10
U128
Hexachlorobutadiene
Hexachlorobutadiene
87-68-3
0.055
5.6
U129
Lindane
α
-BHC
319-84-6
0.00014
0.066
β
-BHC
319-85-7
0.00014
0.066
δ
-BHC
319-86-8
0.023
0.066
χ
-BHC (Lindane)
58-89-9
0.0017
0.066
U130
Hexachlorocyclopentadiene
Hexachlorocyclopentadiene
77-47-4
0.057
2.4
U131
Hexachloroethane
Hexachloroethane
67-72-1
0.055
30
U132
Hexachlorophene
Hexachlorophene
70-30-4
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U133
Hydrazine
Hydrazine
302-01-2
CHOXD;
CHRED;
CARBN; BIODG;
or CMBST
CHOXD;
CHRED; or
CMBST
U134
Hydrogen fluoride
Fluoride (measured in
wastewaters only)
16964-48-8
35
ADGAS fb
NEUTR; or
NEUTR
386
U135
Hydrogen sulfide
Hydrogen sulfide
7783-06-4
CHOXD;
CHRED; or
CMBST
CHOXD;
CHRED; or
CMBST
U136
Cacodylic acid
Arsenic
7440-38-2
1.4
5.0 mg/l TCLP
U137
Indeno(1,2,3-c,d)pyrene
Indeno(1,2,3-c,d)pyrene
193-39-5
0.0055
3.4
U138
Iodomethane
Iodomethane
74-88-4
0.19
65
U140
Isobutyl alcohol
Isobutyl alcohol
78-83-1
5.6
170
U141
Isosafrole
Isosafrole
120-58-1
0.081
2.6
U142
Kepone
Kepone
143-50-8
0.0011
0.13
U143
Lasiocarpine
Lasiocarpine
303-34-4
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U144
Lead acetate
Lead
7439-92-1
0.69
0.75 mg/l TCLP
U145
Lead phosphate
Lead
7439-92-1
0.69
0.75 mg/l TCLP
387
U146
Lead subacetate
Lead
7439-92-1
0.69
0.75 mg/l TCLP
U147
Maleic anhydride
Maleic anhydride
108-31-6
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U148
Maleic hydrazide
Maleic hydrazide
123-33-1
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U149
Malononitrile
Malononitrile
109-77-3
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U150
Melphalan
Melphalan
148-82-3
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U151
U151 (mercury) nonwastewaters that contain greater than or equal to 260 mg/kg total mercury.
Mercury
7439-97-6
NA
RMERC
U151
U151 (mercury) nonwastewaters that contain less than 260 mg/kg total mercury and that are
residues from RMERC only.
Mercury
7439-97-6
NA
0.20 mg/l TCLP
U151
U151 (mercury) nonwastewaters that contain less than 260 mg/kg total mercury and that are not
residues from RMERC only.
Mercury
7439-97-6
NA
0.025 mg/l TCLP
388
U151
All U151 (mercury) wastewater.
Mercury
7439-97-6
0.15
NA
U151
Element Mercury Contaminated with Radioactive Materials
Mercury
7439-97-6
NA
AMLGM
U152
Methacrylonitrile
Methacrylonitrile
126-98-7
0.24
84
U153
Methanethiol
Methanethiol
74-93-1
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U154
Methanol
Methanol
67-56-1
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
Methanol; alternate
6
set of
standards for both wastewaters
and nonwastewaters
67-56-1
5.6
0.75 mg/l TCLP
U155
Methapyrilene
Methapyrilene
91-80-5
0.081
1.5
U156
Methyl chlorocarbonate
Methyl chlorocarbonate
79-22-1
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U157
3-Methylcholanthrene
3-Methylcholanthrene
56-49-5
0.0055
15
389
U158
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
0.28
36
U160
Methyl ethyl ketone peroxide
Methyl ethyl ketone peroxide
1338-23-4
CHOXD;
CHRED;
CARBN; BIODG;
or CMBST
CHOXD;
CHRED; or
CMBST
U161
Methyl isobutyl ketone
Methyl isobutyl ketone
108-10-1
0.14
33
U162
Methyl methacrylate
Methyl methacrylate
80-62-6
0.14
160
U163
N-Methyl-N'-nitro-N-nitrosoguanidine
N-Methyl-N'-nitro-N-nitroso-
guanidine
70-25-7
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U164
Methylthiouracil
Methylthiouracil
56-04-2
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U165
Naphthalene
Naphthalene
91-20-3
0.059
5.6
390
U166
1,4-Naphthoquinone
1,4-Naphthoquinone
130-15-4
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U167
1-Naphthylamine
1-Naphthylamine
134-32-7
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U168
2-Naphthylamine
2-Naphthylamine
91-59-8
0.52
CMBST
U169
Nitrobenzene
Nitrobenzene
98-95-3
0.068
14
U170
p-Nitrophenol
p-Nitrophenol
100-02-7
0.12
29
U171
2-Nitropropane
2-Nitropropane
79-46-9
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U172
N-Nitrosodi-n-butylamine
N-Nitrosodi-n-butylamine
924-16-3
0.40
17
U173
N-Nitrosodiethanolamine
N-Nitrosodiethanolamine
1116-54-7
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
391
U174
N-Nitrosodiethylamine
N-Nitrosodiethylamine
55-18-5
0.40
28
U176
N-Nitroso-N-ethylurea
N-Nitroso-N-ethylurea
759-73-9
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U177
N-Nitroso-N-methylurea
N-Nitroso-N-methylurea
684-93-5
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U178
N-Nitroso-N-methylurethane
N-Nitroso-N-methylurethane
615-53-2
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U179
N-Nitrosopiperidine
N-Nitrosopiperidine
100-75-4
0.013
35
U180
N-Nitrosopyrrolidine
N-Nitrosopyrrolidine
930-55-2
0.013
35
U181
5-Nitro-o-toluidine
5-Nitro-o-toluidine
99-55-8
0.32
28
U182
Paraldehyde
Paraldehyde
123-63-7
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
392
U183
Pentachlorobenzene
Pentachlorobenzene
608-93-5
0.055
10
U184
Pentachloroethane
Pentachloroethane
76-01-7
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
Pentachloroethane; alternate
6
standards for both wastewaters
and nonwastewaters
76-01-7
0.055
6.0
U185
Pentachloronitrobenzene
Pentachloronitrobenzene
82-68-8
0.055
4.8
U186
1,3-Pentadiene
1,3-Pentadiene
504-60-9
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U187
Phenacetin
Phenacetin
62-44-2
0.081
16
U188
Phenol
Phenol
108-95-2
0.039
6.2
U189
Phosphorus sulfide
Phosphorus sulfide
1314-80-3
CHOXD;
CHRED; or
CMBST
CHOXD;
CHRED; or
CMBST
U190
Phthalic anhydride
Phthalic anhydride (measured as
Phthalic acid or Terephthalic
acid)
100-21-0
0.055
28
393
Phthalic anhydride (measured as
Phthalic acid or Terephthalic
acid)
85-44-9
0.055
28
U191
2-Picoline
2-Picoline
109-06-8
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U192
Pronamide
Pronamide
23950-58-5
0.093
1.5
U193
1,3-Propane sultone
1,3-Propane sultone
1120-71-4
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U194
n-Propylamine
n-Propylamine
107-10-8
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U196
Pyridine
Pyridine
110-86-1
0.014
16
U197
p-Benzoquinone
p-Benzoquinone
106-51-4
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
394
U200
Reserpine
Reserpine
50-55-5
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U201
Resorcinol
Resorcinol
108-46-3
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U202
Saccharin and salts
Saccharin
81-07-2
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U203
Safrole
Safrole
94-59-7
0.081
22
U204
Selenium dioxide
Selenium
7782-49-2
0.82
5.7 mg/l TCLP
U205
Selenium sulfide
Selenium
7782-49-2
0.82
5.7 mg/l TCLP
U206
Streptozotocin
Streptozotocin
18883-66-4
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U207
1,2,4,5-Tetrachlorobenzene
1,2,4,5-Tetrachlorobenzene
95-94-3
0.055
14
395
U208
1,1,1,2-Tetrachloroethane
1,1,1,2-Tetrachloroethane
630-20-6
0.057
6.0
U209
1,1,2,2-Tetrachloroethane
1,1,2,2-Tetrachloroethane
79-34-5
0.057
6.0
U210
Tetrachloroethylene
Tetrachloroethylene
127-18-4
0.056
6.0
U211
Carbon tetrachloride
Carbon tetrachloride
56-23-5
0.057
6.0
U213
Tetrahydrofuran
Tetrahydrofuran
109-99-9
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U214
Thallium (I) acetate
Thallium (measured in
wastewaters only)
7440-28-0
1.4
RTHRM; or
STABL
U215
Thallium (I) carbonate
Thallium (measured in
wastewaters only)
7440-28-0
1.4
RTHRM; or
STABL
U216
Thallium (I) chloride
Thallium (measured in
wastewaters only)
7440-28-0
1.4
RTHRM; or
STABL
U217
Thallium (I) nitrate
Thallium (measured in
wastewaters only)
7440-28-0
1.4
RTHRM; or
STABL
396
U218
Thioacetamide
Thioacetamide
62-55-5
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U219
Thiourea
Thiourea
62-56-6
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U220
Toluene
Toluene
108-88-3
0.080
10
U221
Toluenediamine
Toluenediamine
25376-45-8
CARBN; or
CMBST
CMBST
U222
o-Toluidine hydrochloride
o-Toluidine hydrochloride
636-21-5
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U223
Toluene diisocyanate
Toluene diisocyanate
26471-62-5
CARBN; or
CMBST
CMBST
U225
Bromoform (Tribromomethane)
Bromoform (Tribromomethane)
75-25-2
0.63
15
U226
1,1,1-Trichloroethane
1,1,1-Trichloroethane
71-55-6
0.054
6.0
397
U227
1,1,2-Trichloroethane
1,1,2-Trichloroethane
79-00-5
0.054
6.0
U228
Trichloroethylene
Trichloroethylene
79-01-6
0.054
6.0
U234
1,3,5-Trinitrobenzene
1,3,5-Trinitrobenzene
99-35-4
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U235
tris-(2,3-Dibromopropyl)-phosphate
tris-(2,3-Dibromopropyl)-
phosphate
126-72-7
0.11
0.10
U236
Trypan Blue
Trypan Blue
72-57-1
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U237
Uracil mustard
Uracil mustard
66-75-1
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U238
Urethane (Ethyl carbamate)
Urethane (Ethyl carbamate)
51-79-6
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
398
U239
Xylenes
Xylenes-mixed isomers
(sum of o-, m-, and p-xylene
concentrations)
1330-20-7
0.32
30
U240
2,4-D (2,4-Dichlorophenoxyacetic acid)
2,4-D (2,4-Dichloro-
phenoxyacetic acid)
94-75-7
0.72
10
2,4-D (2,4-Dichloro-
phenoxyacetic acid) salts and
esters
NA
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U243
Hexachloropropylene
Hexachloropropylene
1888-71-7
0.035
30
U244
Thiram
Thiram
137-26-8
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
U246
Cyanogen bromide
Cyanogen bromide
506-68-3
CHOXD;
WETOX; or
CMBST
CHOXD;
WETOX; or
CMBST
U247
Methoxychlor
Methoxychlor
72-43-5
0.25
0.18
U248
Warfarin, & salts, when present at concentrations of 0.3 percent or less
Warfarin
81-81-2
(WETOX or
CHOXD) fb
CARBN; or
CMBST
CMBST
399
U249
Zinc phosphide, Zn
3
P
2
, when present at concentrations of 10 percent or less
Zinc Phosphide
1314-84-7
CHOXD;
CHRED; or
CMBST
CHOXD;
CHRED; or
CMBST
U271
Benomyl
Benomyl
17804-35-2
0.056
1.4
U278
Bendiocarb
Bendiocarb
22781-23-3
0.056
1.4
U279
Carbaryl
Carbaryl
63-25-2
0.006
0.14
U280
Barban
Barban
101-27-9
0.056
1.4
U328
o-Toluidine
o-Toluidine
95-53-4
CMBST; or
CHOXD fb
(BIODG or
CARBN); or
BIODG fb
CARBN
CMBST
U353
p-Toluidine
p-Toluidine
106-49-0
CMBST; or
CHOXD fb
(BIODG or
CARBN); or
BIODG fb
CARBN
CMBST
400
U359
2-Ethoxyethanol
2-Ethoxyethanol
110-80-5
CMBST; or
CHOXD fb
(BIODG or
CARBN); or
BIODG fb
CARBN
CMBST
U364
Bendiocarb phenol
10
Bendiocarb phenol
22961-82-6
0.056
1.4
U367
Carbofuran phenol
Carbofuran phenol
1563-38-8
0.056
1.4
U372
Carbendazim
Carbendazim
10605-21-7
0.056
1.4
U373
Propham
Propham
122-42-9
0.056
1.4
U387
Prosulfocarb
Prosulfocarb
52888-80-9
0.042
1.4
U389
Triallate
Triallate
2303-17-5
0.042
1.4
U394
A2213
10
A2213
30558-43-1
0.042
1.4
U395
Diethylene glycol, dicarbamate
10
Diethylene glycol, dicarbamate
5952-26-1
0.056
1.4
U404
Triethylamine
Triethylamine
101-44-8
0.081
1.5
401
U408
2,4,6-Tribromophenol
2,4,6-Tribromophenol
118-79-6
0.035
7.4
U409
Thiophanate-methyl
Thiophanate-methyl
23564-05-8
0.056
1.4
U410
Thiodicarb
Thiodicarb
59669-26-0
0.019
1.4
U411
Propoxur
Propoxur
114-26-1
0.056
1.4
Notes:
1
The waste descriptions provided in this table do not replace waste descriptions in 35 Ill.
Adm. Code 721. Descriptions of Treatment or Regulatory Subcategories are provided,
as needed, to distinguish between applicability of different standards.
2
CAS means Chemical Abstract Services. When the waste code or regulated constituents
are described as a combination of a chemical with its salts or esters, the CAS number is
given for the parent compound only.
3
Concentration standards for wastewaters are expressed in mg/l and are based on analysis
of composite samples.
4
All treatment standards expressed as a Technology Code or combination of Technology
Codes are explained in detail in Table C of this Part, “Technology Codes and
Descriptions of Technology-Based Standards”. “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 upon 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 upon 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
402
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
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.
BOARD NOTE: Derived from table to 40 CFR 268.40 (1998) (1999), as amended at 63 64
Fed. Reg. 47415 (Sep. 4, 1998) 56471 (October 20, 1999) and 63 65 Fed. Reg. 51264 (Sep.
24, 1998) 14472 (Mar, 17, 2000).
NA
means not applicable.
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
403
Section 728.Table U
Universal Treatment Standards (UTS)
Regulated Constituent-
Common Name
CAS
1
No.
Wastewater
Standard
Concentration (in
mg/l
2
)
Nonwastewater
Standard
Concentration (in
mg/kg
3
unless
noted as “mg/l
TCLP”)
Acenaphthylene
208-96-8
0.059
3.4
Acenaphthene
83-32-9
0.059
3.4
Acetone
67-64-1
0.28
160
Acetonitrile
75-05-8
5.6
38
Acetophenone
96-86-2
0.010
9.7
2-Acetylaminofluorene
53-96-3
0.059
140
Acrolein
107-02-8
0.29
NA
Acrylamide
79-06-1
19
23
Acrylonitrile
107-13-1
0.24
84
Aldicarb sulfone
6
1646-88-4
0.056
0.28
Aldrin
309-00-2
0.021
0.066
4-Aminobiphenyl
92-67-1
0.13
NA
Aniline
62-53-3
0.81
14
Anthracene
120-12-7
0.059
3.4
Aramite
140-57-8
0.36
NA
α
-BHC
319-84-6
0.00014
0.066
β
-BHC
319-85-7
0.00014
0.066
δ
-BHC
319-86-8
0.023
0.066
χ
-BHC
58-89-9
0.0017
0.066
Barban
6
101-27-9
0.056
1.4
Bendiocarb
6
22781-23-3
0.056
1.4
Benomyl
6
17804-35-2
0.056
1.4
Benz(a)anthracene
56-55-3
0.059
3.4
Benzal chloride
98-87-3
0.055
6.0
Benzene
71-43-2
0.14
10
Benzo(b)fluoranthene
(difficult to distinguish from
benzo(k)fluoranthene)
205-99-2
0.11
6.8
Benzo(k)fluoranthene
(difficult to distinguish from
benzo(b)fluoranthene)
207-08-9
0.11
6.8
Benzo(g,h,i)perylene
191-24-2
0.0055
1.8
Benzo(a)pyrene
50-32-8
0.061
3.4
Bromodichloromethane
75-27-4
0.35
15
Methyl bromide (Bromo-
methane)
74-83-9
0.11
15
4-Bromophenyl phenyl ether
101-55-3
0.055
15
404
n-Butyl alcohol
71-36-3
5.6
2.6
Butylate
6
2008-41-5
0.042
1.4
Butyl benzyl phthalate
85-68-7
0.017
28
2-sec-Butyl-4,6-dinitrophenol
(Dinoseb)
88-85-7
0.066
2.5
Carbaryl
6
63-25-2
0.006
0.14
Carbenzadim
6
10605-21-7
0.056
1.4
Carbofuran
6
1563-66-2
0.006
0.14
Carbofuran phenol
6
1563-38-8
0.056
1.4
Carbon disulfide
75-15-0
3.8
4.8 mg/l TCLP
Carbon tetrachloride
56-23-5
0.057
6.0
Carbosulfan
6
55285-14-8
0.028
1.4
Chlordane (
α
and
χ
isomers)
57-74-9
0.0033
0.26
p-Chloroaniline
106-47-8
0.46
16
Chlorobenzene
108-90-7
0.057
6.0
Chlorobenzilate
510-15-6
0.10
NA
2-Chloro-1,3-butadiene
126-99-8
0.057
0.28
p-Chloro-m-cresol
59-50-7
0.018
14
Chlorodibromomethane
124-48-1
0.057
15
Chloroethane
75-00-3
0.27
6.0
bis(2-Chloroethoxy)methane
111-91-1
0.036
7.2
bis(2-Chloroethyl)ether
111-44-4
0.033
6.0
2-Chloroethyl vinyl ether
110-75-8
0.062
NA
Chloroform
67-66-3
0.046
6.0
bis(2-Chloroisopropyl)ether
39638-32-9
0.055
7.2
Chloromethane (Methyl
chloride)
74-87-3
0.19
30
2-Chloronaphthalene
91-58-7
0.055
5.6
2-Chlorophenol
95-57-8
0.044
5.7
3-Chloropropylene
107-05-1
0.036
30
Chrysene
218-01-9
0.059
3.4
o-Cresol
95-48-7
0.11
5.6
m-Cresol (difficult to
distinguish from p-cresol)
108-39-4
0.77
5.6
p-Cresol (difficult to
distinguish from m-cresol)
106-44-5
0.77
5.6
m-Cumenyl methyl-
carbamate
6
64-00-6
0.056
1.4
Cyclohexanone
108-94-1
0.36
0.75 mg/l TCLP
o,p'-DDD
53-19-0
0.023
0.087
p,p'-DDD
72-54-8
0.023
0.087
o,p'-DDE
3424-82-6
0.031
0.087
p,p'-DDE
72-55-9
0.031
0.087
o,p'-DDT
789-02-6
0.0039
0.087
p,p'-DDT
50-29-3
0.0039
0.087
405
Dibenz(a,h)anthracene
53-70-3
0.055
8.2
Dibenz(a,e)pyrene
192-65-4
0.061
NA
1,2-Dibromo-3-chloro-
propane
96-12-8
0.11
15
1,2-Dibromoethane/Ethylene
dibromide
106-93-4
0.028
15
Dibromomethane
74-95-3
0.11
15
m-Dichlorobenzene
541-73-1
0.036
6.0
o-Dichlorobenzene
95-50-1
0.088
6.0
p-Dichlorobenzene
106-46-7
0.090
6.0
Dichlorodifluoromethane
75-71-8
0.23
7.2
1,1-Dichloroethane
75-34-3
0.059
6.0
1,2-Dichloroethane
107-06-2
0.21
6.0
1,1-Dichloroethylene
75-35-4
0.025
6.0
trans-1,2-Dichloroethylene
156-60-5
0.054
30
2,4-Dichlorophenol
120-83-2
0.044
14
2,6-Dichlorophenol
87-65-0
0.044
14
2,4-Dichlorophenoxyacetic
acid/2,4-D
94-75-7
0.72
10
1,2-Dichloropropane
78-87-5
0.85
18
cis-1,3-Dichloropropylene
10061-01-5
0.036
18
trans-1,3-Dichloropropylene
10061-02-6
0.036
18
Dieldrin
60-57-1
0.017
0.13
Diethyl phthalate
84-66-2
0.20
28
p-Dimethylaminoazobenzene
60-11-7
0.13
NA
2,4-Dimethyl phenol
105-67-9
0.036
14
Dimethyl phthalate
131-11-3
0.047
28
Di-n-butyl phthalate
84-74-2
0.057
28
1,4-Dinitrobenzene
100-25-4
0.32
2.3
4,6-Dinitro-o-cresol
534-52-1
0.28
160
2,4-Dinitrophenol
51-28-5
0.12
160
2,4-Dinitrotoluene
121-14-2
0.32
140
2,6-Dinitrotoluene
606-20-2
0.55
28
Di-n-octyl phthalate
117-84-0
0.017
28
Di-n-propylnitrosamine
621-64-7
0.40
14
1,4-Dioxane
123-91-1
12.0
170
Diphenylamine (difficult to
distinguish from
diphenylnitrosamine)
122-39-4
0.92
13
Diphenylnitrosamine (difficult
to distinguish from
diphenylamine)
86-30-6
0.92
13
1,2-Diphenylhydrazine
122-66-7
0.087
NA
Disulfoton
298-04-4
0.017
6.2
Dithiocarbamates (total)
6
137-30-4
0.028
28
406
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
Ethyl acetate
141-78-6
0.34
33
Ethyl benzene
100-41-4
0.057
10
Ethyl cyanide
(Propanenitrile)
107-12-0
0.24
360
Ethylene oxide
75-21-8
0.12
NA
Ethyl ether
60-29-7
0.12
160
bis(2-Ethylhexyl) phthalate
117-81-7
0.28
28
Ethyl methacrylate
97-63-2
0.14
160
Famphur
52-85-7
0.017
15
Fluoranthene
206-44-0
0.068
3.4
Fluorene
86-73-7
0.059
3.4
Formetanate hydrochloride
6
23422-53-9
0.056
1.4
Heptachlor
76-44-8
0.0012
0.066
Heptachlor epoxide
1024-57-3
0.016
0.066
Hexachlorobenzene
118-74-1
0.055
10
Hexachlorobutadiene
87-68-3
0.055
5.6
Hexachlorocyclopentadiene
77-47-4
0.057
2.4
HxCDDs (All Hexachloro-
dibenzo-p-dioxins)
NA
0.000063
0.001
HxCDFs (All Hexachloro-
dibenzofurans)
NA
0.000063
0.001
Hexachloroethane
67-72-1
0.055
30
Hexachloropropylene
1888-71-7
0.035
30
Indeno (1,2,3-c,d) pyrene
193-39-5
0.0055
3.4
Iodomethane
74-88-4
0.19
65
Isobutyl alcohol
78-83-1
5.6
170
Isodrin
465-73-6
0.021
0.066
Isosafrole
120-58-1
0.081
2.6
Kepone
143-50-0
0.0011
0.13
Methacrylonitrile
126-98-7
0.24
84
Methanol
67-56-1
5.6
0.75 mg/l TCLP
Methapyrilene
91-80-5
0.081
1.5
Methiocarb
6
2032-65-7
0.056
1.4
Methomyl
6
16752-77-5
0.028
0.14
Methoxychlor
72-43-5
0.25
0.18
3-Methylcholanthrene
56-49-5
0.0055
15
4,4-Methylene bis(2-chloro-
aniline)
101-14-4
0.50
30
Methylene chloride
75-09-2
0.089
30
407
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
Metolcarb
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
29
N-Nitrosodiethylamine
55-18-5
0.40
28
N-Nitrosodimethylamine
62-75-9
0.40
2.3
N-Nitroso-di-n-butylamine
924-16-3
0.40
17
N-Nitrosomethylethylamine
10595-95-6
0.40
2.3
N-Nitrosomorpholine
59-89-2
0.40
2.3
N-Nitrosopiperidine
100-75-4
0.013
35
N-Nitrosopyrrolidine
930-55-2
0.013
35
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)
1336-36-3
0.10
10
Pebulate
6
1114-71-2
0.042
1.4
Pentachlorobenzene
608-93-5
0.055
10
PeCDDs (All Pentachloro-
dibenzo-p-dioxins)
NA
0.000063
0.001
PeCDFs (All Pentachloro-
dibenzofurans)
NA
0.000035
0.001
Pentachloroethane
76-01-7
0.055
6.0
Pentachloronitrobenzene
82-68-8
0.055
4.8
Pentachlorophenol
87-86-5
0.089
7.4
Phenacetin
62-44-2
0.081
16
Phenanthrene
85-01-8
0.059
5.6
Phenol
108-95-2
0.039
6.2
Phorate
298-02-2
0.021
4.6
Phthalic acid
100-21-0
0.055
28
Phthalic anhydride
85-44-9
0.055
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
408
Pronamide
23950-58-5
0.093
1.5
Propham
6
122-42-9
0.056
1.4
Propoxur
6
114-26-1
0.056
1.4
Prosulfocarb
6
52888-80-9
0.042
1.4
Pyrene
129-00-0
0.067
8.2
Pyridine
110-86-1
0.014
16
Safrole
94-59-7
0.081
22
Silvex (2,4,5-TP)
93-72-1
0.72
7.9
1,2,4,5-Tetrachlorobenzene
95-94-3
0.055
14
TCDDs (All Tetrachloro-
dibenzo-p-dioxins)
NA
0.000063
0.001
TCDFs (All Tetrachloro-
dibenzofurans)
NA
0.000063
0.001
1,1,1,2-Tetrachloroethane
630-20-6
0.057
6.0
1,1,2,2-Tetrachloroethane
79-34-5
0.057
6.0
Tetrachloroethylene
127-18-4
0.056
6.0
2,3,4,6-Tetrachlorophenol
58-90-2
0.030
7.4
Thiodicarb
6
59669-26-0
0.019
1.4
Thiophanate-methyl
6
23564-05-8
0.056
1.4
Toluene
108-88-3
0.080
10
Toxaphene
8001-35-2
0.0095
2.6
Triallate
6
2303-17-5
0.042
1.4
Tribromomethane
(Bromoform)
75-25-2
0.63
15
2,4,6-Tribromophenol
118-79-6
0.035
7.4
1,2,4-Trichlorobenzene
120-82-1
0.055
19
1,1,1-Trichloroethane
71-55-6
0.054
6.0
1,1,2-Trichloroethane
79-00-5
0.054
6.0
Trichloroethylene
79-01-6
0.054
6.0
Trichloromonofluoromethane
75-69-4
0.020
30
2,4,5-Trichlorophenol
95-95-4
0.18
7.4
2,4,6-Trichlorophenol
88-06-2
0.035
7.4
2,4,5-Trichlorophenoxyacetic
acid/2,4,5-T
93-76-5
0.72
7.9
1,2,3-Trichloropropane
96-18-4
0.85
30
1,1,2-Trichloro-1,2,2-
trifluoroethane
76-13-1
0.057
30
Triethylamine
6
101-44-8
0.081
1.5
tris-(2,3-Dibromopropyl)
phosphate
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
409
Antimony
7440-36-0
1.9
1.15 mg/l TCLP
Arsenic
7440-38-2
1.4
5.0 mg/l TCLP
Barium
7440-39-3
1.2
21 mg/l TCLP
Beryllium
7440-41-7
0.82
1.22 mg/l TCLP
Cadmium
7440-43-9
0.69
0.11 mg/l TCLP
Chromium (Total)
7440-47-3
2.77
0.60 mg/l TCLP
Cyanides (Total)
4
57-12-5
1.2
590
Cyanides (Amenable)
4
57-12-5
0.86
30
Fluoride
5
16984-48-8
35
NA
Lead
7439-92-1
0.69
0.75 mg/l TCLP
Mercury-Nonwastewater
from Retort
7439-97-6
NA
0.20 mg/l TCLP
Mercury-All Others
7439-97-6
0.15
0.025 mg/l TCLP
Nickel
7440-02-0
3.98
11 mg/l TCLP
Selenium
7
7782-49-2
0.82
5.7 mg/l TCLP
Silver
7440-22-4
0.43
0.14 mg/l TCLP
Sulfide
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.
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).
410
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.
Note: NA means not applicable.
BOARD NOTE: Derived from table to 40 CFR 268.48(a) (19981999), as amended at 63 65
Fed. Reg. 47410 (Sep. 4, 1998) 14472 (Mar, 17, 2000).
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
TITLE 35: ENVIRONMENTAL PROTECTION
SUBTITLE G: WASTE DISPOSAL
CHAPTER I: POLLUTION CONTROL BOARD
SUBCHAPTER c: HAZARDOUS WASTE OPERATING REQUIREMENTS
PART 733
STANDARDS FOR UNIVERSAL WASTE MANAGEMENT
SUBPART A: GENERAL
Section
733.101
Scope
733.102
Applicability--Batteries
733.103
Applicability--Pesticides
733.104
Applicability--Mercury Thermostats
733.105 Applicability--Lamps.
733.105 Applicability--Household and Conditionally Exempt Small Quantity Generator
Waste
733.106 Definitions
733.107
Applicability--Mercury-Containing Lamps (Repealed)
733.108 Applicability--Household and Conditionally Exempt Small Quantity Generator
Waste
733.109 Definitions
SUBPART B: STANDARDS FOR SMALL QUANTITY HANDLERS
Section
733.110
Applicability
733.111
Prohibitions
411
733.112
Notification
733.113
Waste Management
733.114
Labeling and Marking
733.115
Accumulation Time Limits
733.116
Employee Training
733.117
Response to Releases
733.118
Off-Site Shipments
733.119
Tracking Universal Waste Shipments
733.120
Exports
SUBPART C: STANDARDS FOR LARGE QUANTITY HANDLERS
Section
733.130
Applicability
733.131
Prohibitions
733.132
Notification
733.133
Waste Management
733.134
Labeling and Marking
733.135
Accumulation Time Limits
733.136
Employee Training
733.137
Response to Releases
733.138
Off-Site Shipments
733.139
Tracking Universal Waste Shipments
733.140
Exports
SUBPART D: STANDARDS FOR UNIVERSAL WASTE
TRANSPORTERS
Section
733.150
Applicability
733.151
Prohibitions
733.152
Waste Management
733.153
Accumulation Time Limits
733.154
Response to Releases
733.155
Off-site Shipments
733.156
Exports
SUBPART E: STANDARDS FOR DESTINATION FACILITIES
Section
733.160
Applicability
733.161
Off-Site Shipments
733.162
Tracking Universal Waste Shipments
SUBPART F: IMPORT REQUIREMENTS
Section
733.170
Imports
412
SUBPART G: PETITIONS TO INCLUDE OTHER WASTES
Section
733.180
General
733.181
Factors for Petitions to Include Other Wastes
AUTHORITY: Implementing Sections 7.2, 22.4 and 22.23a and authorized by Section 27 of
the Environmental Protection Act [415 ILCS 5/7.2, 22.4, 22.23a, and 27].
SOURCE: Adopted in R95-20 at 20 Ill. Reg. 11291, effective August 1, 1996; amended in
R96-10/R97-3/R97-5 at 22 Ill. Reg. 944, effective December 16, 1997; amended in R98-12 at
22 Ill. Reg. 7650, effective April 15, 1998; amended in R99-15 at 23 Ill. Reg. 9502, effective
July 26, 1999; amended in R00-13 at 24 Ill. Reg. ________, effective
______________________.
SUBPART A: GENERAL
Section 733.101
Scope
a)
This Part establishes requirements for managing the following:
1)
Batteries, as described in Section 733.102;
2)
Pesticides, as described in Section 733.103;
3)
Thermostats, as described in Section 733.104; and
4)
Mercury-containing lampsLamps, as described in Section 733.107
733.105.
BOARD NOTE: Subsection (a)(4) of this Section was added pursuant to
Section 22.23a of the Act [415 ILCS 5/22.23a] (see P.A. 90-502,
effective August 19, 1997).
b)
This Part provides an alternative set of management standards in lieu of
regulation under 35 Ill. Adm. Code 702 through 705, 720 through 726, and
728.
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
Section 733.102
Applicability--Batteries
a)
Batteries covered under this Part.
1)
The requirements of this Part apply to persons managing batteries, as
described in Section 733.106 733.109, except those listed in subsection
413
(b) below of this Section.
2)
Spent lead-acid batteries that are not managed under 35 Ill. Adm. Code
726.Subpart G, are subject to management under this Part.
b)
Batteries not covered under this Part. The requirements of this Part do not apply
to persons managing the following batteries:
1)
Spent lead-acid batteries that are managed under 35 Ill. Adm. Code
726.Subpart G.
2)
Batteries, as described in Section 733.106 733.109, that are not yet
wastes under 35 Ill. Adm. Code 721, including those that do not meet the
criteria for waste generation in subsection (c) below of this Section.
3)
Batteries, as described in Section 733.106 733.109, that are not
hazardous waste. A battery is a hazardous waste if it exhibits one or
more of the characteristics identified in 35 Ill. Adm. Code 721.Subpart
C.
c)
Generation of waste batteries.
1)
A used battery becomes a waste on the date it is discarded (e.g., when
sent for reclamation).
2)
An unused battery becomes a waste on the date the handler decides to
discard it.
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
Section 733.103
Applicability--Pesticides
a)
Pesticides covered under this Part. The requirements of this Part apply to
persons managing pesticides, as described in Section 733.106 733.109, that meet
the following conditions, except those listed in subsection (b) below of this
Section:
1)
Recalled pesticides:
A)
Stocks of a suspended and canceled pesticide that are part of a
voluntary or mandatory recall under Section 19(b) of the Federal
Insecticide, Fungicide and Rodenticide Act (FIFRA; 7 U.S.C.
§ USC 136q), including, but not limited to those owned by the
registrant responsible for conducting the recall; or
414
B)
Stocks of a suspended or cancelled pesticide, or a pesticide that is
not in compliance with FIFRA, that are part of a voluntary recall
by the registrant.
2)
Stocks of other unused pesticide products that are collected and managed
as part of a waste pesticide collection program.
b)
Pesticides not covered under this Part. The requirements of this Part do not
apply to persons managing the following pesticides:
1)
Recalled pesticides described in subsection (a)(1) above of this Section,
and unused pesticide products described in subsection (a)(2) above of this
Section, that are managed by farmers in compliance with 35 Ill. Adm.
Code 722.170. (35 Ill. Adm. Code 722.170 addresses pesticides
disposed of on the farmer’s own farm in a manner consistent with the
disposal instructions on the pesticide label, providing the container is
triple rinsed in accordance with 35 Ill. Adm. Code 721.107(b)(3).);
2)
Pesticides not meeting the conditions set forth in subsection (a) above of
this Section must be managed in compliance with the hazardous waste
regulations in 35 Ill. Adm. Code 702 through 705, 720 through 726, and
728;
3)
Pesticides that are not wastes under 35 Ill. Adm. Code 721, including
those that do not meet the criteria for waste generation in subsection (c)
below of this Section or those that are not wastes as described in
subsection (d) below of this Section; and
4)
Pesticides that are not hazardous waste. A pesticide is a hazardous waste
if it is a waste (see subsection (b)(3) above of this Section) and either it is
listed in 35 Ill. Adm. Code 721.Subpart D or it exhibits one or more of
the characteristics identified in 35 Ill. Adm. Code 721.Subpart C.
c)
When a pesticide becomes a waste.
1)
A recalled pesticide described in subsection (a)(1) above of this Section
becomes a waste on the first date on which both of the following
conditions apply:
A)
The generator of the recalled pesticide agrees to participate in the
recall; and
B)
The person conducting the recall decides to discard (e.g., burn the
pesticide for energy recovery).
415
2)
An unused pesticide product described in subsection (a)(2) above of this
Section becomes a waste on the date the generator decides to discard it.
d)
Pesticides that are not wastes. The following pesticides are not wastes:
1)
Recalled pesticides described in subsection (a)(1) above of this Section,
provided that:
A)
The person conducting the recall has not made a decision to
discard the pesticide (e.g., burn it for energy recovery). Until
such a decision is made, the pesticide does not meet the definition
of “solid waste” under 35 Ill. Adm. Code 721.102; thus the
pesticide is not a hazardous waste and is not subject to hazardous
waste requirements, including those of this Part. This pesticide
remains subject to the requirements of FIFRA; or
B)
The person conducting the recall has made a decision to use a
management option that, under 35 Ill. Adm. Code 721.102, does
not cause the pesticide to be a solid waste (i.e., the selected option
is use (other than use constituting disposal) or reuse (other than
burning for energy recovery) or reclamation). Such a pesticide is
not a solid waste and therefore is not a hazardous waste, and is
not subject to the hazardous waste requirements including this
Part. This pesticide, including a recalled pesticide that is exported
to a foreign destination for use or reuse, remains subject to the
requirements of FIFRA.
2)
Unused pesticide products described in subsection (a)(2) above of this
Section, if the generator of the unused pesticide product has not decided
to discard them (e.g., burn for energy recovery). These pesticides
remain subject to the requirements of FIFRA.
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
Section 733.104
Applicability--Mercury Thermostats
a)
Thermostats covered under this Part. The requirements of this Part apply to
persons managing thermostats, as described in Section 733.106 733.109, except
those listed in subsection (b) below of this Section.
b)
Thermostats not covered under this Part. The requirements of this Part do not
apply to persons managing the following thermostats:
1)
Thermostats that are not yet wastes under 35 Ill. Adm. Code 721.
Subsection (c) below of this Section describes when thermostats become
416
wastes.
2)
Thermostats that are not hazardous waste. A thermostat is a hazardous
waste if it is a waste (see subsection (b)(1) above of this Section) and it
exhibits one or more of the characteristics identified in 35 Ill. Adm. Code
721.Subpart C.
c)
Generation of waste thermostats.
1)
A used thermostat becomes a waste on the date it is discarded (e.g., sent
for reclamation).
2)
An unused thermostat becomes a waste on the date the handler decides to
discard it.
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
Section 733.105 Applicability--Lamps.
a) Lamps covered under this Part. The requirements of this Part apply to persons
that manage lamps, as described in Section 733.109, except those listed in
subsection (b) of this Section.
b) Lamps not covered under this Part. The requirements of this Part do not apply
to persons that manage the following lamps:
1) Lamps that are not yet wastes under 35 Ill. Adm. Code 721, as provided
in subsection (c) of this Section.
2) Lamps that are not hazardous waste. A lamp is a hazardous waste if it
exhibits one or more of the characteristics identified in 35 Ill. Adm. Code
721.Subpart C.
c) Generation of waste lamps.
1) A used lamp becomes a waste on the date it is discarded.
2) An unused lamp becomes a waste on the date the handler decides to
discard it.
(Source: Former Section 733.105 renumbered to Section 733.108 and amended and new
Section 733.105 added at 24 Ill. Reg. ________, effective ______________________)
417
Section 733.107
Applicability--Mercury-Containing Lamps (Repealed)
a) Mercury-containing lamps covered under this Part. The requirements of this
Part apply to persons managing mercury-containing lamps, except those listed in
subsection (b) of this Section.
b) Mercury-containing lamps not covered under this Part. The requirements of this
Part do not apply to persons managing the following mercury-containing lamps:
1) Mercury-containing lamps that are not yet wastes under 35 Ill. Adm.
Code 721, including those that do not meet the criteria for waste
generation in subsection (c) of this Section.
2) Mercury-containing lamps that are not hazardous waste. A mercury-
containing lamp is not a hazardous waste if it does not exhibit one or
more of the characteristics identified in 35 Ill. Adm. Code 721.Subpart
C.
c) Generation of waste mercury-containing lamps.
1) A used mercury-containing lamp becomes a waste on the date the handler
permanently removes it from its fixture.
2) An unused mercury-containing lamp becomes a waste on the date the
handler decides to discard it.
BOARD NOTE: Section 733.107 was added pursuant to Section 22.23a of the Act
[415 ILCS 5/22.23a] (see P.A. 90-502, effective August 19, 1997).
(Source: Repealed at 22 Ill. Reg. ________, effective ______________________)
Section 733.105 Applicability--Household and Conditionally Exempt Small Quantity
Generator Waste
Section 733.108 Applicability--Household and Conditionally Exempt Small Quantity
Generator Waste
a)
Persons managing A person that manages any of the wastes listed below may, at
their its option, manage them the waste under the requirements of this Part:
1)
Household wastes that are exempt under 35 Ill. Adm. Code
721.104(b)(1) and which are also of the same type as the universal wastes
defined at Section 733.106 733.109; or
2)
Conditionally exempt small quantity generator wastes that are exempt
under 35 Ill. Adm. Code 721.105 and are also of the same type as the
418
universal wastes defined at Section 733.106 733.109.
b)
Persons A person that commingle commingles the wastes described in
subsections (a)(1) and (a)(2) above of this Section together with universal waste
regulated under this Part shall manage the commingled waste under the
requirements of this Part.
(Source: Renumbered from Section 733.105 and amended at 24 Ill. Reg. ________, effective
______________________)
Section 733.106 Definitions
Section 733.109 Definitions
“Battery” means a device consisting of one or more electrically connected
electrochemical cells which 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.
“Destination facility” means a facility that treats, disposes of, or recycles a
particular category of universal waste, except those management activities
described in Sections 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 purposes of managing that category of universal waste.
“Electric lamp” means the bulb or tube portion of a lighting device specifically
designed to produce radiant energy, most often in the ultraviolet, visible, and
infrared regions of the electromagnetic spectrum.
BOARD NOTE: The definition of “electric lamp” was added pursuant to
Section 22.23a of the Act [415 ILCS 5/22.23a] (see P.A. 90-502, effective
August 19, 1997).
“FIFRA” means the Federal Insecticide, Fungicide, and Rodenticide Act (7 USC
136 through 136y).
“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.
“Lamp” or “universal waste lamp” is defined as 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. Common examples of universal waste electric lamps
419
include, but are not limited to, fluorescent, high intensity discharge, neon,
mercury vapor, high pressure sodium, and metal halide lamps.
“Large quantity handler of universal waste” means a universal waste handler (as
defined in this Section) that accumulates 5,000 kilograms or more total of
universal waste (batteries, pesticides, thermostats, or mercury-containing lamps,
calculated collectively) at any time. This designation as a large quantity handler
of universal waste is retained through the end of the calendar year in which
5,000 kilograms or more total of universal waste is accumulated.
BOARD NOTE: Mercury-containing lamps were added pursuant to Section
22.23a of the Act [415 ILCS 5/22.23a] (see P.A. 90-502, effective August 19,
1997).
“Mercury-containing lamp” means an electric lamp into which mercury is
purposely introduced by the manufacturer for the operation of the lamp.
Mercury-containing lamps include, but are not limited to, fluorescent lamps and
high-intensity discharge lamps.
BOARD NOTE: The definition of “mercury-containing lamp” was added
pursuant to Section 22.23a of the Act [415 ILCS 5/22.23a] (see P.A. 90-502,
effective August 19, 1997).
“On-site” means the same or geographically contiguous property that may be
divided by public or private right-of-way, provided that the entrance and exit
between the properties is at a cross-roads intersection, and access is by crossing
as opposed to going along the right of way. Non-contiguous properties, owned
by the same person but connected by a right-of-way that that person controls and
to which the public does not have access, are also considered on-site property.
“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 35 Ill. Adm. Code 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
360b(j), incorporated by reference in Section 35 Ill. Adm. Code 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 35 Ill. Adm. Code 720.111, that
bears or contains any substances described in either of the two preceding
420
paragraphs of this definition.
BOARD NOTE: The second exception of corresponding 40 CFR 273.6
reads as follows: “Is an animal drug that has been determined by
regulation of the Secretary of Health and Human Services not to be a
new animal drug”. This is very similar to the language of Section 2(u) of
the Federal Insecticide, Fungicide, and Rodenticide Act (FIFRA; 7 USC
136(u)). The three exceptions, taken together, appear intended not to
include as “pesticide” any material within the scope of federal Food and
Drug Administration regulation. The Board codified this provision with
the intent of retaining the same meaning as its federal counterpart while
adding the definiteness required under Illinois law.
“Small quantity handler of universal waste” means a universal waste handler (as
defined in this Section) that does not accumulate 5,000 kilograms or more total of
universal waste (batteries, pesticides, thermostats, or mercury-containing lamps,
calculated collectively) at any time.
BOARD NOTE: Mercury-containing lamps were added pursuant to Section
22.23a of the Act [415 ILCS 5/22.23a] (see P.A. 90-502, effective August 19,
1997).
“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 Section 733.113(c)(2) or
733.133(c)(2).
“Universal waste” means any of the following hazardous wastes that are subject
to the universal waste requirements of this Part:
Batteries, as described in Section 733.102;
Pesticides, as described in Section 733.103;
Thermostats, as described in Section 733.104; and
Mercury-containing lampsLamps, as described in Section 733.107
733.105.
BOARD NOTE: Mercury-containing lamps were added as universal
waste pursuant to Section 22.23a of the Act [415 ILCS 5/22.23a] (see
P.A. 90-502, effective August 19, 1997).
“Universal waste handler” means either of the following:
A generator (as defined in this Section) of universal waste; or
421
The owner or operator of a facility, including all contiguous property,
that receives universal waste from other universal waste handlers,
accumulates universal waste, and sends 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 transfer facility” means any transportation-related facility
including loading docks, parking areas, storage areas, and other similar areas
where shipments of universal waste are held during the normal course of
transportation for ten days or less.
“Universal waste transporter” means a person engaged in the off-site
transportation of universal waste by air, rail, highway, or water.
(Source: Renumbered from Section 733.106 and amended at 24 Ill. Reg. ________, effective
______________________)
SUBPART B: STANDARDS FOR SMALL QUANTITY HANDLERS
Section 733.110
Applicability
This Subpart applies to small quantity handlers of universal waste (as defined in Section
733.106 733.109).
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
Section 733.113
Waste Management
a)
Universal waste batteries. A small quantity handler of universal waste shall
manage universal waste batteries in a way manner that prevents releases of any
universal waste or component of a universal waste to the environment, as
follows:
1)
A small quantity handler of universal waste shall contain any universal
422
waste battery that shows evidence of leakage, spillage, or damage that
could cause leakage under reasonably foreseeable conditions in a
container. The container must be closed, structurally sound, compatible
with the contents of the battery, and must lack evidence of leakage,
spillage, or damage that could cause leakage under reasonably foreseeable
conditions.
2)
A small quantity handler of universal waste may conduct the following
activities, as long as the casing of each individual battery cell is not
breached and remains intact and closed (except that cells may be opened
to remove electrolyte but must be immediately closed after removal):
A)
Sorting batteries by type;
B)
Mixing battery types in one container;
C)
Discharging batteries so as to remove the electric charge;
D)
Regenerating used batteries;
E)
Disassembling batteries or battery packs into individual batteries
or cells;
F)
Removing batteries from consumer products; or
G)
Removing electrolyte from batteries.
3)
A small quantity handler of universal waste that removes electrolyte from
batteries, or that generates other solid waste (e.g., battery pack materials,
discarded consumer products) as a result of the activities listed above,
shall determine whether the electrolyte or other solid waste exhibits a
characteristic of hazardous waste identified in 35 Ill. Adm. Code
721.Subpart C.
A)
If the electrolyte or other solid waste exhibits a characteristic of
hazardous waste, it is subject to all applicable requirements of 35
Ill. Adm. Code 702 through 705, 720 through 726, and 728. The
handler is considered the generator of the hazardous electrolyte or
other waste and is subject to 35 Ill. Adm. Code 722.
B)
If the electrolyte or other solid waste is not hazardous, the handler
may manage the waste in any way that is in compliance with
applicable federal, state State, or local solid (nonhazardous) waste
regulations.
423
BOARD NOTE: See generally the Act and 35 Ill. Adm. Code
807 through 817 to determine whether additional facility siting,
special waste, or nonhazardous waste regulations apply to the
waste. Consult the ordinances of relevant units of local
government to determine whether local requirements apply.
b)
Universal waste pesticides. A small quantity handler of universal waste shall
manage universal waste pesticides in a way that prevents releases of any
universal waste or component of a universal waste to the environment. The
universal waste pesticides must be contained in one or more of the following:
1)
A container that remains closed, structurally sound, compatible with the
pesticide, and that lacks evidence of leakage, spillage, or damage that
could cause leakage under reasonably foreseeable conditions;
2)
A container that does not meet the requirements of subsection (b)(1)
above of this Section, provided that the unacceptable container is
overpacked in a container that does meet the requirements of subsection
(b)(1);
3)
A tank that meets the requirements of 35 Ill. Adm. Code 725.Subpart J,
except for 35 Ill. Adm. Code 725.297(c), 265.300, and 265.301; or
4)
A transport vehicle or vessel that is closed, structurally sound, compatible
with the pesticide, and that lacks evidence of leakage, spillage, or damage
that could cause leakage under reasonably foreseeable conditions.
c)
Universal waste thermostats. A small quantity handler of universal waste shall
manage universal waste thermostats in a way that prevents releases of any
universal waste or component of a universal waste to the environment, as
follows:
1)
A small quantity handler of universal waste shall contain any universal
waste thermostat that shows evidence of leakage, spillage, or damage that
could cause leakage under reasonably foreseeable conditions in a
container. The container must be closed, structurally sound, compatible
with the contents of the thermostat, and must lack evidence of leakage,
spillage, or damage that could cause leakage under reasonably foreseeable
conditions.
2)
A small quantity handler of universal waste may remove mercury-
containing ampules from universal waste thermostats provided the handler
follows each of the following procedures:
A)
It removes the ampules in a manner designed to prevent breakage
424
of the ampules;
B)
It removes ampules only over or in a containment device (e.g.,
tray or pan sufficient to collect and contain any mercury released
from an ampule in case of breakage);
C)
It ensures that a mercury clean-up system is readily available to
immediately transfer any mercury resulting from spills or leaks
from broken ampules, from the containment device to a container
that meets the requirements of 35 Ill. Adm. Code 722.134;
D)
It immediately transfers any mercury resulting from spills or leaks
from broken ampules from the containment device to a container
that meets the requirements of 35 Ill. Adm. Code 722.134;
E)
It ensures that the area in which ampules are removed is well
ventilated and monitored to ensure compliance with applicable
OSHA exposure levels for mercury;
F)
It ensures that employees removing ampules are thoroughly
familiar with proper waste mercury handling and emergency
procedures, including transfer of mercury from containment
devices to appropriate containers;
G)
It stores removed ampules in closed, non-leaking containers that
are in good condition; and
H)
It packs removed ampules in the container with packing materials
adequate to prevent breakage during storage, handling, and
transportation.
3)
Required hazardous waste determination and further waste management.
A)
A small quantity handler of universal waste that removes mercury-
containing ampules from thermostats shall determine whether the
following exhibit a characteristic of hazardous waste identified in
35 Ill. Adm. Code 721.Subpart C:
i)
Mercury or clean-up residues resulting from spills or
leaks; or
ii)
Other solid waste generated as a result of the removal of
mercury-containing ampules (e.g., remaining thermostat
units).
425
B)
If the mercury, residues, or other solid waste exhibits a
characteristic of hazardous waste, it must be managed in
compliance with all applicable requirements of 35 Ill. Adm. Code
702 through 705, 720 through 726, and 728. The handler is
considered the generator of the mercury, residues, or other waste
and shall manage it is as subject to 35 Ill. Adm. Code 722.
C)
If the mercury, residues, or other solid waste is not hazardous, the
handler may manage the waste in any way that is in compliance
with applicable federal, state State, or local solid (nonhazardous)
waste regulations.
BOARD NOTE: See generally the Act and 35 Ill. Adm. Code
807 through 817 to determine whether additional facility siting,
special waste, or nonhazardous waste regulations apply to the
waste. Consult the ordinances of relevant units of local
government to determine whether local requirements apply.
d)
Universal waste mercury-containing lamps. Lamps. A small quantity handler of
universal waste shall manage universal waste mercury-containing lamps in a
manner that prevents releases of any universal waste or component of a universal
waste to the environment, as follows:
1)
A small quantity handler of universal waste mercury-containing lamps
shall, at all times: contain all lamps in containers or packages that are
structurally sound, adequate to prevent breakage, and compatible with the
contents of the lamps. Such containers and packages must remain closed
and must lack evidence of leakage, spillage, or damage that could cause
leakage under reasonably foreseeable conditions.
A) Contain unbroken lamps in packaging that will minimize breakage
during normal handling conditions; and
B) Contain broken lamps in packaging that will prevent releases of
lamp fragments and residues.
2)
A small quantity handler of universal waste mercury-containing lamps
shall, at all times, manage waste lamps in a manner designed to minimize
lamp breakage immediately clean up and place in a container any lamp
that is broken, and the small quantity handler shall place in a container
any lamp that shows evidence of breakage, leakage, or damage that could
cause the release of mercury or other hazardous constituents to the
environment. Any container used must be closed, structurally sound,
compatible with the contents of the lamps, and must lack evidence of
leakage, spillage, or damage that could cause leakage or releases of
426
mercury or other hazardous constituents to the environment under
reasonably foreseeable conditions.
3) A small quantity handler of universal waste mercury-containing lamps
shall immediately contain all releases of lamp fragments and residues from
broken lamps.
4) A small quantity handler of universal wastes shall undertake hazardous
waste determination and further waste management as follows:
A) A small quantity handler of universal waste mercury-containing
lamps shall determine whether the following exhibit a
characteristic of hazardous waste identified in 35 Ill. Adm. Code
721.Subpart C:
i) Any materials resulting from a release;
ii) Clean-up residues from spills or breakage; or
iii) Other solid waste generated as a result of handling waste
lamps.
B) If the material, residue, or other solid waste exhibits a
characteristic of hazardous waste, it shall be managed in
compliance with all applicable requirements of 35 Ill. Adm. Code
702 through 705, 720 through 726, and 728. The handler is
considered to be the generator of the material, residue, or other
hazardous waste and shall manage it in accordance with 35 Ill.
Adm. Code 722.
C) If the material, residue, or other solid waste is not hazardous, the
handler may manage the waste in any manner that is in
compliance with applicable federal, State, or local solid
(nonhazardous) waste regulations.
53)
Small quantity handlers of mercury containing universal waste lamps may
treat mercury containing those lamps for volume reduction at the site
where they were generated under the following conditions:
A)
The lamps must be crushed in a closed system designed and
operated in such a manner that any emission of mercury from the
crushing system shall not exceed 0.1 mg/m
3
when measured on
the basis of time weighted average over an 8-hour period;
B)
The handler must provide notification of crushing activity to the
427
Agency quarterly, in a form as provided by the Agency. Such
notification must include the following information:
i)
Name and address of the handler;
ii)
Estimated monthly amount of lamps crushed; and
iii)
The technology employed for crushing, including any
certification or testing data provided by the manufacturer
of the crushing unit verifying that the crushing device
achieves the emission controls required in subsection
(d)(5)(A) of this Section;
C)
The handler immediately transfers any material recovered from a
spill or leak to a container that meets the requirements of 40 CFR
262.34, and has available equipment necessary to comply with this
requirement;
D)
The handler ensures that the area in which the lamps are crushed
is well-ventilated and monitored to ensure compliance with
applicable OSHA exposure levels for mercury;
E)
The handler ensures that employees crushing lamps are
thoroughly familiar with proper waste mercury handling and
emergency procedures, including transfer of mercury from
containment devices to appropriate containers; and
F)
The crushed lamps are stored in closed, non-leaking containers
that are in good condition (e.g., no severe rusting, apparent
structural defects or deterioration), suitable to prevent releases
during storage, handling and transportation.
BOARD NOTE: Subsection (d) of this Section was added pursuant to Section
22.23a of the Act [415 ILCS 5/22.23a] (see P.A. 90-502, effective August 19,
1997).
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
Section 733.114
Labeling and Marking
A small quantity handler of universal waste shall label or mark the universal waste to identify
the type of universal waste as follows:
a)
Universal waste batteries (i.e., each battery) or a container in which the batteries
are contained must be labeled or marked clearly with any one of the following
428
phrases: “Universal Waste-Battery(ies)Batteries”, “Waste Battery(ies) Batteries”,
or “Used Battery(ies) Batteries”;
b)
A container (or multiple container package unit), tank, transport vehicle, or
vessel in which recalled universal waste pesticides, as described in Section
733.103(a)(1), are contained must be labeled or marked clearly as follows:
1)
The label that was on or accompanied the product as sold or distributed;
and
2)
The words “Universal Waste-Pesticide(s)Pesticides” or “Waste-
Pesticide(s)Pesticides”;
c)
A container, tank, or transport vehicle, or vessel in which unused pesticide
products, as described in Section 733.103(a)(2), are contained must be labeled or
marked clearly as follows:
1)
Pesticide labeling:
A)
The label that was on the product when purchased, if still legible;
B)
If using the labels described in subsection (c)(1)(A) above of this
Section is not feasible, the appropriate label as required under
USDOT regulation 49 CFR 172; or
C)
If using the labels described in subsections (c)(1)(A) and (c)(1)(B)
above of this Section is not feasible, another label prescribed or
designated by the waste pesticide collection program administered
or recognized by a state; and
2)
The words “Universal Waste-Pesticide(s)Pesticides” or “Waste-
Pesticide(s)Pesticides”;
d)
Universal waste thermostats (i.e., each thermostat) or a container in which the
thermostats are contained must be labeled or marked clearly with any one of the
following phrases: “Universal Waste-Mercury Thermostat(s) Thermostats”, or
“Waste Mercury Thermostat(s) Thermostats”, or “Used Mercury Thermostat(s)
Thermostats”; and
e)
Universal waste mercury-containing lamps Each lamp or a container or package
in which the such lamps are contained shall must be labeled or clearly marked
with any one of the following phrases: “Universal Waste--Mercury-Containing
Lamp(s)Lamps”, “Waste Mercury-Containing Lamp(s)Lamps” or “Used
Mercury-Containing Lamp(s)Lamps”.
429
BOARD NOTE: Subsection (e) of this Section was added pursuant to Section
22.23a of the Act [415 ILCS 5/22.23a] (see P.A. 90-502, effective August 19,
1997).
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
SUBPART C: STANDARDS FOR LARGE QUANTITY HANDLERS
Section 733.130
Applicability
This subpart applies to large quantity handlers of universal waste (as defined in Section 733.106
733.109).
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
Section 733.132
Notification
a)
Written notification of universal waste management.
1)
Except as provided in subsections (a)(2) and (a)(3) below of this Section,
a large quantity handler of universal waste shall have sent written
notification of universal waste management to the Agency, and received a
USEPA Identification Number, before meeting or exceeding the 5,000
kilogram storage limit.
2)
A large quantity handler of universal waste that has already notified
USEPA or the Agency of its hazardous waste management activities and
has received a USEPA Identification Number is not required to renotify
under this Section.
3)
A large quantity handler of universal waste that manages recalled
universal waste pesticides, as described in Section 733.103(a)(1), and that
has sent notification to USEPA or the Agency, as required by 40 CFR
165, is not required to notify for those recalled universal waste pesticides
under this Section.
b)
This notification must include:
1)
The universal waste handler’s name and mailing address;
2)
The name and business telephone number of the person at the universal
waste handler’s site who should be contacted regarding universal waste
management activities;
430
3)
The address or physical location of the universal waste management
activities;
4)
A list of all of the types of universal waste managed by the handler (e.g,
batteries, pesticides, thermostats, and or mercury-containing lamps); and
5)
A statement indicating that the handler is accumulating more than 5,000
kilograms of universal waste at one time and the types of universal waste
(e.g, batteries, pesticides, thermostats, or mercury-containing lamps) the
handler is accumulating above this quantity.
BOARD NOTE: At 60 Fed. Reg. 25520-21 (May 11, 1995), USEPA
explained the generator or consolidation point may use USEPA Form 8700-12
for notification. (To obtain USEPA Form 8700-12 call the Agency at 217-782-
6761.) USEPA further explained that it is not necessary for the handler to
aggregate the amounts of waste at multiple non-contiguous sites for the purposes
of the 5,000 kilogram determination. Mercury-containing lamps were added as
universal waste pursuant to Section 22.23a of the Act [415 ILCS 5/22.23a] (see
P.A. 90-502, effective August 19, 1997).
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
Section 733.133
Waste Management
a)
Universal waste batteries. A large quantity handler of universal waste shall
manage universal waste batteries in a way manner that prevents releases of any
universal waste or component of a universal waste to the environment, as
follows:
1)
A large quantity handler of universal waste shall contain any universal
waste battery that shows evidence of leakage, spillage, or damage that
could cause leakage under reasonably foreseeable conditions in a
container. The container must be closed, structurally sound, compatible
with the contents of the battery, and must lack evidence of leakage,
spillage, or damage that could cause leakage under reasonably foreseeable
conditions.
2)
A large quantity handler of universal waste may conduct the following
activities, as long as the casing of each individual battery cell is not
breached and remains intact and closed (except that cells may be opened
to remove electrolyte but must be immediately closed after removal):
A)
Sorting batteries by type;
B)
Mixing battery types in one container;
431
C)
Discharging batteries so as to remove the electric charge;
D)
Regenerating used batteries;
E)
Disassembling batteries or battery packs into individual batteries
or cells;
F)
Removing batteries from consumer products; or
G)
Removing electrolyte from batteries.
3)
A large quantity handler of universal waste that removes electrolyte from
batteries or that generates other solid waste (e.g., battery pack materials,
discarded consumer products) as a result of the activities listed above shall
determine whether the electrolyte or other solid waste exhibits a
characteristic of hazardous waste identified in 35 Ill. Adm. Code
721.Subpart C.
A)
If the electrolyte or other solid waste exhibits a characteristic of
hazardous waste, it must be managed in compliance with all
applicable requirements of 35 Ill. Adm. Code 702 through 705,
720 through 726, and 728. The handler is considered the
generator of the hazardous electrolyte or other waste and is
subject to 35 Ill. Adm. Code 722.
B)
If the electrolyte or other solid waste is not hazardous, the handler
may manage the waste in any way that is in compliance with
applicable federal, state State, or local solid (nonhazardous) waste
regulations.
BOARD NOTE: See generally the Act and 35 Ill. Adm. Code
807 through 817 to determine whether additional facility siting,
special waste, or nonhazardous waste regulations apply to the
waste. Consult the ordinances of relevant units of local
government to determine whether local requirements apply.
b)
Universal waste pesticides. A large quantity handler of universal waste shall
manage universal waste pesticides in a way manner that prevents releases of any
universal waste or component of a universal waste to the environment. The
universal waste pesticides must be contained in one or more of the following:
1)
A container that remains closed, structurally sound, compatible with the
pesticide, and that lacks evidence of leakage, spillage, or damage that
could cause leakage under reasonably foreseeable conditions;
432
2)
A container that does not meet the requirements of subsection (b)(1)
above of this Section, provided that the unacceptable container is
overpacked in a container that does meet the requirements of subsection
(b)(1);
3)
A tank that meets the requirements of 35 Ill. Adm. Code 725.Subpart J,
except for 35 Ill. Adm. Code 725.297(c), 725.300, and 725.301; or
4)
A transport vehicle or vessel that is closed, structurally sound, compatible
with the pesticide, and that lacks evidence of leakage, spillage, or damage
that could cause leakage under reasonably foreseeable conditions.
c)
Universal waste thermostats. A large quantity handler of universal waste shall
manage universal waste thermostats in a way manner that prevents releases of
any universal waste or component of a universal waste to the environment, as
follows:
1)
A large quantity handler of universal waste shall contain any universal
waste thermostat that shows evidence of leakage, spillage, or damage that
could cause leakage under reasonably foreseeable conditions in a
container. The container must be closed, structurally sound, compatible
with the contents of the thermostat, and must lack evidence of leakage,
spillage, or damage that could cause leakage under reasonably foreseeable
conditions.
2)
A large quantity handler of universal waste may remove mercury-
containing ampules from universal waste thermostats provided the handler
follows each of the following procedures:
A)
It removes the ampules in a manner designed to prevent breakage
of the ampules;
B)
It removes ampules only over or in a containment device (e.g.,
tray or pan sufficient to collect and contain any mercury released
from an ampule in case of breakage);
C)
It ensures that a mercury clean-up system is readily available to
immediately transfer any mercury resulting from spills or leaks
from broken ampules, from the containment device to a container
that meets the requirements of 35 Ill. Adm. Code 722.134;
D)
It immediately transfers any mercury resulting from spills or leaks
from broken ampules from the containment device to a container
that meets the requirements of 35 Ill. Adm. Code 722.134;
433
E)
It ensures that the area in which ampules are removed is well
ventilated and monitored to ensure compliance with applicable
OSHA exposure levels for mercury;
F)
It ensures that employees removing ampules are thoroughly
familiar with proper waste mercury handling and emergency
procedures, including transfer of mercury from containment
devices to appropriate containers;
G)
It stores removed ampules in closed, non-leaking containers that
are in good condition; and
H)
It packs removed ampules in the container with packing materials
adequate to prevent breakage during storage, handling, and
transportation.
3)
Required hazardous waste determination and further waste management.
A)
A large quantity handler of universal waste that removes mercury-
containing ampules from thermostats shall determine whether the
following exhibit a characteristic of hazardous waste identified in
35 Ill. Adm. Code 721.Subpart C:
i)
Mercury or clean-up residues resulting from spills or
leaks; or
ii)
Other solid waste generated as a result of the removal of
mercury-containing ampules (e.g., remaining thermostat
units).
B)
If the mercury, residues, or other solid waste exhibits a
characteristic of hazardous waste, it must be managed in
compliance with all applicable requirements of 35 Ill. Adm. Code
702 through 705, 720 through 726, and 728. The handler is
considered the generator of the mercury, residues, or other waste
and is subject to 35 Ill. Adm. Code 722.
C)
If the mercury, residues, or other solid waste is not hazardous, the
handler may manage the waste in any way that is in compliance
with applicable federal, state State, or local solid (nonhazardous)
waste regulations.
BOARD NOTE: See generally the Act and 35 Ill. Adm. Code
807 through 817 to determine whether additional facility siting,
434
special waste, or nonhazardous waste regulations apply to the
waste. Consult the ordinances of relevant units of local
government to determine whether local requirements apply.
d)
Universal waste mercury-containing lamps. Lamps. A large quantity handler of
universal waste shall manage universal waste mercury-containing lamps in a
manner that prevents releases of any universal waste or component of a universal
waste to the environment, as follows:
1)
A large quantity handler of universal waste mercury-containing lamps
shall, at all times: contain all lamps in containers or packages that are
structurally sound, adequate to prevent breakage, and compatible with the
contents of the lamps. Such containers and packages must remain closed
and must lack evidence of leakage, spillage, or damage that could cause
leakage under reasonably foreseeable conditions.
A) Contain unbroken lamps in packaging that will minimize breakage
during normal handling conditions; and
B) Contain broken lamps in packaging that will prevent releases of
lamp fragments and residues.
2)
A large quantity handler of universal waste mercury-containing lamps
shall, at all times, manage waste lamps in a manner designed to minimize
lamp breakage immediately clean up and place in a container any lamp
that is broken, and the large quantity handler shall place in a container
any lamp that shows evidence of breakage, leakage, or damage that could
cause the release of mercury or other hazardous constituents to the
environment. Any container used must be closed, structurally sound,
compatible with the contents of the lamps, and must lack evidence of
leakage, spillage, or damage that could cause leakage or releases of
mercury or other hazardous constituents to the environment under
reasonably foreseeable conditions.
3) A large quantity handler of universal waste mercury-containing lamps
shall immediately contain all releases of lamp fragments and residues from
broken lamps.
4) A large quantity handler of universal waste shall undertake a hazardous
waste determination and further waste management as follows:
A) A large quantity handler of universal waste mercury-containing
lamps shall determine whether the following exhibit a
characteristic of hazardous waste identified in 35 Ill. Adm. Code
721.Subpart C:
435
i) Any materials resulting from a release;
ii) Clean-up residues from spills or breakage; or
iii) Other solid waste generated as a result of handling waste
lamps.
B) If the material, residue, or other solid waste exhibits a
characteristic of hazardous waste, it shall be managed in
compliance with all applicable requirements of 35 Ill. Adm. Code
702 through 705, 720 through 726, and 728. The handler is
considered to be the generator of the material, residue, or other
hazardous waste and shall manage it in accordance with 35 Ill.
Adm. Code 722.
C) If the material, residue, or other solid waste is not hazardous, the
handler may manage the waste in any manner that is in
compliance with applicable federal, State, or local solid
(nonhazardous) waste regulations.
53)
Large quantity handlers of mercury containing universal waste lamps may
treat mercury containing those lamps for volume reduction at the site
where they were generated under the following conditions:
A)
The lamps must be crushed in a closed system designed and
operated in such a manner that any emission of mercury from the
crushing system shall not exceed 0.1 mg/m
3
when measured on
the basis of time weighted average over an 8-hour period;
B)
The handler must provide notification of crushing activity to the
Agency quarterly, in a form as provided by the Agency. Such
notification must include the following information:
i)
Name and address of the handler;
ii)
Estimated monthly amount of lamps crushed; and
iii)
The technology employed for crushing, including any
certification or testing data provided by the manufacturer
of the crushing unit verifying that the crushing device
achieves the emission controls required in subsection
(d)(5)(A) of this Section;
C)
The handler immediately transfers any material recovered from a
436
spill or leak to a container that meets the requirements of 40 CFR
262.34, and has available equipment necessary to comply with this
requirement;
D)
The handler ensures that the area in which the lamps are crushed
is well-ventilated and monitored to ensure compliance with
applicable OSHA exposure levels for mercury;
E)
The handler ensures that employees crushing lamps are
thoroughly familiar with proper waste mercury handling and
emergency procedures, including transfer of mercury from
containment devices to appropriate containers; and
F)
The crushed lamps are stored in closed, non-leaking containers
that are in good condition (e.g., no severe rusting, apparent
structural defects or deterioration), suitable to prevent releases
during storage, handling and transportation.
BOARD NOTE: Subsection (d) of this Section was added pursuant to Section
22.23a of the Act [415 ILCS 5/22.23a] (see P.A. 90-502, effective August 19,
1997).
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
Section 733.134
Labeling and Marking
A large quantity handler of universal waste shall label or mark the universal waste to identify
the type of universal waste as follows:
a)
Universal waste batteries (i.e., each battery), or a container or tank in which the
batteries are contained, must be labeled or marked clearly with any one of the
following phrases: “Universal Waste-Battery(ies)Batteries”; or “Waste
Battery(ies)Batteries”; or “Used Battery(ies)Batteries”;
b)
A container (or multiple container package unit), tank, transport vehicle or vessel
in which recalled universal waste pesticides as described in Section 733.103(a)(1)
are contained must be labeled or marked clearly as follows:
1)
The label that was on or accompanied the product as sold or distributed;
and
2)
The words “Universal Waste-Pesticide(s)Pesticides” or “Waste-
Pesticide(s)Pesticides”;
c)
A container, tank, or transport vehicle or vessel in which unused pesticide
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products, as described in Section 733.103(a)(2), are contained must be labeled or
marked clearly as follows:
1)
Pesticide labeling:
A)
The label that was on the product when purchased, if still legible;
B)
If using the labels described in subsection (c)(1)(A) above of this
Section is not feasible, the appropriate label as required under the
USDOT regulation 49 CFR 172; or
C)
If using the labels described in subsections (c)(1)(A) and (c)(1)(B)
above of this Section is not feasible, another label prescribed or
designated by the pesticide collection program; and
2)
The words “Universal Waste-Pesticide(s)Pesticides” or “Waste-
Pesticide(s)Pesticides”;
d)
Universal waste thermostats (i.e., each thermostat) or a container or tank in
which the thermostats are contained must be labeled or marked clearly with any
one of the following phrases: “Universal Waste-Mercury Thermostat(s)
Thermostats”, or “Waste Mercury Thermostat(s) Thermostats”, or “Used
Mercury Thermostat(s) Thermostats”; and
e)
Universal waste mercury-containing lamps Each lamp or a container or package
in which the such lamps are contained shall must be labeled or clearly marked
with any one of the following phrases: “Universal Waste-Mercury-Containing
Lamp(s)Lamps”, “Waste Mercury-Containing Lamp(s)Lamps” or “Used
Mercury-Containing Lamp(s)Lamps”.
BOARD NOTE: Subsection (e) of this Section was added pursuant to Section
22.23a of the Act [415 ILCS 5/22.23a] (see P.A. 90-502, effective August 19,
1997).
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
SUBPART D: STANDARDS FOR UNIVERSAL WASTE
TRANSPORTERS
Section 733.150
Applicability
This Subpart applies to universal waste transporters (as defined in Section 733.106 733.109).
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
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SUBPART E: STANDARDS FOR DESTINATION FACILITIES
Section 733.160
Applicability
a)
The owner or operator of a destination facility (as defined in Section 733.106
733.109) is subject to all applicable requirements of 35 Ill. Adm. Code 702
through 705, 720 724 through 726, and 728, and the notification requirement
under section 3010 of RCRA.
b)
The owner or operator of a destination facility that recycles a particular universal
waste without storing that universal waste before it is recycled shall comply with
35 Ill. Adm. Code 721.106(c)(2).
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
SUBPART G: PETITIONS TO INCLUDE OTHER WASTES
Section 733.181
Factors for Petitions to Include Other Wastes
a)
Hazardous waste listing or characteristics. The waste or category of waste, as
generated by a wide variety of generators, is listed in 35 Ill. Adm. Code
721.Subpart D, or (if not listed) a proportion of the waste stream exhibits one or
more characteristics of hazardous waste identified in 35 Ill. Adm. Code
721.Subpart C. (When a characteristic waste is added to the universal waste
regulations of this Part by using a generic name to identify the waste category
(e.g., batteries), the definition of universal waste in 35 Ill. Adm. Code 720.110
and Section 733.106 733.109 will be amended to include only the hazardous
waste portion of the waste category (e.g., hazardous waste batteries).) Thus,
only the portion of the waste stream that does exhibit one or more characteristics
(i.e., is hazardous waste) is subject to the universal waste regulations of this Part;
b)
Generation by a wide variety of types of facilities. The waste or category of
waste is not exclusive to a specific industry or group of industries, is commonly
generated by a wide variety of types of establishments (including, for example,
households, retail and commercial businesses, office complexes, conditionally
exempt small quantity generators, small businesses, or government organizations,
as well as large industrial facilities);
c)
Generation by a large number of generators. The waste or category of waste is
generated by a large number of generators (e.g., more than 1,000 nationally) and
is frequently generated in relatively small quantities by each generator;
d)
Collection systems to ensure close stewardship. Systems to be used for
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collecting the waste or category of waste (including packaging, marking, and
labeling practices) would ensure close stewardship of the waste;
e)
Waste management standards and risk to human health and the environment.
The risk posed by the waste or category of waste during accumulation and
transport is relatively low compared to other hazardous wastes, and specific
management standards proposed or referenced by the petitioner (e.g., waste
management requirements appropriate to be added to Sections 733.113, 733.133,
and 733.152; or applicable USDOT requirements) would be protective of human
health and the environment during accumulation and transport;
f)
Increased likelihood of diversion of waste from non-hazardous waste
management systems. Regulation of the waste or category of waste under this
Part will increase the likelihood that the waste will be diverted from non-
hazardous waste management systems (e.g., the municipal waste stream, non-
hazardous industrial or commercial waste stream, municipal sewer or stormwater
systems) to recycling, treatment, or disposal in compliance with Subtitle C of
RCRA;
g)
Improved implementation of the hazardous waste program. Regulation of the
waste or category of waste under this Part will improve implementation of and
compliance with the hazardous waste regulatory program; or
h)
Such other factors as may be appropriate.
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
