ILLINOIS POLLUTION CONTROL BOARD
June 20, 1996
IN THE MATTER OF:
)
)
R95-20
RCRA UPDATE, USEPA REGULATIONS
)
(Identical in Substance Rules-
(1-1-95 THROUGH 6-30-95, 7-7-95,
)
RCRA Subtitle C)
9-29-95, 11-13-95 & 6-6-96)
)
Adopted Rule.
Final Order.
OPINION OF THE BOARD (by E. Dunham):
Pursuant to Section 13(c) and 22.4(a) of the Environmental Protection Act (Act) [415
ILCS 5/13(c) & 22.4(a) (1994)], the Board adopts amendments to the RCRA Subtitle C
hazardous waste (RCRA) regulations.
Section 22.4(a) provides for quick adoption of regulations that are "identical in
substance" to federal regulations adopted by U.S. Environmental Protection Agency (USEPA)
to implement Sections 3001 through 3005 of the Resource Conservation and Recovery Act of
1976 (RCRA, 42 U.S.C. §§ 6921-6925) and that Title VII of the Act and Section 5 of the
Administrative Procedure Act (APA) [5 ILCS 100/5-35 & 5-40 (1994)] shall not apply.
Section 13(c) similarly provides with respect to underground injection control regulations
adopted by USEPA pursuant to Section 1421 of the Safe Drinking Water Act (SDWA; 42
U.S.C. § 300h). Because this rulemaking is not subject to Section 5 of the APA, it is not
subject to first notice or to second notice review by the Joint Committee on Administrative
Rules (JCAR). The federal RCRA Subtitle C regulations are found at 40 CFR 260 through
268, 270 through 271, and, more recently, 279.
This opinion supports an order adopted on the same day. The Board will delay filing
the adopted amendments with the Office of the Secretary of State for 30 days to allow time for
USEPA to review them prior to filing. The amendments will become effective upon filing,
and Notices of Adopted Amendments (or Rules, as appropriate) will appear in the Illinois
Register.
FEDERAL ACTIONS CONSIDERED IN THIS RULEMAKING
This rulemaking updates the Illinois RCRA Subtitle C rules to correspond with federal
amendments made in the period from January 1 through June 30, 1995. The USEPA actions
during this period are as follows:
Federal Action
Summary
Jan. 3, 1995,
Technical Corrections to Phase II LDRs
2
60 Fed. Reg. 242
Jan. 13, 1995,
60 Fed. Reg. 3089
Update to testing and monitoring methods
Feb. 3, 1995,
60 Fed. Reg. 6666
Response to City of Chicago v. Environmental Defense
Fund decision
Feb. 7, 1995,
60 Fed. Reg. 7366
Determination that additional regulation is necessary for
cement kiln dust
Feb. 9, 1995,
60 Fed. Reg. 7824
New hazardous waste listings for six carbamate
production wastes; addition of 58 commercial chemical
product wastes; exemption of certain biological treatment
sludges
Apr. 4, 1995,
60 Fed. Reg. 17001
Update to testing and monitoring methods
Apr. 4, 1995,
60 Fed. Reg. 17160
Update to CWA analytical methods
Apr. 17, 1995,
60 Fed. Reg. 19165
Corrections to carbamate waste listings
May 11, 1995,
60 Fed. Reg. 25492
Universal Waste Rule
May 12, 1995,
60 Fed. Reg. 25619
Correction to carbamate waste listings
May 19, 1995,
60 Fed. Reg. 26828
Postponement of effective date for tank, container, and
surface impoundment air emissions rules
June 13, 1995,
60 Fed. Reg. 31114
Delisting of hazardous waste generated in Illinois by a
Pennsylvania company
June 29, 1995,
60 Fed. Reg. 33912
Deletion of obsolete, redundant, and outdated RCRA rules
Deviations from Routine Docket Time-Frame for Federal Amendments
3
In addition to these principal amendments that occurred during the normal docket
update period, the Board has included four additional, later actions that are corrections or
relaxations of prior amendments in the preceding RCRA Subtitle C update docket, R95-4/R95-
6:
July 7, 1995,
60 Fed. Reg. 35452
Correction to the Subpart CC organic material emissions
standards for tanks, containers and surface impoundments
September 29, 1995,
60 Fed. Reg. 50426
Stay of Subpart CC rules as they apply to tanks,
containers, and surface impoundments that contain wastes
generated in the manufacture of organic peroxides
November 13, 1995,
60 Fed. Reg. 56952
Stay of Subpart CC rules in their entirety until June 6,
1996
June 5, 1996,
61 Fed. Reg. 28508
Stay of Subpart CC rules in their entirety until October 6,
1996
Further, the Board used this opportunity to include a number of corrective amendments
to the existing regulations. These corrections are more fully described below. They are
derived from comments by the Joint Committee on Administrative Rules (JCAR) and the
Illinois EPA (Agency).
Finally, the Board omitted from consideration two set of federal amendments that
occurred during the time-frame of this docket. First, on
January 3, 1995
, USEPA corrected
errors and clarified language in the universal treatment standards adopted on September 19,
1994 as the Phase II LDRs. The Board did not include those amendments in this docket
because we dealt with them in docket R95-4/R95-6, when adopting the Phase II rules.
Second, on
May 19, 1995
, USEPA stayed of the 40 CFR 264, subpart CC and 265, subpart
CC (Subpart CC) regulations governing organic material emissions from tanks, containers, and
surface impoundments. USEPA delayed the effective date by six months, until December 6,
1995. This delay was similarly included with the R95-4/R95-6 amendments, so there was no
need for Board to take action at this time. Further, the subsequent federal stay granted on
November 13, 1995 and extended on June 5, 1996 made that initial stay of May 19 obsolete.
Brief Summaries of the Federal Actions Considered in this Docket
By way of brief elaboration, the Board will summarily describe the federal actions that
occurred in the time-frame of this docket and our action on each matter.
The federal amendments of
January 13, 1995
added Update II to the third edition of
"Test Methods for Evaluating Solid Waste, Physical/Chemical Methods", SW-846, by
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updating the incorporations by reference. The Board included corresponding amendments in
this docket.
On
February 3, 1995
, USEPA responded to public inquiries in the wake of the
Supreme Court's decision in City of Chicago v. Environmental Defense Fund, Inc., 114 S. Ct.
1588 (1994). USEPA resolved an issue by interpreting that municipal solid waste incinerator
ash could become a hazardous waste when it leaves the combustion building after the
combustion and air pollution control processes. At this point, the facility owner or operator
must make the determination whether the ash is hazarous waste. This avoids designating the
combustion building as a hazardous waste management facility. Although there were no
regulatory amendments accompanying the interpretation, the Board has already noted the City
of Chicago decision in a Board Note in our rules, so we amend the Note to include the recent
federal interpretation.
On
February 7, 1995
, USEPA announced that it had studied cement kiln dust and
determined that some further regulation of this material (which is RCRA Subtitle C-exempt) is
desirable. However, USEPA noted that the costs of complete Subtitle C compliance would
likely be prohibitive. USEPA stated that it plans to establish a special subset of regulations for
this material at some future time. Since there are no regulatory amendments at this time, and
since the federal determination does not yet carry any substantive effect, the Board does not
need to react to this determination by amendment of the Illinois rules. This opinion will not
further discuss this federal action.
By the amendments of
February 9, 1995
, USEPA established hazardous waste listings
(K156 through K161) for six carbamate production wastes. It added 58 new chemicals to the
list of commercial chemical products that become hazardous waste when discarded. USEPA
also exempted biological treatment sludges from hazardous waste regulation, so long as the
treated sludges do not exhibit a hazardous characteristic. On
April 17, 1995
and again on
May 12, 1995
, USEPA corrected the earlier carbamate amendments. The present docket
includes amendments to the Illinois RCRA Subtitle C rules in response to these federal actions.
There were two sets of ostensibly unrelated amendments on
April 4, 1995
which will
have a related impact on the Illinois regulations. First, USEPA amended its methods for
testing hazardous waste to clarify the temperature for pH measurements and add an additional
analytical method. The Board will have to incorporate these amendments into the Illinois
rules. Second, USEPA amended its guideline for testing under the Clean Water Act (40 CFR
136) to add clarifying notes and update analytical methods. Although this action does not
directly affect the RCRA Subtitle C program, the Illinois RCRA/UIC regulations incorporate
federal part 136 by reference at Section 720.111. Both sets of amendments have required the
Board to update the incorporations by reference provisions to reflect the latest federal versions
of the methods.
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A major set of federal regulations arose on
May 11, 1995
, when USEPA established a
new body of regulations to govern certain high-volume hazardous wastes that are being
collected for recycling or disposal. Although USEPA plans to add wastes in the future
(notably, fluorescent light bulbs), these streamlined rules (not unlike the used oil regulations)
apply to batteries, pesticides, and thermostats at this time. This is the single most significant
set of amendments within the update period, and the Board has received a request for
expedited consideration of these amendments. The Board is establishing a new Part 733 in this
proceeding to correspond with new federal 40 CFR 273.
By the amendments of
June 13, 1995
, USEPA delisted the treated residues of certain
listed hazardous waste generated by Conversion Systems, Inc. (CSI) in Sterling, Illinois. As is
explained below, CSI submitted a request that has prompted the Board to include
corresponding amendments in this docket.
On
June 29, 1995
, USEPA deleted a vast number of rules that were obsolete,
redundant, or outdated. USEPA amended three provisions in 40 CFR 261 and 266 of the
RCRA Subtitle C (hazardous waste) rules as part of this effort. The Board has included
amendments in this docket to correspond with this federal action.
Finally, USEPA undertook three actions relating to the 40 CFR 264, subpart CC and
265, subpart CC regulations (Subpart CC rules) governing organic material emissions from
tanks, containers, and surface impoundments. One action, on
July 7, 1995
, made corrections
to the Subpart CC rules. Since both corrections relate to the Federal Register preamble
discussion and not to the text of the regulations themselves, no amendments were necessary
based on that action. On the other hand, Board action is required by two other actions relating
to the Subpart CC rules that are outside the routine time-frame of this docket. Although both
actions are within the nominal time-frame of the next RCRA Subtitle C update docket, R96-
10, which covers the period of July 1 through December 31, 1995, the Board has decided to
take action at this time and include both stays in this docket. Both are partial stays of the
Subpart CC rules. First, on
September 29, 1995
, USEPA indefinitely stayed the Subpart CC
regulations as they would apply to tanks, surface impoundments, and containers containing
hazardous waste generated by an organic peroxide manufacturing process. Second, on
November 13, 1995
and again on
June 5, 1996
, USEPA further delayed the effective date of
the Subpart CC rules by another six months, until October 6, 1996. Each stay required
amendment of the base hazardous waste regulations.
PUBLIC COMMENTS
The Board adopted a proposal for public comment in this matter on February 1, 1996.
Notices of Proposed Amendments appeared in the Illinois Register on February 16, 1996, at
20 Ill. Reg. 2651 (Part 720), 2685 (Part 721), 2791 (Part 725), 2813 (Part 728), 2924 (Part
702), 2940 (Part 703), 2951 (Part 722), 2960 (Part 724), and 2980 (Part 726). A Notice or
6
Proposed Rules also appeared in that issue at 20 Ill. Reg. 3008 (Part 733). The Board
received public comment on the proposal for a period of 45 days following the date of its
publication in the Illinois Register. The Board will delay filing any adopted rules with the
Secretary of State for 30 days after adoption, particularly to allow USEPA review. The
complete text of the proposed amendments appears in a separate order adopted this day.
As of the time of proposing these amendments for public comment, the Board had
already received five public comments on the rules:
PC 1
Vicki Thomas, Executive Director, Joint Committee on Administrative Rules
(letter and attachments docketed August 22, 1995)
PC 2
Vicki Thomas, Executive Director, Joint Committee on Administrative Rules
(JCAR; text of 35 Ill. Adm. Code 728.Table T, as adopted in R95-4/R95-6,
with corrections marked docketed August 25, 1995)
PC 3
Ron Klint, TDI Batteries (letter docketed October 13, 1995)
PC 4
Jeffrey C. Moore, General Counsel, Conversion Systems, Inc. (CSI; letter
docketed November 6, 1995)
PC 5
Mark Homer, Regulatory Affairs Counsel, Chemical Industry Council of
Illinois (CICI; letter docketed November 29, 1995)
After adoption of the February 1, 1996 proposal for public comment, the Board
received 14 additional public comments:
PC 6
William R. Uffelman, Divisional Vice-President, Government Affairs, Midwest
Region, Browning-Ferris Industries (BFI; letter docketed March 5, 1996)
PC 7
Robert G. Hilton, Vice President-Sales & Marketing, Specialized Services,
EnviroSource Treatment and Disposal Services, Inc. (CSI's parent company;
letter docketed March 29, 1996)
PC 8
Paul E. Guterman, John N. Moore, and Akin, Gump, Strauss, et al., Counsel
for Horsehead Resource Development Co. (HRD; comments docketed April 2,
1996)
PC 9
Kim Kelly, President, Rechargeable Battery Recycling Corp. (RBRC; comments
and attachments docketed April 4, 1996)
PC 10
C. Norman Englund, President & CEO, Portable Rechargeable Battery Assoc.
(PRBA; comments docketed April 4, 1996)
7
PC 11
Judy Dyer, Assistant Counsel, Division of Legal Counsel, Illinois EPA
(Agency; comments docketed April 4, 1996)
PC 12
Charles Dickhut, Chairman, Association of Waste Hazardous Materials
Transporters (AWHMT; letter docketed March 28, 1996)
PC 13
Bill S. Forcade and Jenner & Block, Counsel for CSI (letter docketed April 26,
1996)
PC 14
Dan A. Rosenbaum and Jenner & Block, Counsel for CSI (letter and copy of
final federal action on CSI delisting docketed April 26, 1996)
PC 15
David E. Long, Environmental Manager, Northwestern Steel and Wire Co.
(letter docketed April 30, 1996)
PC 16
Richard T. Traub, Chief, State Programs and Authorization Section, USEPA
Region V (letter and comments docketed May 13, 1996)
PC 17
Paul E. Guterman, John N. Moore, and Akin, Gump, Strauss, et al., Counsel
for HRD (comments docketed May 15, 1996)
PC 18
William M. Guerry and Collier, Shannon, Rill & Scott, Counsel for the Steel
Manufacturers Association (SMA; letter and attachments docketed May 16,
1996)
PC 19
Paul E. Guterman, John N. Moore, and Akin, Gump, Strauss, et al., Counsel
for HRD (letter and attached comments docketed June 4, 1996)
By PC 1 and PC 2, JCAR indicates a number of minor corrections to the base text of
the Illinois RCRA Subtitle C regulations and as last amended in R95-4/R95-6. The Board has
examined those corrections and acted on them where necessary, which is discussed below.
In PC 3, a member of the regulated community has requested expedited consideration
of the universal waste rules, adopted by USEPA on May 19, 1995. The letter outlines the
environmental and economic benefits of prompt adoption of what amounts to a relaxation of
the hazardous waste regulations. The Board granted expedited consideration of these
amendments by an order dated October 19, 1995. The universal waste rules are a major
segment of the present action.
By PC 4, a regulated entity requests that the Board adopt a federal hazardous waste
delisting (of June 13, 1995) by identical-in-substance rulemaking. Although we possess the
statutory authority to adopt such site-specific federal regulations using the identical-in-
substance procedure, the Board does not unilaterally propose and adopt such rules in the
8
absence of a request that we act to adopt the rule. The Board has included the delisting with
the present amendments in response to the request.
In PC 5, an industry trade association requested expedited consideration of the federal
stay (dated November 13, 1995) of major provisions of existing rules adopted in docket R95-
4/R95-6. USEPA adopted the stay outside the nominal time-frame of this docket. The Board
granted expedited consideration of the stay by an order dated December 7, 1995. As discussed
above, this stay and another are both dealt with in the present action. (See infra, pp. 16-19.)
In PC 6, BFI expressed support for adoption of the federal universal waste rule.
However, BFI requested clarification of the procedural and informational requirements for
adding additional universal waste. The Board discusses the BFI request for clarification
below. (See infra, pp. 28-31.)
In PC 7, EnviroSource submitted comments from CSI supporting the Board's adoption
of the federally-granted CSI hazardous waste delisting as soon as possible. EnviroSource
stated that the adoption would allow the management of the subject waste outside the RCRA
Subtitle C regulatory system and allow reduced operating costs. EnviroSource also stated that
the adoption would allow CSI to petition the Board for further identical-in-substance action if
USEPA changes the scope of the delisting. EnviroSource is the parent company of CSI.
EnviroSource stated that it had reviewed the proposed delisting and concluded that the
proposed language correctly reflects USEPA's intent in granting the delisting. It urges
adoption of the delisting without revision of the language as proposed.
In PC 8, HRD urged the Board not to adopt the proposed delisting for the CSI waste.
HRD set forth a number of arguments against the delisting based in state and federal law and
on resource conservation. CSI responded to the HRD comments by PC 13 and PC 14. HRD
replied by PC 17 and requested oral argument before the Board. By PC 18, SMA responded
to HRD's PC 8, supporting the CSI delisting and urging the Board to adopt it. HRD
responded to SMA's comments by PC 19. The Board discusses HRD's and SMA's relative
positions and their arguments and the SMA comments below. (See infra, pp. 19-21.) In PC
15, Northwestern Steel and Wire expressed support of the Board adopting the proposed CSI
hazardous waste delisting. It stated that it supports the comments submitted in PC 13. The
Northwestern Steel plant at Sterling has used the CSI Super Detox process since 1989 to
stabilize its waste for disposal, and it is this waste that is the subject of the delisting.
Northwestern Steel wants to reduce the costs associated with disposal of this stabilized waste
by managing it outside the scope RCRA Subtitle C regulations, which the delisting would
allow.
By PC 9, RBRC commented in support of the adoption of the Universal Waste Rule.
PRBA commented similarly in PC 10. RBRC explained that it administers the collection and
recycling of rechargeable batteries. PRBA is an industry association of nickel-cadmium
battery manufacturers. RBRC and PRBA stated that the present RCRA Subtitle C regulations,
currently imposed on the recycling activities, create a substantial compliance burden which
9
acts as a disincentive to the recycling. They stated that on September 18, 1995 the Illinois
EPA issued a letter indicating that it has adopted a temporary policy as to recycled batteries
forebearing enforcement of the hazardous waste regulations in light of the federal Universal
Waste Rule and the prospective Board adoption of that rule, thus allowing initial development
of recycling programs in Illinois. RBRC and PRBA urged prompt adoption of the Rule to
allow full, formal implementation of the programs in this state.
In PC 11, the Agency offered a number of comments on the text of the proposed
amendments. The Agency suggested a small number of revisions and clarifications to the text.
The Board discusses the details of those comments in the appropriate segments of this opinion,
below. (See infra, pp. 31-33 & 48-52.)
In PC 12, AWHMT explained that it is an industry association of companies that
transport waste hazardous materials by truck and rail. AWHMT raised a number of concerns
over the interstate implementation of the Universal Waste Rule and requested Board
clarification of some of these issues. The Board addresses the details of the AWHMT
comments below. (See infra, pp. 28-31.)
By PC 16, USEPA submits its comments on the proposed amendments. USEPA
submitted a small number of corrective amendments to the text. These corrections are outlined
in the appropriate segments of the following discussions.
In addition to the several comments received, the Board received a motion for oral
argument on May 28, 1996 from HRD. We received a response in opposition to oral
argument on May 29, 1996 from CSI. The Board concluded that it was fully advised on the
issues involved in the CSI delisting through the various public comments received and denied
the motion by an order dated June 6, 1996.
EXPEDITED CONSIDERATION AND REASON FOR DELAY
Prior to commencing work on the present amendments, the Board received requests to
expedite this docket. As described above, the Board granted expedited consideration by orders
dated October 19 and December 7, 1995. The October 19, 1995 order also set forth reasons
for delay in this docket--i.e., "present and recent-past demands on Board resources and
personnel, including those associated with completing the prior update, R95-4/R95-6". The
Board again set forth reasons for delay in the proposed opinion of February 1, 1996.
Although the proposal of these amendments is later than was originally anticipated on October
19, this proposal for public comment represents a significant effort on the part of the Board to
act as promptly as possible, given the magnitude of the amendments included in this docket
and competing priorities for the Board and its staff. Having now completed all the necessary
work to complete this rulemaking occurs as rapidly as possible and having now voted to adopt
10
the amendments, the Board presently anticipates filing the adopted amendments with the
Secretary of State 30 days later.
The Board will cause a copy of the above segment of this proposed opinion to be
published in the Illinois Register, as required by Section 7.2(b) of the Act.
HISTORY OF RCRA SUBTITLE C, UST and UIC ADOPTION
AGENCY OR BOARD ACTION?
EDITORIAL CONVENTIONS
The Board appends three routine discussions at the end of this opinion. The first is a
summary history of the Illinois RCRA Subtitle C and UIC programs. It lists all actions taken
to adopt and maintain these programs since their inceptions. It includes a listing of all site-
specific rulemaking and adjusted standards proceedings filed that relate to these programs. It
also lists all USEPA program authorizations issued to date. The second is a discussion of how
the Board codifies requirements that call for state determinations, such as for exemptions,
exceptions, etc. The third discussion relates to our use of language in the codification of
identical-in-substance rules. We intend these as reference aids for interested persons in the
regulated community.
DISCUSSION
The federal actions that underlie this proceeding require amendment of the Illinois
RCRA Subtitle C regulations. This discussion briefly focuses on each by subject matter,
indicating the specific details of the actions taken by the Board where pertinent.
General Revisions
The Board has engaged in an ongoing effort to change its method of referring to the
United States Environmental Protection Agency in the hazardous waste and other regulations
through the course of the last several update proceedings, R93-16, R94-7, R94-17, and R95-
4/R95-6. Subsequent to the final opinion and order in the next preceding update, R95-4/R95-6
dated June 1, 1995, JCAR requested that the Board adopt the same usage throughout all of our
bodies of regulations--i.e., air, water, drinking water, RCRA Subtitle D (municipal solid
waste landfill), RCRA Subtitle C (hazardous waste), underground injection control (UIC), etc.
The Board included the Agency in our discussion of whether "USEPA" or "U.S. EPA" would
become the chosen form. The Agency's Bureau of Air pressed for unity in favor of the
"USEPA" usage. For this reason, the Board begins the process of reversing the prior unifying
amendments in the provisions that are open in this docket. We will now refer to "USEPA".
11
We will continue this conversion in future rulemakings as additional Sections otherwise
become open to amendment.
The Board substituted "or" for "/" in most instances where this appeared in the federal
base text, using "and" where more appropriate. The Board further used this opportunity to
make a number of corrections to punctuation, grammar, and cross-reference format throughout
the opened text. We also changed "who" to "that" and "he" to "it", where the person to which
the regulation referred was not necessarily a natural person, or to "he or she", where a natural
person was evident; changed "which" to "that" for restrictive relative clauses; substituted
"shall" for "will"; capitalized the Section headings and corrected their format where necessary;
and corrected punctuation within sentences.
Finally, some of the language structure of the federal base text (in the new
amendments) is cumbersome or less than clear. The Board has attempted to correct some of
the worst instances of this. We realize that the language of the hazardous waste regulations
would still be clearer and more concise, but the Board cannot go further at this time and still
maintain parity with the federal regulations. However, we invite interested members of the
regulated community to submit suggestions relating to correcting deficiencies and errors and
enhancing clarity of the rules at any time, for possible inclusion in some future update docket.
For the sake of brevity, the following table sets forth the miscellaneous corrections to
the pre-amended base text of the rules for persons needing to make the comparison in detail.
Corrections made to the amendments incorporated in this docket are set forth in the topical
discussions that follow.
Corrections to Base Pre-Amended Text*
Section
Correction
702.110 "corrective action management
unit", "date of approval . . ." & "Environ-
mental Protection Agency"
Switched to "USEPA"
703.123(e), (f) & (g)
Changed subsection numbering
703.151 & 703.152
Reformated Board Notes
720.110
Switched to "USEPA" in "corrective action
management unit", "designated facility",
"EPA hazardous waste number", "EPA
identification number", "manifest document
number" & "replacement unit"; move
definitions of "USEPA", "representative
sample" & "uppermost aquifer"; added
12
definition of "USDOT"
720.111
Switched to "USEPA" under "APTI",
"GPO" & "USEPA"; corrected end-of-
quote punctuation of reference to SW-846
720.120(a)
Changed to "that"
720.103(a)(2)(D)
Removed "or" from subsections (i) through
(iv); repunctuate (v) (JCAR requests); used
possessive "wastes'"
720.103(b)(1)(B) & (b)(11)
Switched to "USEPA"
721.103(e)(2)(C)
Deleted decimal from zinc entries (JCAR
request); switched to "USEPA"; corrected
subsection label format
721.103(f)(2), (f)(7)(A), (f)(7)(G),
(f)(9)(A) & (f)(9)(C)
Switched to "USEPA"
721.105(f)(3)
Added "fulfills any of . . ." to preamble &
"the facility is" to subsections; add
reference to 40 CFR 271
721.105(f)(3)(C)
Switched to "USEPA"
721.105(g)(3)
Added "fulfills any of . . ." to preamble;
"the facility is" to subsections & added
reference to 40 CFR 271
721.105(g)(3)(C)
Switched to "USEPA"
721.105(g)(3)(E)
Used "that"
721.106(a)(3)
Switched to "USEPA"
721.130(b)(2)
Corrected "a" (JCAR request)
721.131(a) F023
Added closing parentheses (JCAR request)
721.132 K001
Changed to "or"
721.132 K066
Corrected punctuation of quotation
13
721.132 K149
Changed location of end punctuation
(JCAR request)
721.App. H warfarin, warfarin salts, zinc
phosphide & ziram
Removed end punctuation
721.App. H
Added "note:"
721.App. I, Table B
Switched to "USEPA"
721.App. Z
Corrected first-row entries' parentheticals
(prompted by JCAR request); added cross-
references to column heading footnotes;
added Board Note indicating source
722.111(d)
Added comma
724.101(f)
Switched to "USEPA"
724.101(g)(7) through (g)(10)
Added cross-reference to reserved federal
provision & renumbered subsections to
correspond with federal counterparts
724.980(a)
Switched to "USEPA"
725.980(a)
Switched to "USEPA"
726.180(a)
Used singular; changed to "that" in place of
"who"; used "the batteries" in place of
"them"
726.203(a)(1)(B), (a)(3), (b)(2),
(c)(2)(A)(i), (c)(4)(A)(i) & (c)(8)(B)(i) &
726.204(a)(3)
Switched to "USEPA"
728.101(e)(3)
Switched to "USEPA"
728.Table T D033
Corrected CAS number (JCAR requested)
728.Table T F028
Switched to "USEPA"
728.Table T F037
Corrected wastewaters entry for xylenes
(JCAR requested)
14
728.Table T F039
Switched to "USEPA"
728.Table T F039
Corrected CAS number for bis(2-chloro-
isopropyl)ether (JCAR requested)
728.Table T K019
Corrected CAS number for bis(2-chloro-
isopropyl)ether (JCAR requested)
728.Table T K051
Corrected CAS number for toluene (JCAR
requested)
728.Table T P024
Corrected wastewaters entry (JCAR
requested)
728.Table T U027
Corrected CAS number for bis(2-chloro-
isopropyl)ether (JCAR requested)
728.Table T end note 7
Switched to "USEPA"
728.Table U Diphenylnitrosoamine
Added space (JCAR requested)
728.Table U end note 4
Switched to "USEPA"
* Additional corrections appear in the discussion of revisions to the text of the proposed rules
based on public comments, beginning below on page 48.
Updated Analytical Methods--Section 720.111
USEPA amended 40 CFR 260.11(a) on January 13, 1995, at 60 Fed. Reg. 3089, and
on April 4, 1995, at 60 Fed. Reg. 17001. Section 720.111 of the Illinois hazardous waste
regulations corresponds with 40 CFR 260.11. Both sets of amendments related to updating the
reference, "Test Methods for Evaluating Solid Waste, Physical/Chemical Methods" (SW-846).
Both sets of amendments added methods to SW-846. The January 13 amendments added
Updates I, II, and IIA to the third edition in the reference to this document. Those
amendments also revised the references to the updates to indicate that they are now available
through the Government Printing Office, which means the deletion of the references to MICE
and USEPA-OSW as sources of these documents. The April 4 federal amendments added
Update IIB to the reference. In reviewing the January 13, 1995 Federal Register discussion of
the methods included in the updates, the Board observed that Method 8290 is included in
Update II. We therefore deleted the reference to USEPA as the source for this method.
15
Although not directly related to the hazardous waste regulations, USEPA also amended
the Clean Water Act programs analytical procedures of 40 CFR 136 on April 4, 1995, at 60
Fed. Reg. 17160. USEPA added clarifying footnotes; updated the methods in Tables IA, IB,
IC, and ID; and corrected typographic errors in the text. The Board has incorporated 40 CFR
136 by reference in Section 720.111(b).
The Board has incorporated the three sets of federal amendments into Section 720.111.
We updated the reference to SW-846 to indicate the new updates and revised availability of
those updates. The Board also updated the incorporation of 40 CFR 136 by adding the April 4
Federal Register citation. The Board invited public comment on the updated incorporations in
Section 720.111 and received no comments.
Hazardous Waste Determinations--Sections 721.103, 721.104, 721.132, 721.133 &
721.Appendices G through I
USEPA undertook three basic actions relating to identification of hazardous waste to
which the Board responds in this docket. First, USEPA published its interpretation of the
point at which municipal incinerator ash initially becomes subject to regulation as hazardous
waste in light of a recent Supreme Court decision. Second, USEPA adopted and corrected
regulations adding a number of hazardous waste listings and hazardous constituents listings.
These primarily involve wastes generated in carbamate manufacturing processes. Finally,
USEPA granted a hazardous waste delisting to a company for a waste generated in Illinois.
USEPA announced its interpretation of when municipal incinerator ash becomes subject
to hazardous waste regulation on February 3, 1995. It took this action as a result of the
Supreme Court's decision in City of Chicago v. Environmental Defense Fund, -- U.S. --, 114
S. Ct. 1588 (1994). Prior to that decision, USEPA had interpreted the exclusions of 40 CFR
261.4(b)(1)(ii) (corresponding with and Section 3001(i) of RCRA as excluding the combustion
of municipal waste from hazardous waste regulation. (See 50 Fed. Reg. 28702, July 15,
1985.) At various times, USEPA took the position that the resulting ash itself was exempted.
(See 59 Fed. Reg. 29372, June 7, 1994.) In City of Chicago, the Court determined that the
resulting ash was subject to RCRA Subtitle C regulation if it exhibited a characteristic of
hazardous waste. On February 3, 1995, USEPA stated that the Court's opinion left open the
issue of the point at which the ash would become subject to Subtitle C regulation. USEPA
interpreted that this point was when the ash actually leaves the combustion building for
disposal. Prior to that point, USEPA does not consider the ash subject to regulation as
hazardous waste.
In response to the federal action of June 7, 1994, relating to facility permitting, the
Board added a Board Note to Section 721.104(b)(1)(B) indicating the Supreme Court decision
and USEPA's June 7, 1994 action in response. The Board has added language to this Note
16
indicating the newer February 3 action by USEPA in further response to the Supreme Court's
decision.
USEPA added six wastes generated in the manufacture of carbamates (i.e., "carbamate
wastes") to the lists of hazardous wastes 40 CFR 261 Subpart D ("Subpart D wastes") on
February 9, 1995, at 60 Fed. Reg. 7824. USEPA further added 58 specific chemical
substances to the list of commercial chemical products that are hazardous waste when
discarded. This action entailed amendments to 40 CFR 261.3(a)(2)(iv)(F), (a)(2)(iv)(G), and
(c)(2)(ii)(D) (all added); 261.32; 261.33(e) and (f); and 261, Appendices VII and VIII, which
correspond with 35 Ill. Adm. Code 721.103(a)(2)(D)(vi), (a)(2)(D)(vii), and (e)(2)(D);
721.132; 721.133(e) and (f); and 721.Appendices G and H. USEPA later corrected errors in
these amendments on April 17, at 60 Fed. Reg. 19165, and May 12, 1995, at 25619. The
Board has made all the amendments necessary to incorporate the federal revisions. The Board
made minor editorial changes in the federal text in a number of locations. The changes are
limited to correction of punctuation, the capitalization of an abbreviated chemical name, and
the correction of the format (i.e., spacing and hyphenation) and spelling of chemical names for
the added constituents. We have not otherwise deviated from the federal carbamate rule
revisions. A table at the end of this segment of the discussion indicates the location of the
changes.
USEPA granted Conversion Systems, Inc. (CSI) a hazardous waste delisting on June
13, 1995, at 60 Fed. Reg. 31107. The waste to which the delisting immediately applies is
proprietarily-treated electric arc furnace dust (K061) generated at CSI's Sterling, Illinois
operations. The federally-granted delisting includes a number of conditions pertaining to
waste treatment, maximum leachable contaminant concentrations, testing, recordkeeping, and
reporting. The delisting includes conditions relating to future expansion to other locations
upon written amendment by USEPA.
The Board has incorporated the CSI delisting into Section 721.Appendix I, Table B,
relating to delisted wastes from specific sources with a limited number of revisions to the
language for the sake of clarity and to make it fit within Illinois administrative and statutory
requirements. We list the revisions and our reasons in the following table:
Deviations from the Federal Text of the CSI Delisting*
Deviation from Federal Text
Explanation
Use of full name instead of "EAFD" for
initial reference in preamble
Enhanced clarity
Added reference "municipal solid waste
landfill" to Subtitle D references in
preamble and paragraph 2.
Language convention used in Illinois
nonhazardous waste landfill (Subtitle D)
regulations
17
Offset parenthetical language of "as . . . "
clauses with commas and in the preamble
and paragraph 2.
Grammatical corrections
Changed "that" to "which" in preamble
Grammatical correction
Added incorporation language to reference
to SW-846 in paragraph 1.
Administrative Procedure Act requirement
Changed "must" to "shall" in several
locations in paragraphs 1.A., 1.C., 2., 4.,
and 5.
Board language convention for imperative
actions
Changed "composites" to "composite
samples" in paragraph 1.A.
Enhanced clarity
Changed "comprised" to "composed" in
paragraph 1.A.
Grammatical correction
Added "above" and "below" to cross-
references
Codification requirement
Added language to paragraph 1.B. outlining
options for future expansion of the delisting
Expressly clarify the options available
under Illinois law that do not exist in
federal law
Substituted "approved facility" for
"Sterling, Illinois facility and any new
facility subsequently added" in paragraph
1.C.
Clarity and economy of language
Substituted "as hazardous waste" and cross
reference to the pertinent regulations for a
reference to RCRA Subtitle C in paragraph
2.
Correct reference in Illinois regulatory
scheme
Substituted "this exclusion" for "the
exclusion" in paragraph 2
Enhanced clarity
Added "in parts per million" to paragraph
3.
Enhanced clarity
Substituted language relating to advanced
notice and approval of process changes in
paragraph 4.
Enhanced clarity
18
Changed references to notification of
USEPA to notification of the Agency
(Illinois EPA), changed a reference to
"sufficient basis to revoke" to "a violation
of the Act and Board regulations", and
altered the USEPA-specific references in
the certifications in paragraph 5.
Comports with Illinois regulatory scheme
* Additional deviations appear in the discussion of revisions to the text of the proposed rules
based on public comments, beginning below on page 48.
The Board lists its deviations from the text of the carbamate waste amendments in the
following table for the convenience of those who must make a detailed comparison of the
federal and state texts:
Deviations from the Federal Text of the Carbamate Waste Rule*
Section
Derived from
Deviation(s)
721.103(a)(2)(D)(vi)
& (vii)
261.3(a)(2)(iv)(F) &
(G)
Used colon; added commas for parentheticals
721.103(e)(2)(D)
261.3(c)(2)(ii)(D)
Used colon; deleted comma from two-
element series; used of "USEPA"
721.133(e) P189,
P191, P192, P185 &
P202
261.33(e)
Corrected format of chemical names
721.133(f) U409 &
U378
261.33(f)
Corrected format of chemical names
721.App. G K159 &
K160
261.App. VII
Corrected format of chemical abbreviated
names
721.App. H
261.App. VIII
Corrected format of chemical names in
entries for "A2213", "aldicarb sulfone",
"bendiocarb", "bendiocarb phenol", "beno-
myl", "bis(pentamethylene)thiuram",
"carbosufan", "ferbam", "formetanate
hydrochloride", "formparanate", "3-iodo-2-
propynyl-n-butyl-carbamate", "physo-
stigmine", "physostigmine salicylate",
19
"selenium, tetrakis(dimethyldithio-
carbamate)", "thiodiarb", "thiophanate-
methyl" & "tirpate"
* Additional deviations appear in the discussion of revisions to the text of the proposed rules
based on public comments, beginning below on page 48.
The Board invited comment on our amendments to the exclusions from regulation as
hazardous waste in Section 721.104 in response to the USEPA response to the City of Chicago
decision. We received no comments relating to that decision.
The Board also invited comment on our responses to the carbamate rules, to the
definition of hazardous waste in Section 721.103 the listings of Subpart D listed wastes in
Sections 721.132 and 721.133, to the listing of the bases for waste listing in Section
721.Appendix G, and to the hazardous constituents in Section 721.Appendix H. Again, we
received no comment on these matters.
Finally, the Board invited comment on our codification of the federally-granted CSI
hazardous waste delisting. In response, we received a series of public comments from three
sources. As indicated above in brief (supra, pp. 6-10), the parent company of Conversion
Systems, Inc. (CSI) submitted PC 7 in support of Board adoption of the delisting without
revision. Horsehead Resource Development Company (HRD) submitted PC 8 in opposition to
the delisting. CSI responded with PC 13 and PC 14. Northwestern Steel and Wire Co.
submitted PC 15 to support the Board adopting the CSI delisting. In PC 17, HRD replied to
CSI's PC 13, again opposing the adoption of the hazardous waste delisting. The Steel
Manufacturers Association (SMA) commented in PC 18 in favor of the Board adopting the
delisting. HRD responded to the SMA comments in PC 19.
After consideration of all the comments and the nature of our identical-in-substance
mandate, the Board has determined that it will proceed to adopt the CSI delisting. Nothing in
the arguments put forward by HRD convinces us that we should not do so.
In essence, HRD explains in PC 8 that K061, electric arc furnace dust, which is the
subject of the CSI delisting, is a high volume waste. HRD is in the business of processing this
waste by high temperature metals recovery (HTMR) to recover resources from the waste.
HRD states that granting the delisting for chemically stabilized electric arc furnace dust
(CSFEAD) would result in the disruption of the HTMR processing of the waste and that a high
volume of the delisted CSFEAD would then be disposed in nonhazardous waste landfills.
HRD asserts, without setting forth the precise statutory citations, that the disruption of the
HTMR process and resulting added burden on landfill disposal resources would violate various
Illinois and federal laws and policies. HRD challenges the Board's statutory authority to adopt
the CSI delisting using the identical-in-substance procedure. It states that this procedure would
allow the adoption without notice and comment, which it contends is without precedent. It
further asserts that using the identical-in-substance procedure subverts the federally-authorized
20
Illinois hazardous waste delisting procedure and the adjusted standard procedure, which it
contends is an abdication of the Board's responsibility to review the merits of the delisting.
HRD challenges the merits of the CSI delisting. CSI's basic position in favor of adopting the
delisting in PC 13 asserts that the Board is under a statutory mandate to adopt the federally-
granted delisting using the identical-in-substance procedure. CSI further contends that the
Board lacks the authority to review the merits of the delisting in the context of an identical-in-
substance proceeding. Northwestern Steel and Wire state in PC 15 that it supports the CSI
position put forward in PC 13. SMA explains in PC 18 that it is a national trade association
representing 60 steel industry members, including Northwestern Steel & Wire, which
generates the waste that CSI further treats to make CSFEAD. SMA strongly encourages the
Board to adopt the CSI delisting, primarily addressing the merits of the delisting. HRD
responds to the CSI comments in PC 17, essentially reasserting that the Board lacks the
authority to adopt the delisting using the identical-in-substance procedure. HRD responds to
the SMA comments in PC 19, making substantive arguments.
The Board has concluded after reviewing the comments that we have the statutory
authority to adopt the CSI delisting. We now proceed to adopt the CSI hazardous waste
delisting without substantive revision from the February 1, 1996 proposal for public comment
for the reasons discussed below.
The Board had traditionally adopted hazardous waste delistings using the identical-in-
substance procedure. As explained in the June 1, 1995 opinion and order in the prior
consolidated update docket, R95-4/R95-6:
In response to petitions from Amoco Corporation (R85-2), Envirite Corporation
(R87-30), and USX Corporation (R91-12), the Board added the federally-
granted delistings to the tables.
On April 30, 1990, at 55 Fed. Reg. 7320 (March 1, 1990), U.S. EPA
authorized Illinois to grant hazardous waste delistings. On February 28, 1991,
in docket R90-17, the Board adopted procedures for granting the delistings
using the statutorily-prescribed adjusted standard mechanism. Since gaining the
authority and establishing the procedures, the Board has granted hazardous
waste delistings by adjusted standards.
Nothing in the adoption of the adjusted standard procedure to accommodate federal
authorization of this segment of the Illinois RCRA Subtitle C regulations was intended to
supersede the identical-in-substance procedure. Rather, the adjusted standard procedure was
intended to provide another necessary tool for use when the Board was required to conduct a
substantive, de novo review of the merits of a delisting, which was the subject of the R90-17
procedural rulemaking. Since there would be no federally-granted delisting that would allow
the use of the identical-in-substance procedure, the Board was required to use a process for
such substantive review. Rather than being antagonistic towards the more recently-adopted
21
adjusted standard procedure, the identical-in-substance procedure is a complementary tool;
each procedure is useful for its own particular purpose.
The purpose behind the identical-in-substance procedure of Sections 7.2 and 22.4(a) of
the Act is to allow the Board to expeditiously adopt amendments that are necessary to maintain
a federally-approvable RCRA Subtitle C program. While incorporating the elements necessary
to assure that the Illinois program is no less stringent than and not inconsistent with the federal
program, as required by federal law (see 42 U.S.C § 6926(b); 40 CFR 271.3 & 271.4), the
purpose is also to assure that the Illinois RCRA Subtitle C program does not become
inadvertently more stringent than the federal program. It is within the Board's discretion to
accept a federal hazardous waste delisting using the identical-in-substance procedure or to
require the petitioner to use the adjusted standard procedure to obtain delisting. Whether it is
a federal decision to remove a category of listed hazardous waste or a decision to remove
certain wastes from a category of listed hazardous waste, the result is the same: the federal
action renders the Illinois regulations more stringent than the federal rules upon which they are
based as to the affected wastes. In the interest of keeping the Illinois RCRA Subtitle C
regulations from becoming more stringent than the federal rules, Section 22.4(a) has long been
understood as requiring the Board to incorporate the farther-reaching federal action of effecting
removal of an entire category of listed hazardous waste (see, e.g., R90-11, Apr. 11, 1991).
Therefore, the Board has pursued the practice of allowing a person that has obtained a federal
hazardous waste delisting to request that the Board remove a listed waste from a category,
whether using the identical-in-substance procedure or the adjusted standard procedure.
1
Having determined that the identical-in-substance procedure is a legitimate mechanism
for adopting a federally-granted hazardous waste delisting, the Board notes that such procedure
does not allow us to revisit the merits of the delisting. The theory behind the identical-in-
substance procedure is that USEPA has reviewed all the merits of the actions that it has
undertaken, so substantive Board review of those actions is not necessary. For these reasons,
the Board does not further consider all the arguments put forward in favor of or opposition to
the CSI delisting. If any person wishes to render the Illinois rules more stringent than the
federal RCRA Subtitle C regulations in this regard, we observe that the appropriate context for
such considerations is in a Sections 22.4(b) and 27 general rulemaking proceeding.
Postponement of Subpart CC Organic Emissions Rules Effective Date--Sections 724.980,
724.989, 725.980, 725.982 & 725.990
1
The Board notes, contrary to HRD's assertions, that the delisting of hazarodus waste in
Illinois does not remove the waste from regulation. Rather, the waste is regulated as "special
waste", since it would fulfill the statutory definition of such a waste. (See Sections 3.15,
3.17, 3.27, 3.45, 21 & 22.01.)
22
USEPA adopted the 40 CFR 264, Subpart CC and 265, Subpart CC organic material
emission regulations applicable to hazardous waste tanks, containers, and surface
impoundments in December, 1994. It stayed the effective date of those rules by six months on
May 19, 1995, at 60 Fed. Reg. 26828. As discussed above, the Board incorporated both the
original adoption and that first six-month stay into the Illinois regulations in the prior update
docket, R95-4/R95-6.
USEPA granted further limited stays of the Subpart CC regulations on September 29,
1995, at 60 Fed. Reg. 33912, November 13, 1995, at 60 Fed. Reg. 56952, and June 5, 1996,
at 61 Fed. Reg. 28508. As discussed above, USEPA indefinitely stayed the rules as to wastes
from the manufacture of organic peroxides in the September action, for safety reasons.
USEPA amended 40 CFR 264.1080, 264.1089, 265.1080, and 265.1090, which correspond
with 35 Ill. Adm. Code 724.980, 724.989, 725.980, and 725.990, to effect this stay. USEPA
then granted a second six-month stay of the effective date for the rules in their entirety in the
November action, until June 6, 1996, and a further four-month stay in the June action, until
October 6, 1996. This required amendment of 40 CFR 264.1080, 265.1080, and 265.1082
(corresponding with 35 Ill. Adm. Code 264.980, 265.980, and 265.982).
The Board has incorporated both stays into this docket in response to public comments
and to avoid a situation where the Illinois regulations could be read as more stringent than the
federal rules. In anticipation of these further stays, the Board added Board Notes to Sections
724.1080(a) and 725.1080(a) in the R95-4/R95-6 update to cite the earlier stay and to explain
that we do not intend greater stringency. Therefore, to incorporate the federal stays, the Board
has amended the effective date citations in these rules to reference October 6, 1996 and the
November 13, 1995 and June 5, 1996 Federal Register citations to the stays at Sections
724.1080(a) and (b), 725.1080(a) and (b), and 725.982(a), to correspond with the federal
revisions at 40 CFR 264.1080(b), 265.1080(b), and 265.1082(a). The Board has further
added the new language for the organic peroxides stay at Sections 724.980(d), 724.989(i),
725.980(d), and 725.990(i), to correspond with the federal additions of 40 CFR 264.1080(d),
264.1089(i), 265.1080(d), and 265.1090(i). In incorporating the federal amendments, the
Board notes an error in one of the new effective dates for the Subpart CC rules: USEPA used
"October 6, 1995" in 40 CFR 265.1082(a)(1) (corresponding with 35 Ill. Adm. Code
725.980(a)(1)) instead of the intended "October 6, 1996". We corrected the error.
The Board lists its deviations from the text of the Subpart CC stay amendments in the
following table for the convenience of those who must make a detailed comparison of the
federal and state texts:
Deviations from the Federal Text of the Subpart CC Stays*
Section
Derived from
Deviation(s)
724.980(a)
264.1080(a)
Altered effective date and Board Note
previously added to federal base text
23
724.980(d)
264.1080(d)
Removed "administratively"; remove "a";
add comma
724.980(d)(3)
264.1080(d)(3)
Used "must"; removed comma from two-
element series
724.990(i)(2)
264.1090(i)(2)
Added "pursuant to"; use "must"
724.990(i)(2)(A)
264.1090(i)(2)(i)
Used "must"; used commas in place of
semicolons
724.990(i)(2)(b)
264.1090(i)(2)(ii)
Used "must"; used commas in place of
semicolons; removed commas from two-
element series; use singular "waste" and
"this"; replaced "handled" with "managed"
724.990(i)(3)
264.1090(i)(3)
Used "or" in place of "and"; added
"pursuant to" and "specified in"; used
"were" to state condition contrary to fact;
used "must"
724.990(i)(3)(A) &
(B)
264.1090(i)(3)(i) &
(ii)
Used singular "waste" and "this"; used
"must"; used "would" to state condition
contrary to fact
725.980(a)
265.1080(a)
Altered effective date and Board Note
previously added to federal base text
725.980(d)
265.1080(d)
Removed "administratively"; removed "a";
add comma
725.980(d)(3)
265.1080(d)(3)
Used "must"; removed comma from two-
element series
725.982(a)(1)
265.1080(a)(1)
Used "October 6, 1996" in place of "October
6, 1995"
725.990(i)(2)
265.1090(i)(2)
Added "pursuant to"; used "must"
725.990(i)(2)(A)
265.1090(i)(2)(i)
Used "must"; used commas in place of
semicolons
725.990(i)(2)(b)
265.1090(i)(2)(ii)
Used "must"; used commas in place of
semicolons; removed commas from two-
24
element series; used singular "waste" and
"this"; replaced "handled" with "managed"
725.990(i)(3)
265.1090(i)(3)
Used "or" in place of "and"; added
"pursuant to" and "specified in"; used
"were" to state condition contrary to fact;
used "must"
725.990(i)(3)(A) &
(B)
265.1090(i)(3)(i) &
(ii)
Used singular "waste" and "this"; used
"must"; used "would" to state condition
contrary to fact
* Additional deviations appear in the discussion of revisions to the text of the proposed rules
based on public comments, beginning below on page 48.
The Board invited comment on our codification of the federal stays of the Subpart CC
regulations. The two stays upon which the Board sought comment were the indefinite stay
relating to organic peroxides manufacturing waste and the second six-month general stay of the
rules. We received no comment on these matters.
Universal Waste Rules--Sections 703.123, 720.110, 720.120, 720.123, 721.105, 721.106,
721.109, 722.110, 722.111, 724.101, 725.101, 726.180, 728.101 & Part 733
USEPA adopted a major new body of alternative hazardous waste management
regulations on May 11, 1995, at 60 Fed. Reg. 25492, as 40 CFR 273. These new regulations,
called the "universal waste rule", modify the RCRA Subtitle C program to streamline the
system as it applies to these widely-generated wastes. The wastes to which the alternative
regulations currently apply are batteries, pesticides, and mercury-containing thermostats.
USEPA stated in adopting the rules that it intends to expand their applicability to new wastes
in the future, such as fluorescent light bulbs.
In recognition of some fundamental problems with the hazardous waste management
system, USEPA devised the universal waste rule. Its goals are to encourage resource
conservation while adequately protecting human health and the environment, to improve
implementation of the Subtitle C regulations, and to encourage efforts to collect the
unregulated universal waste and remove it from the municipal waste stream. Although
generated in great quantities overall, universal waste is generally generated in small quantities
below the threshold of regulatory concern by individual generators. Thus, they are lawfully
disposed of in municipal trash in large aggregate quantities by these small generators. One
problem with the existing RCRA Subtitle C hazardous waste management scheme is that an
effort to divert or recover these materials from municipal trash at central locations would likely
render the recovery efforts subject to the hazardous waste regulatory scheme, which may be a
25
disincentive to such diversion or recovery efforts and a factor favoring their continued large-
scale disposal in municipal solid waste landfills.
The universal waste rule divides the universe of those handling universal waste into two
groups: large quantity handlers of universal waste (LQHUWs) and small quantity handlers of
universal waste (SQHUWs). A person accumulating and storing 5,000 kilograms (11,000
pounds) or more of universal waste on-site is an LQHUW; a person aggregating less than this
amount is a SQHUW. The major differences in impact of the rules on these entities is that
LQHUW must notify USEPA of its activity and maintain required records for its waste, and
there are no similar requirements imposed on a SQHUW. Both LQHUWs and SQHUWs are
generally prohibited from diluting, treating, and disposing of universal waste, and imposed on
both are general management requirements intended to protect human health and the
environment, such as limitations on waste-related activities and off-site shipment and
packaging and labelling, accumulation time limit, employee training, and release response
requirements.
In addition to requirements imposed on handlers of universal waste, the universal waste
rule includes requirements for universal waste transporters and destination facilities. The
requirements and prohibitions imposed on a universal waste transporter are somewhat similar
to those for handlers to a major extent. The transporter standards include general prohibition
against diluting, treating, and disposing of universal waste, required compliance with USDOT
standards, an accumulation time limit, release response requirements, and destination
requirements. The management standards for destination facilities include requirements for
receipt or diversion or rejection of consignments of universal waste. They also include
recordkeeping requirements for receipts of waste.
The universal waste rule has two additional sets of requirements for universal waste
management. First, the regulations include requirements for importation of universal waste
that subject handlers, transporters, and destination facilities to the universal waste rule when
the shipment arrives in the United States. Second, the universal waste rule includes specific
petition requirements for those interested in asking USEPA or an authorized state to include
additional wastes as subject to universal waste regulation.
Finally, accompanying new 40 CFR 273 were amendments to other segments of the
existing hazardous waste regulations necessary to implement the new rules. These include
amendments to 40 CFR 260.1, to incorporate new definitions; amendment of 260.20(a) and
the addition of 260.23, to accommodate petitions for rulemaking under the universal waste
rule; and amendment of 40 CFR 261.5, 262.10, 262.11, 264.1, 265.1, 266.80, 268.1, and
270.1 and the addition of 261.9, to set forth the applicability and interplay of the universal
waste rule and relevant segments of the generally-applicable hazardous waste management
regulations.
The Board has incorporated the universal waste rule into the Illinois hazardous waste
regulations with minimal, nonsubstantive deviation from the federal text. This incorporation
26
adds Part 733 and Sections 720.123 and 721.109 to the rules and the amendment of Sections
703.123, 720.110, 720.120, 721.105, 721.106, 722.110, 722.111, 724.101, 725.101,
726.180, 728.101. The deviations from the federal language were primarily corrections to
grammar and punctuation, were enhancements in clarity, or were necessary to integrate the
universal waste rules to the Illinois regulatory structure. The Board summarizes the deviations
in a table at the end of this segment of the discussion. The table is intended to aid those
persons, such as JCAR or USEPA, that must compare the federal and state versions of the
text.
One series of routine substitutions bears specific discussion. These are the substitutions
of a state agency to perform functions where USEPA uses its own name in the rules.
Generally, the Board substitutes itself or the Agency for most functions USEPA cites for itself
in the regulations. A routine discussion at the end of this opinion, entitled "Agency or Board
Actions?" outlines the circumstances that dictate whether the Agency or the Board is used in
substitution. An exception is the grant of an extension to the federal effective date for a land
disposal restriction under 40 CFR 268.5, which is beyond a state's authority to grant. Another
example is the granting of federal facility identification numbers under 40 CFR 262.12,
263.11, 264.11, or 265.11.
In the universal waste rule, the Board encountered two special instances of
substitutions. The first is the notification requirements of Sections 733.112 (small quantity
handlers of universal waste; derived from 40 CFR 273.12) and 733.132 (large quantity
handlers of universal waste; derived from 40 CFR 273.32). Both appear parallel to RCRA
section 3010 notification, since the handler must obtain a USEPA identification number. For
this reason, the Board has retained the requirement of notifying USEPA while imposing the
duty to also notify the Agency of the activity.
2
Second, Section 733.161(c) (derived from 40 CFR 273.61(c)) imposes a notification
requirement on a destination facility if it receives a shipment containing hazardous waste.
Since this is clearly an enforcement-related notification, the Board has required notification of
the Agency alone.
Finally, in the 733.Subpart G and Section 720.123, the Board has substituted itself as
the appropriate person to petition for inclusion of additional hazardous waste in regulation as
universal waste. The preamble Federal Register discussion, at 60 Fed. Reg. 25537, indicates
that USEPA intends that states may obtain federal authorization to grant additions to universal
2
The Board realizes that USEPA and the Agency work cooperatively in exchanges of
information and in policing regulated entities. However, requiring notification to both entities gives
the regulators and the regulated community an added measure of certainty that both sets of files are
complete.
27
waste similar to state authorization to grant hazardous waste delistings.
3
In the February 1,
1996 proposed opinion, the Board stated its belief that we cannot effectively grant an addition
to universal waste until the state received federal authorization of that aspect of our
regulations, similar to hazardous waste delistings. Further, federal primacy provisions would
make a federal grant of universal waste status ineffective in Illinois until also granted by the
Board.
4
For these reasons, the Board has crafted the universal waste designation provisions so
that it is clear that we will consider federally-granted designations using the identical-in-
substance procedure and those not federally-granted using the general rulemaking procedure.
The Board has added a Board Note at Section 733.180(a) of the proposed rule
explaining our authority to include additional hazardous waste as universal waste. We noted in
the proposed opinion that section 3009 of RCRA Subtitle C does not allow states to adopt
regulations that are less stringent than the federal regulations. We voiced our opinion that if
the Board were to include additional waste before receiving federal authorization to do so, the
Illinois hazardous waste regulations would violate this requirement. For these reasons, the
added the following language in the proposed Board Note:
The Board cannot add a hazardous waste or category of hazardous waste to this
Part by general rulemaking until USEPA authorizes the Illinois universal waste
regulations. The Board may, however, add a waste or category of waste by
identical-in-substance rulemaking.
We have revised this note in final adoption in response to Agency comments, discussed below
(infra p. 48).
We further noted in the proposed opinion that in establishing the universal waste
designation procedure, the Board realizes that an alternative procedure is available. Instead of
general rulemaking, the Board stated that we could use the adjusted standard procedure of
Section 28.1 of the Act and 35 Ill. Adm. Code 106 to grant universal waste designations, just
like it is used for hazardous waste delistings, once USEPA has conferred this authority on the
state. We opted for the general rulemaking procedure because it appears that universal waste
designations are broader in effect than the delisting of a particular generator's hazardous
waste. Since general rulemaking would result in incorporation of the designation into the
3
An authorization granted the Board effective April 30, 1990, at 55 Fed. Reg. 7320 (March 1,
1990).
4
Section 3006 of RCRA (42 U.S.C. § 6926) provides that state regulations apply in an
authorized state in lieu of the federal regulations. Section 3009 (42 U.S.C. § 6929) provides that
states may establish regulations that are more stringent than the federal regulations. These
provisions made it necessary for owners and operators to obtain relief at both the federal and state
levels until Illinois obtains universal waste authorization from USEPA.
28
regulations, the Board felt that the enhanced public notice would prove beneficial. We discuss
Agency comments on this point below (infra pp. 31-33).
As a final point, the Board notes that in amending 40 CFR 260.20 (corresponding with
35 Ill. Adm. Code 721.120), USEPA added a reference to the Part 273 universal waste
regulations. When adopting the used oil regulations in September, 1992, USEPA did not
amend this provision to reflect amendments to amend the used oil rules. The Board notes this
possible error in the federal text, but we did not propose its correction. It is possible that
USEPA does not intend petitions to amend the used oil rules under this provision. It is further
possible that such an amendment would render the Illinois regulations less stringent than the
federal regulations. Of course, the Board could add a reference to Part 739 if USEPA
indicates that the lack of a corresponding reference at 40 CFR 260.20(a) is an oversight.
The Board invited comment on various aspects of our approach to the universal waste
rule. The Board expressly invited comment on specified issues:
1.
On the designation of the appropriate person to contact and whether notification of both
USEPA and the Agency is necessary for activity notification, for receipt of a universal
waste consignment containing hazardous waste, and for obtaining a universal waste
designation.
2.
On the burden of dual notification on less sophisticated members of the regulated
community.
3.
On whether the general rulemaking procedure or the adjusted standard procedure is the
more appropriate means of granting universal waste designations to add additional
waste to Part 733.
4.
From USEPA, on whether a reference to rulemaking petitions to amend Part 739
should appear in Section 720.120.
Responses to Comments on the Universal Waste Rule
As briefly outlined above (infra, pp. 6-10), the Board received general comments on
the universal waste rule from the Association of Waste Hazardous Materials Transporters
(AWHMT), the Rechargeable Battery Recycling Corporation (RCRI), the Portable
Rechargeable Battery Association (PRBA), and Browning-Ferris Industries (BFI). We further
received comments from the Agency on the specific issues that we raised in the proposed
opinion and order. We have already outlined the RCRI (PC 9) and PRBA (PC 10) comments
above, at page 9. The following discussion focuses on the AWHMT (PC 12), Agency (PC
11), and BFI (PC 6) comments.
AWHMT explained (in PC 12) that it believes that the complexity of the Universal
Waste Rule transportation requirements will frustrate environmentally sound collection and
29
proper recycling of the covered wastes. It raised a number of transportation-related concerns,
such as increased traffic that AWHMT anticipates in the jurisdictions adopting the universal
waste rule, because transporters "plan a route of travel that avoids states where universal waste
rules are not effective." AWHMT also expressed concern over unresolved issues from the
rules, such as what is the proper form of waste manifesting to comply with the disparities in
waste status among the various state jurisdictions and what are the regulatory status of the
waste and the transporter's responsibilities when waste is rejected at a facility because it does
not fulfill the criteria for universal waste. AWHMT requested that the Board provide guidance
and clarification as to how Illinois will address these concerns.
In response to AWHMT's comments, the Board makes some observations as we
conclude that we are not presently in the position to give firm guidance and clarification as
requested. We prefer to let the various state and federal rules speak for themselves. The
Board has two basic reasons for not attempting to provide the requested guidance and
clarification. One relates to the context of this proceeding, and the second relates to the
relative functions of the Board and the Agency in the Illinois regulatory scheme.
First, relating to the context of this proceeding, the Board adopts the hazardous waste
regulations to be identical-in-substance with the federal rules under the Illinois regulatory
regime, as required by Section 22.4(a) of the Act. In adopting the rules under that mandate,
the Board often tries to clarify our understanding of the federal regulations for the benefit of
the Agency and the regulated community, where the federal regulations appear ambiguous in
light of the stated intent of USEPA in adopting them. The Board would attempt such
clarification at this point if we were aware of any ambiguities in the federal regulations that
could be resolved based on the Federal Register discussion of the rules. However, AWHMT
has not suggested specific passages of the regulations that ambiguously set forth USEPA's
intent, and it has provided no recommendations as to what the Board can do to cure any
defects in any specific passage. Rather, AWHMT directs our attention to problems that could
arise from the federal regulatory scheme itself or from its implementation in our sister states.
There is nothing the Board can do under our identical-in-substance mandate to alter either the
substantive aspects of the federal regulations or to make regulations conform to those of our
sister states (or to make those of our sister states conform to ours). The proper context for
actions that address the substance of a regulation based on a federal action is in a general
rulemaking filed pursuant to Sections 22.4(b) and 27 of the Act.
Second, relating to the structure of the Illinois regulatory scheme and the function of
the Board in that scheme, the Board is limited in its role. The Board's first role is to consider
and adopt the substantive regulations. Under certain instances of actual controversy, such as a
permit appeal, an adjusted standard proceeding, or an enforcement action, the Board acts in a
different role, as necessary, to interpret the rules to resolve the particular controversy at issue.
It is the role of the Agency to implement the regulations through the issuance of permits and
by engaging in site monitoring. In performing its duties, the Agency necessarily interprets the
regulations as it sees fit, consistent with their clear language, the federal intent behind them,
and any Illinois case law on point. Outside the context of an actual controversy, it is
30
inappropriate for the Board to determine the effect of issues raised by the federal regulations
themselves. Such an action would go beyond adopting rules to implementing them, which, as
stated, is the Agency's designated function.
Although the Board cannot perceive how we can clarify or explain the issues raised by
AWHMT at this time, we make the following observations before we highlight various aspects
of the regulations: (1) the regulations include only those requirements included in their
express provisions, and (2) there is no obligation on the part of any person unless a
requirement is expressly imposed by rule. The Board directs AWHMT's attention to the
regulations themselves for clarification and explanation. As to management of universal
waste, Part 733 is an alternative set of regulations to the general hazardous waste standards, as
stated in Section 733.101(b). The rules provide at Section 733.118(c) that universal waste
remains subject to the hazardous materials transportation (Haz-Mat) requirements of 49 CFR
172 and 173, but Section 733.152 states that management as hazardous waste under the Haz-
Mat rules is not necessary because no manifest is required for shipment.
Although Section 733.161 includes requirements for management of waste that is
rejected by the consignee or which was illegally shipped as universal waste, the Board does not
see where the rules impose an additional burden on the transporter as a result of rejection or
illegal shipment. Universal waste that is rejected and reconsigned is still universal waste;
hazardous waste that is illegally shipped as universal waste remains hazardous waste. Despite
the fact that Section 733.161(c) requires the consignee to contact the Agency (or USEPA) for
further instructions for managing illegally shipped hazardous waste, the Board does not see
that the regulations would impose any greater obligation on the transporter, qua transporter,
than to deliver the waste to the designated consignee.
5
We remind AWHMT that it is the
shipper that bears the burden of properly packaging, labelling, and documenting a consignment
of waste under both the RCRA Subtitle C rules (see, e.g., 35 Ill. Adm. Code 722.111,
722.120, 722.130-722.133, 724.171(c), 725.171(c), 733.114, 733.118, 733.134 & 733.138;
49 CFR 172.200(a), 172.300(a), 172.400(a), 173.1(b) & 173.3a(a)). As the Board presently
reads the regulations, the universal waste transporter becomes subject to those requirements
only after it has itself acquired the status of a shipper (see 35 Ill. Adm. Code 733.153-
733.155.) or otherwise assumed some duty under the regulations (see, e.g., 49 CFR 173.1(d)).
We do not see that the rules make a transporter become a shipper in the event of a rejected
shipment of universal waste or an illegal shipment of hazardous waste as universal waste.
In addition to a number of textual corrections, outlined below at pages 48-51, the
Agency (PC 11) responded to substantive questions raised by the Board in the February 1,
1996 proposed opinion and order. The Agency commented that it wants the Board to revise
the text of the proposed rules to require universal waste activity notification to the Agency
only. The Agency stated that it would notify USEPA. It stated that it would forward USEPA
5
That is, of course, unless a hazardous materials incident triggers some other, non-RCRA
Subtitle C requirements, such as 49 CFR 171.15 and 171.16 of the Haz-Mat requirements.
31
form EPA 8700-12 and indicate any additional information required under the universal waste
rules. Upon return of the form to the Agency, the Agency committed to sending the necessary
information to USEPA for assignment of a USEPA identification number. Based on the
Agency's comments, the Board has removed all references to the USEPA and made all
necessary ancillary changes in the universal waste notification requirements, at Sections
733.112 and 733.132(a)(1)-(a)(3) and Board Note. The Board did not receive comments on
this issue from USEPA, and in light of the final action that we are taking,
the Board would
appreciate USEPA comments during the 30-day post adoption comment period on
whether notification of the Illinois EPA alone will satisfy the federal requirements.
The Agency (PC 11) and BFI (PC 6) commented on the procedures for adding
universal waste. The comments did not involve the identical-in-substance procedure for
adding waste after USEPA has already designated it universal waste.
6
They related to the
procedure for the Board to add universal waste on its own authority. The Board proposed the
use of the general rulemaking procedure. BFI raised a few procedural questions as to the type
of petition involved, whether the 200-signature requirement would apply, and the statutory
authority for a "general rulemaking". In response, the Board's authority to adopt non-
federally-derived RCRA Subtitle C regulations arise from Sections 22.4(b), 27, and 28 of the
Act and the Administrative Procedure Act (APA). The petition requirements are provided by
the Act; the APA; Sections 720.120, 720.123, 733.180(c), and 733.181 of the RCRA Subtitle
C regulations; and Parts 101 and 102 of the Board's procedural rules.
The Agency's comments related to the actual choice of procedure for adding universal
waste. The Agency stated that it would prefer that the Board select the adjusted standard
procedure for adding universal waste. The Agency commented that pursuing an adjusted
proceeding to conclusion requires "a lesser investment of resources". The Agency conceded
that the adjusted standard procedure is not ideally suited to universal waste designation and
would not result in the addition of any new universal waste to the text of the regulations, but
stated that industry groups would "get the word out" as to added universal waste.
Alternatively, the Agency suggested that the Board could develop a streamlined general
rulemaking procedure, within the requirements of the APA, for adding universal waste.
The Board fully understands the Agency's concerns and agrees that an alternative to a
full general rulemaking procedure might be easier to use, but we cannot now conceive what
that alternative would entail. The Board also notes that our authority to adopt relief is
constrained by the procedures set forth in the Act and the APA. For example, the Board could
not waive the Act Section 28(a) two-hearing requirement if the universal waste rule would
6
The Board notes that HB 2747 would add Section 22.23a to the Act, which would require
the Board to "seek authorization" by December 31, 1997 from USEPA to include "fluorescent
and high intensity discharge lamps" as universal waste. If USEPA itself designates these
lamps as universal waste prior to that time, Section 22.23a would require the Board to use the
identical-in-substance procedure to adopt that designation for these items.
32
have state-wide applicability. On the other hand, as noted by the Agency, the Board could not
amend Sections 720.110 and 733.106, among others, to add universal waste to the rules using
the adjusted standard procedure.
The Board can presently see three alternative procedures for adding universal waste
once Illinois is authorized by USEPA to add universal waste, and others may also exist:
1.
Use the existing general rulemaking procedure;
2.
Use the existing adjusted standard procedure; or
3.
Use the adjusted standard procedure and some subsequent rulemaking action to codify
any additions to the categories of universal waste.
In examining these options, the Board notes that only options one and three are presently fully
developed. The Board notes that we agree with the Agency that codification of the additions is
desirable. In choosing among these two options, we therefore elect to adopt option one: the
general rulemaking process. We reiterate what we noted above (supra p. 25), however, that
even in adopting the general rulemaking procedure, the Board will remain unable to engage in
such review and designate additional universal waste until USEPA authorizes the Illinois
universal waste program. This could take several months. In the interim, the Board would
welcome an opportunity to reexamine the various procedural options for designating additional
universal waste in the context of a regulatory proceeding, should any interested person
commence a procedural rulemaking before us.
The Agency responded in PC 11 that USEPA intends to publish a policy statement that
would allow a state to add universal waste before final federal authorization of the state'
program. The Agency stated that it intends to apply for federal authorization of the Illinois
program immediately upon adoption of the rules by the Board. The Agency requested that the
Board either remain silent on our authority to designate universal waste prior to federal
authorization or that we reword the Board Note to include the possibility of USEPA allowing
pre-authorization additions to universal waste by the state. We agree with the Agency that
change is necessary and choose to reword the Board Note as follows:
The Board cannot add a hazardous waste or category of hazardous waste to this
Part by general rulemaking until USEPA either authorizes the Illinois universal
waste regulations or otherwise authorizes the Board to add new categories of
universal waste. The Board may, however, add a waste or category of waste by
identical-in-substance rulemaking.
We prefer this option to that of deleting the Board Note altogether, since the Board does in fact
lack all authority to add categories of universal waste until federally authorized to do so.
33
Deviations from the Federal Text of the Universal Waste Rule*
Section
Derived from
Deviation(s)
703.123(h)
270.1(c)(2)(viii)
Used singular; added preamble exclusion to
text; add "such a"; added commas for
parentheticals
720.110 "battery" &
"destination facility"
260.10 "battery" &
"destination facility"
Used "that"
720.110 "pesticide"
260.10 "pesticide"
Added "fulfills one of the . . ." to preamble;
added "it" to subsections; correct citations to
FFDCA; expanded citations to FDA &
FFDCA; added clarifying Board Note to cite
probable source of federal exclusion;
removed comma
720.110 "thermostat"
260.10 "thermostat"
Added "such a"; used singular
720.110 "universal
waste"
260.10 "universal
waste"
Used lower case; added commas for
parentheticals
720.110 "universal
waste handler"
260.10 "universal
waste handler"
Added "either of the following" to preamble;
added definite article; used impersonal
"that"; deleted extra "or"; restructured
subsections
720.120(a)
260.20(a)
Added commas to series; switched to
disjunctive "or"
720.123
260.123 (new)
Changed section heading for clarity; added
"the following" and subdivided subsections;
used "Board"; added "that shows the
following . . ."; added "to that set forth
. . ."
721.105(c)
261.5(c)
Added "the following" to preamble; added
"hazardous waste that" to subsections
721.105(f)(3)(F)
261.5(f)(3)(F)
Added "the facility is"
721.105(g)(3)(F)
261.5(g)(3)(F)
Added "the facility is"
34
721.109
261.9 (new)
Added commas to parenthetical phrases;
moved "therefore" and removed comma
724.101(g)(11)
264.1(g)(11) (new)
Used singular; replaced use of gerund with
restrictive relative clause; combined into a
single sentence; added "following"; added
commas for parenthetical clauses
725.101(c)(14)
265.1(c)(14) (new)
Used singular; replaced use of gerund with
restrictive relative clause; combined into a
single sentence; add "following"; added
commas for parenthetical clauses
728.101(f)
268.1(f) (new)
Used singular; replaced use of gerund with
restrictive relative clause; used "such a" in
place of "persons who"; added "following";
added commas for parenthetical clauses
733.Subparts B & C
headings
273, Subparts B & C
headings
Removed redundant words "universal waste"
733.Subpart G
heading
273, Subpart H
heading
Removed self-reference to Part
733.101(a)
273.1(a)
Added commas to parentheticals
733.102(a)(2)
273.2(a)(2)
Used "that"
733.103(a)
273.3(a)
Replaced gerund with "that meet"
733.103(a)(1)
273.3(a)(1)
Removed "that are"
733.103(b)(1)
273.3(b)(1)
Added missing period
733.103(b)(2)
273.3(b)(2)
Combined into single statement
733.103(b)(4)
273.3(b)(4)
Added waste prequalification for hazardous
waste status; removed redundant "if"
733.103(d)(1)
273.3(d)(1)
Removed "the person conducting the recall"
from preamble and put into subsections
733.103(d)(1)(A) &
(d)(2)
273.3(d)(1)(i) &
(d)(2)
Moved parentheticals for readability
35
733.104(b)(2)
273.4(b)(2)
Added waste prequalification for hazardous
waste status
733.105(b)
273.5(b)
Replaced personal "who" with "that"; used
"shall"
733.106 "large
quantity handler
. . .", "on-site",
"small quantity
handler . . ." &
"universal waste
handler"
273.6 "large quantity
handler . . .", "on-
site", "small quantity
handler . . ." &
"universal waste
handler"
Replaced personal pronouns with impersonal
expressions
733.106 "destination
facility"
273.6 "destination
facility"
Removed comma separating subject and verb
733.106 "on-site"
273.6 "on-site"
Added comma to beginning of parenthetical
733.106 "pesticide"
273.6 "pesticide"
Removed comma from two-element series;
added "fulfills one of the . . ." to preamble;
added "it" to subsections; corrected citations
to FFDCA; expanded citations to FDA &
FFDCA; added clarifying Board Note to cite
probable source of federal exclusion;
removed comma
733.106 "thermostat"
273.6 "thermostat"
Added "such a"; used singular
733.106 "universal
waste"
273.6 "universal
waste"
Used lower case; added commas for
parentheticals
733.106 "universal
waste handler"
273.6 "universal
waste handler"
Added "either of the following" to preamble;
added definite article; used impersonal
"that"; deleted extra "or"; added defined
term to preamble to exclusions; restructured
subsections
733.111
273.11
Moved "prohibited from . . ." into
preamble; removed comma from two-
element series
733.112
273.12
Added "its" to clarify breadth of obligation
36
733.113(a) & (a)(1)
273.13(a) & (a)(1)
Used "shall"
733.113(a)(2)
273.13(a)(2)
Added comma to parenthetical
733.113(a)(3)
273.13(a)(3)
Used impersonal "that"; used "shall"
733.113(a)(3) &
(a)(3)(A)
273.13(a)(3) &
(a)(3)(i)
Used "or" in place of "and/or"
733.113(a)(3)(B)
273.13(a)(3)(ii)
Added "nonhazardous" parenthetical; added
Board Note referencing sources of
nonhazardous waste regulations
733.113(b)
273.13(b)
Corrected verb to singular
733.113(c) & (c)(1)
273.13(c)(1)
Used "shall"
733.113(c)(2)
273.13(c)(2)
Added "follows each . . ." to preamble, "it"
to subsections
733.113(c)(3)
273.13(c)(3)
Added subsection heading; used impersonal
"that"; used "shall"; added "or" at end of
subsection; used "or" in place of "and/or";
added "nonhazardous" parenthetical; added
Board Note referencing sources of
nonhazardous waste regulations
733.114
273.14
Used "and" in place of slash in heading;
used "shall"; used "as follows" in preamble
733.114(a)
273.14(a)
corrected use of commas; added missing
quotation mark; corrected placement of
quotation marks
733.114(b)
273.14(b)
Added comma in series; added comma to
parenthetical; added "as follows"; corrected
placement of quotation mark
733.114(c)
273.14(c)
Added comma in series; added commas to
parenthetical; added "as follows"; added
subsection heading; used "USDOT"; added
"or"; corrected placement of quotation mark
733.114(d)
273.14(d)
Corrected use of commas; added missing
quotation mark; corrected placement of
37
quotation marks
733.115(a)
273.15(a)
Deleted comma from two-element series
733.115(b)
273.15(b)
Deleted commas from non-parenthetical
language; added "are"
733.115(c)
273.15(c)
Used impersonal "that"; used "shall"; added
"in any of the following . . ."; moved "on-
site"; used "that"; used past-tense "became"
and "was"
733.116
273.16
Used "shall"
733.117
273.17
Used "shall"; used singular, generic "waste"
733.118(a)-(e)
273.18(a)-(e)
Used "shall"; added comma to series; deleted
comma from two-element series; used
"USDOT"
733.118(f)
273.18(f)
Deleted comma from two-element series;
used impersonal "it"; added "originating
handler"; added "shall perform either . . ."
733.118(g)
273.18(g)
Used "shall"; gave Agency as contact
733.118(h)
273.18(h)
Added comma in series; added
"nonhazardous" parenthetical; added Board
Note referencing sources of nonhazardous
waste regulations
733.120
273.20
Used impersonal "that"; used "shall"; used
semicolons in series; used "USEPA"; added
comma for parenthetical
733.131
273.31
Moved "prohibited from" to preamble;
added commas for parentheticals
733.132(a)
273.32(a)
Added subsection heading; used "shall";
added reference to "Region V"; added
references to notification of Agency; used
"USEPA"; used impersonal "that" and "its";
added commas in parentheticals
38
733.132(g)
273.32(g)
Added explanatory Board Note
733.133(a) & (b)
273.33(a) & (b)
Used "shall"; added commas in
parentheticals; removed comma from two-
element series; used "or" in place of
"and/or"; added "nonhazardous" parentheti-
cal; added Board Note referencing sources of
nonhazardous waste regulations
733.133(c)
273.33(c)
Used "shall"; added "follows each . . .";
added "it" to subsections; added subsection
heading; used impersonal "that"; added "or";
used "or" in place of "and/or"; added
"nonhazardous" parenthetical; added Board
Note referencing sources of nonhazardous
waste regulations
733.134
273.34
Used "and" in place of virgule; used "shall";
used "as follows"; corrected placement of
quotation marks; used commas in parentheti-
cals; added subsection heading; used
"USDOT"; added "or"; removed commas
from non-parenthetical language
733.135
273.35
Removed commas from non-parenthetical
language; used "shall"; added "in any of the
following ways"; moved "on-site"; used
"that"; used past-tense "became" and "was"
733.136
273.36
Used "shall"
733.137
273.37
Used "shall"; used singular "waste"
733.138
273.38
Used "shall"; used "USDOT"; used
impersonal "it" & "the originating handler";
added "perform either of . . ."; gave Agency
as contact; added "nonhazardous" parentheti-
cal; added Board Note referencing sources of
nonhazardous waste regulations
733.139
273.39
Used "shall"
733.140
273.40
Used impersonal "that"; used "shall; added
semicolons in series; used "USEPA"
39
733.151
273.51
Moved "prohibited from . . ." to preamble
733.152
273.52
Used "USDOT"; added incorporation cross-
references; removed reference to USEPA
733.153
273.53
Used "shall"
733.154
273.54
Used "shall"; used singular "waste"
733.155
273.55
Used "USDOT"; added incorporation cross-
reference
733.156
273.56
Used "USEPA"; used "shall"; added "the
following"
733.160
273.60
Replaced colon with period; used "shall"
733.161
273.61
Added comma & "a" in series, used
impersonal "it" & "the shipper"; used
"shall"; gave Agency as contact; added
"nonhazardous" parenthetical; added Board
Note referencing sources of nonhazardous
waste regulations
733.162
273.62
Used "shall"
733.170
273.70
Used "as follows"
733.180
273.80
Used "as follows"; restructured to indicate
both identical-in-substance and general
rulemaking routes; gave the Board as the
source of relief; added Board Note;
subdivide subsection (c); used "the requested
relief"
733.181
273.81
Deleted self-reference to Part from Section
heading; added subsection headings; used
"or" in place of "and/or"; used "USDOT"
40
* Additional deviations appear in the discussion of revisions to the text of the proposed rules
based on public comments, beginning below on page 48.
Deletion of Obsolete, Redundant, and Outdated Rules--Sections 702.110, 703.150
through 703.152, 726.203 & 726.204
USEPA engaged in a series of actions on June 29, 1995 prompted by a Presidential
directive. On March 4, 1995, the President ordered all executive agencies to review their
regulations and identify those that are obsolete or unduly burdensome. USEPA adopted
amendments to its RCRA Subtitle C and Subtitle D programs on June 29, 1995, at 60 Fed.
Reg. 33912, that delete obsolete, redundant, and outdated segments of those rules. A handful
of amendments were prompted to the Illinois rules by those federal amendments. As an
expedient way of outlining the federal amendments and the corresponding Board actions, the
Board sets forth the following table indicating the federal deletions and corresponding Board
actions:
Obsolete, Redundant, and Out-Dated Provisions Deleted
40 CFR Provision
35 Ill. Adm. Code
Provision
Federal Action; Board Comments
261.31(a) footnote 1
721.131(a)
Removal of note re the administrative stay of
F032, F034, and F035 listings; deleted by
Board on October 21, 1993 in R93-4
266.103(c)(5)
726.203(c)(5)
Deletion of language relating to election to
comply with alternative HC provision of
266.104(f); amendment made
266.104(f)
726.204(f)
Deletion of alternative HC limit; amendment
made
267
(727)
Deletion of interim standards for new
hazardous waste disposal facilities that
expired on February 13, 1983; no
amendment necessary because the Board
never adopted the standards
270.2 "Phase I",
"Phase II" & "interim
authorization"
702.110
"Phase I" and "Phase II" definitions deleted,
statutory reference updated; amendments
made
41
270.10(e)(4)
703.150(d)
References to "Phase II" deleted; although
the Board did not incorporate the references,
so none directly required, but amendment
made to removed language relating to federal
authorization of Illinois (Phase II) program
rules and Board Note updated to indicate
federal amendment
270.10(f)(2)
703.151(b)
References to "Phase II" deleted; the Board
did not incorporate the references, so none
directly required, but Board Note updated to
indicate federal amendment
270.10(g)(1)
703.152(a)
References to "Phase II" deleted; the Board
did not incorporate the references, so none
directly required, but Board Note updated to
indicate federal amendment
REVISIONS TO THE TEXT OF THE PROPOSED AMENDMENTS
The Board has made a number of revisions to the text of the amendments that appeared
in the February 1, 1996 proposed order of the Board. All of the revisions are minor in
character, limited to corrections of usage, spelling, punctuation, and grammar. Most of these
revisions were prompted by JCAR. Smaller numbers of changes were prompted by the
Board's subsequent review of the text and by public comments: PC 11, from the Agency, and
PC 16, from USEPA.. For the convenience of JCAR, the Agency, and the regulated
community, the Board summarizes the revisions in tabular form below.
Revisions Prompted by JCAR
In addition to the public comments, the Board received from JCAR a set of documents,
each pertaining to a particular Part involved in this proceeding and entitled "Identical First
Notice Line Numbered Version". The text of these documents reflects the text of the
regulations as re-typed by JCAR for publication in the Illinois Register. Unknown to the
Board, JCAR undertook a series of revisions to the text as submitted by the Board for
publication. These revisions are not JCAR recommendations; rather, JCAR actually made the
changes on its own without consulting Board staff. The result is that a number of changes
were made without the prior knowledge of the Board between February 1, when the Board
voted to propose the amendments, and February 16, when the amendments appeared in the
Illinois Register. Determining the exact location and nature of the JCAR-initiated revisions
took significant effort on the part of Board staff. The Board would have preferred to accept a
series of recommended changes from JCAR and incorporated the acceptable ones in this final
42
adoption. Most of the revisions are useful corrections that the Board now incorporates into the
text of the amendments as adopted in the accompanying order. The Board will not accept a
small number of the JCAR-incorporated changes. Two tables follow. The first table indicates
the JCAR revisions that the Board has accepted, explicitly indicating which of the revisions are
a variation of a JCAR suggestion. The second table indicates the JCAR revisions that the
Board declines to make, briefly indicating the Board's reason for not wanting to incorporate
each one declined.
JCAR Revisions to the Text of the Proposed Rules that the Board Has Accepted
Section
Correction
702.110 "CWA", "SDWA"
Commas added and deleted
702.110 "wastewater treatment unit"
Subsection repunctuated
702.110 "well"
Quotation mark added
703.123(g)
Changed end punctuation
703.123(h)
Removed redundant language: "is not
subject to the requirements of this Part"
703.150(a)(2)
Added "or"
703.123(h)
Deleted "is not subject to the requirements
of this Part" (as redundant in light of the
preamble language)
703.152(a)(2)
Changed end punctuation
703.152(b)
Corrected "paragraph" to "subsection"
720.110 "destination facility"
Deleted comma after "accumulated"
720.110 "federal, state, and local approvals
or permits necessary to begin physical
construction"
Added commas after "state"
720.110 "industrial furnace"
Added period after "as generated"
720.110 "pesticide"
Added "by" after "determined"
43
720.110 "qualified groundwater scientist"
Deleted Illinois Revised Statutes reference
720.120(a)
Corrected "35 Ill. Adm. Code . . . 268 or
273" to "35 Ill. Adm. Code . . . 728 or
733"
720.123(b)
Divided further into two subsections,
adding subsection heading; added "each of"
before "the following" (variations on JCAR
suggestions)
721.103(a)(2)(D)(vi)
Corrected subsection number; corrected
"can not" to "cannot"; removed "is" after
"or"
721.104(e)(2)(E)(iii) & 721.105(d)(2)
Deleted commas from ends
721.105(e)(1) & (e)(2)
Corrected "Sections" to "Section"
721.105(f)(2)
Corrected "subsections" to "subsection"
721.105(f)(3)(B) & (g)(3)(B)
Deleted "in" before "interim status"
721.106(a)(3)(A)(ii)
Changed end punctuation
721.109 Source Note
Added "effective"
721.132 "K066" listing
Removed Illinois Revised Statutes citation
and corrected Illinois Compiled Statutes
citation format
721.132 "K149" listing
Deleted end punctuation
721.133(a), (b) & (d)
Changed "subsections" to "subsection"
721.133(e) "P001", "P047", "P051",
"P075" & "P108" listings
Removed "P" notations from CAS numbers
and added footnote and Board Note to
restore missing federal language relating to
the number for the parent compounds (a
variation on the JCAR suggestion to move
the "P" notations); added end punctuation
to second P001 listing
44
721.Appendix G "F005", "F039", "K036",
"K052", "K064", "K065", "K066",
"K088", "K090", "K091", "K117",
"K118", "K123", "K124", "K125",
"K126", "K132" & "K136" listings
Added end punctuation
721.Appendix G "K116" listing
Changed to lower case "tetrachloride"
721.Appendix H "Potassium hydroxy-
methyl-n-methyl-dithiocarbamate" listing
Corrected spelling of "hydroxy"
721.Appendix H "Toluenediamine" listing
Corrected spelling of "benzene"
721.Appendix I, Table B "CSI" delisting
Removed parentheses from references to
conditions; added end punctuation where
missing; removed "those" from before
"metals" (variation of JCAR suggestion);
corrected spelling of "data" & "compiled";
corrected "an" to "and" before "upon
conveyance"; added end quotation mark
where missing
721.Appendix Z
Corrected "characteristics" to
"characteristic" (variation of JCAR
suggestion)
722.110(g)
Removed subsection referring to repealed
provision
722.111(d)
Moved "and"
724.980(d)(1)
Corrected spelling of "structural"
724.980(d)(2)
Added comma before "explaining"
724.980(d)(3)
Corrected spelling of "processes"
725.101(b), (c)(11)(C), (c)(12) & (c)(13)
Changed end punctuation
725.101(c)(14)(A)-(c)(14)(C)
Underlined text added by amendments
(change made by JCAR but not included in
the express listing)
45
725.980(a)
Added "that are" before "subject to";
deleted "either" from before
"725.Subpart"; changed "725.Subparts" to
"725.Subpart"; deleted "the" from before
"725.Subpart"; deleted "rules" from before
"be enforceable"; changed "they become"
to "it becomes" (variations on JCAR
suggestions)
725.980(d)(2)
Added comma before "explaining";
corrected reference to "725.985"
725.980(d)(3)
Added comma before "explaining";
corrected reference to "725.985"
725.982(a) & (b)
Changed "725.Subparts I, J, and K" to
"725.Subpart" (variation of JCAR
suggestions)
725.982(b)(2)(B)
Restructured subsection, adding subsection
heading (variation of JCAR suggestion
725.982(b)(2)(C)
Corrected subsection indent level (variation
of JCAR suggestion)
726.180(b)(1)
Changed end punctuation
726.203(c)(1)(B)(i), (c)(1)(B)(iii),
(c)(1)(K)(ii), (c)(2)(B)(v), (c)(2)(B)(vi),
(c)(4)(A)(vi), (c)(4)(B)(i), (c)(4)(D)(i) &
(j)(1)(B)
Changed end punctuation, adding "and"
where appropriate (variations of JCAR
suggestions at (c)(2)(B)(vi) & (j)(1)(B))
726.203(c)(4)(D)
Changed "either" to "one"
726.203(c)(7)(A)
Deleted "either" (variation of JCAR
suggestion)
728 Source Note
Added references to withdrawal of R90-11
amendments and adoption of R91-13
amendments
728.101(e)(3) & (e)(4)
Changed end punctuation
46
728.101(g)
Corrected reference to "415 ILCS 5/22.6
or 39(h)"
733.101(b)
Corrected references to "726, and 728"
733.102(a)(2)
Capitalized "726.Subpart G"
733.103(d)(1)(B)
Deleted comma before "or recovery"
733.106 "pesticide"
Added "by" before "regulation"; deleted by
from before "in either"; changed
"subsections of this section" to "paragraphs
of this definition"; added "law"
733.113(a)(3), (a)(3)(A) & (c)(3)(B)
Corrected "exhibit" to "exhibits"
733.113(a)(3)(B) & (c)(3)(C) (Board Note)
Deleted "state" (variation of JCAR
suggestion)
733.113(c)(2)(H)
Changed end punctuation
733.114(b)
Removed comma from before parenthetical
733.114(c)(2)
Changed end punctuation, added "and"
733.118(c)
Changed end punctuation
733.118(g)
Added closing parenthesis
733.118(h) (Board Note)
Deleted "state" (variation of JCAR
suggestion)
733.131(a) & (b)
Deleted "from" from before "disposing"
and "diluting"
733.132 Board Note
Added period within parentheses
733.133(a)(3), (a)(3)(A) & (c)(3)(B)
Corrected "exhibit" to "exhibits"
733.133(a)(3)(B) & (c)(3)(C) (Board Note)
Deleted "state" (variation of JCAR
suggestion)
733.133(c)(2)(H)
Changed end punctuation
47
733.134(a)
Deleted "the" from before "any one"
733.134(c)(2)
Changed end punctuation, added "and"
(variation of JCAR suggestion)
733.138(h) & (Board Note)
Deleted "state" (variation of JCAR
suggestion)
733.140(b)
Corrected reference to "35 Ill. Adm. Code
722.Subpart E" (variation of JCAR
suggestion)
733.150
Capitalized "Subpart"
733.151(a) & (b)
Deleted "from" from before "disposing"
and "diluting"
733.161(c)
Deleted "a" from before "owner or
operator"
733.161(d) (Board Note)
Deleted "state" (variation of JCAR
suggestion)
733.181(a)
Corrected references to "35 Ill. Adm. Code
721.Subpart D" and "35 Ill. Adm. Code
721.Subpart C" (variation of JCAR
suggestion)
733.181(f)
Changed end punctuation
JCAR Revisions to the Text of the Proposed Rules that the Board Has Declined to Accept
Section
Correction; Explanation
720.110 "federal, state, and local approvals
or permits necessary to begin physical
construction"
Capitalize "state"; Word intended in
generic sense and not as limited to Illinois
721.104(f)(1)
Add "(f)" after subsection reference; Not
necessary because the subsection referred to
is clear on its face
48
721.Appendix I, Table B "CSI" delisting
Delete opening quotes from second and
third paragraphs of certification language;
Could lead to misunderstanding as to extent
of required certification language
733.106 "FIFRA"
Change "136-136y" to "136 through 136y";
Use of dash character is standard short-
form citation format
733.113(a)(1) & (c)(1)
Move "in a container" to immediately
follow "contain"; The proposed
construction was direct from the federal
language, and the relocation does not add
clarity
733.113(a)(1) & (b)(1)
Add "and" before "compatible";
"Compatible" is not the last element of the
series
733.133(a)(1) & (c)(1)
Move "in a container" to immediately
follow "contain"; The proposed
construction was direct from the federal
language, and the relocation does not add
clarity
733.113(a)(3)(B) & (c)(3)(C); 733.118(h);
733.133(a)(3)(B) & (c)(3)(C); 733.138(h)
& 733.161(d) (text of rules)
Capitalize "state"; Whether the State of
Illinois or any state was intended by
USEPA is unclear, so using the generic
"state" is a better choice
733.133(c)(1)
Add "and" before "compatible";
"Compatible is not the last element of the
series
Revisions Based on Board Review and Public Comments
Aside from the textual revisions prompted by JCAR, the Board revised the text based
on public comments from USEPA (PC 16) and the Agency (PC 11) and based on our
subsequent review of the text. Where brief explanation is warranted, the Board has added
footnotes to include those explanations. The Board notes that JCAR also submitted some of
the USEPA and Agency-recommended revisions. Where this occurred, the center column
indicates the source of the revision and adds "(& JCAR)".
49
Other Revisions to Text of Proposed Amendments
Section
Source
Revision
721.105(e)(1) & (e)(2)
Board
Added "one or more of the"
721.105(g)(3)(C) & (g)(3)(D)
Board
Used lower case "state"
720.110 "federal, state, and local
approvals or permits necessary to
begin physical construction"
Board
Added commas before "and local"
and "or local"
720.110 "final closure"
Board
Placed in correct alphabetical order
720.110 "pesticide"
Agency
Correct spelling of "definiteness" in
Board Note
721.111(b)
Board
Added incorporations of 49 CFR
171 and 173 for the purposes of
Sections 733.152 & 733.155(b)
720.120(a)
Agency
(& JCAR)
Corrected "35 Ill. Adm. Code . . .
268 or 273" to "35 Ill. Adm. Code
. . . 728 or 733"
721.105(f)(3) & (g)(3)
Agency, Board
Corrected spelling of "conditions";
deleted commas from before "or
ensure"; added commas before "or
disposal facility"; Replaced "either
of which, if located in the United
States, is" with "provided that if the
on-site or off-site facility is located
in the United States, it fulfills any
of the following conditions" (varia-
tions of Agency suggestions
1
)
721.105(f)(3)(B) & (g)(3)(B)
Agency
(& JCAR)
Deleted "in" before "interim status"
50
721.131(a)
Board, Agency
Included the text of the amendments
in the order (although described in
the proposed opinion, see infra pp.
13 & 40, they were omitted from
the proposed order); removed
erroneous space from "2,4,5-tri-
chlorophenol"
721.132 "K149" listing
Agency
(& JCAR)
Deleted end punctuation
721.133(e) "U203" listing
USEPA
Corrected "P023" to "P203" for
"aldicarb sulfone" entry
721.Appendix G "K131" listing
Board
Corrected "sulfte" to "sulfate"
721.Appendix Z
Agency
(& JCAR)
Corrected "characteristics" to
"characteristic"
722.111(d)
Agency
(& JCAR)
Moved "and"
725.982(a)
Board
Changed "Owners or operators of
facilities existing" to "An owner or
operator of a facility in existence"
725.982(b)
Board
Changed "facilities" to "a facility"
726.180(a)
Board
Added comma before "or 705"
726.180(c)
Board & JCAR
Added subsection
2
733.106 "generator"
Board
Corrected reference to "35 Ill.
Adm. Code 721"
725.980(d)(2)
USEPA
(& JCAR)
Corrected reference to "725.985"
725.980(d)(3)
USEPA
Corrected spelling of "processes"
733.101(b)
USEPA
(& JCAR)
Corrected references to "35 Ill.
Adm. Code . . . 726, and 728"
51
733.104 Section heading, including
Table of Contents
Agency
Added "Mercury"
3
733.106 "generator"
Board, Agency
& USEPA
Corrected reference to "35 Ill.
Adm. Code 721"
733.106 "pesticide"
Agency
Correct spelling of "definiteness" in
Board Note
733.112 & 733.132(a)(1)
Agency
Removed "USEPA and"
733.118(g), 733.138(g) &
733.161(c) Board Notes
Agency
Corrected Agency address
733.132(a)(2) & (a)(3)
Agency
Changed "USEPA and the Agency"
to "USEPA or the Agency"
733.132 Board Note
Agency
Deleted "ordering information for";
changed "RCRA/Superfund Hotline
at 1-800-424-9346 or 703-920-
9810." to "Agency at 217-782-
6761"
733.138(g)
USEPA
Corrected spelling of "Agency"
733.161(c)
Agency
(& JCAR)
Deleted "a" from before "owner or
operator"
733.180(a)(1) & (a)(2)
Board
Corrected references to "35 Ill.
Adm. Code 101 and 102"
733.180(a) Board Note
Agency
Changed "USEPA authorizes the
Illinois universal waste regulations"
to "USEPA either authorizes the
Illinois universal waste regulations
or otherwise authorizes the Board to
add new categories of universal
waste"
733.181(a)
Agency
Corrected reference to "35 Ill.
Adm. Code 720.110"
52
1
The Board chose this wording over the Agency suggestion, "provided that such on-site or off-
site facility, if located in the United States, meets the applicable condition of those following",
for even greater clarity.
2
The Board adapted this provision from 40 CFR 273.2(a)(2) (corresponding with 35 Ill. Adm.
Code 733.102(a)(2)). The general pattern for the RCRA Subtitle C applicability statements is
to clearly indicate the existence of other Subtitle C rules that potentially apply. For example,
see 40 CFR 268.1(f) (corresponding with 35 Ill. Adm. Code 728.101(f)) and 273.2(a)(2). The
Board added the converse of Section 733.102(a)(2) as new subsection 726.180(c) to enhance
the clarity of the larger body of the RCRA Subtitle C regulations after JCAR inquired as to
why such a similar statement was absent from this Section.
3
USEPA adopted "Applicability--thermostats" in the table of contents (at 60 Fed. Reg. 25542,
May 11, 1996) but gave the actual textual section heading as "Applicability--mercury
thermostats" (at 60 Fed. Reg. 25543). The Board used the version without "mercury" because
the Section 733.106 definition of "thermostat" defines such as containing mercury. The Board
accepted the Agency's suggestion to add the word to the Section heading in order to enhance
the facial clarity of the requirements.
HISTORY OF RCRA SUBTITLE C and UIC ADOPTION
The Illinois UIC (Underground Injection Control) and RCRA (Resource Conservation
and Recovery Act) Subtitle C regulations, together with more stringent state regulations
particularly applicable to hazardous waste, include the following Parts of Title 35 of the
Illinois Administrative Code:
700
Outline of Waste Disposal Regulations
702
RCRA Subtitle C and UIC Permit Programs
703
RCRA Subtitle C Permit Program
704
UIC Permit Program
705
Procedures for Permit Issuance
709
Wastestream Authorizations
720
General
721
Identification and Listing
722
Generator Standards
723
Transporter Standards
724
Final TSD Standards
725
Interim Status TSD Standards
726
Specific Wastes and Management Facilities
728
USEPA Land Disposal Restrictions
729
Landfills: Prohibited Wastes
730
UIC Operating Requirements
53
731
Underground Storage Tanks
732
Petroleum Underground Storage Tanks
738
Hazardous Waste Injection Restrictions
739
Standards for the Management of Used Oil
Special provisions for RCRA Subtitle C cases are included in Parts 102, 103, 104 and
106 of the Board's procedural rules.
History of RCRA Subtitle C and State Hazardous Waste Rules Adoption
The Board has adopted and amended the Resource Conservation and Recovery Act
(RCRA) Subtitle C hazardous waste rules in several dockets. Dockets R81-22 and R82-18
dockets dealt with the Phase I RCRA Subtitle C regulations. USEPA granted Illinois Phase I
authorization on May 17, 1982, at 47 Fed. Reg. 21043. The Board adopted RCRA Subtitle C
Phase II regulations in Parts 703 and 724 in dockets R82-19 and R83-24. USEPA granted
final authorization of the Illinois RCRA Subtitle C "base program" on January 31, 1986, at 51
Fed. Reg. 3778 (January 30, 1986). USEPA granted authorization to "Cluster I revisions" to
the Illinois program and granted partial Hazardous and Solid Waste Amendments (HSWA)
(Pub. L. 98-616, Nov. 8, 1984) authorization effective March 5, 1988, at 53 Fed. Reg. 126
(January 5, 1988). USEPA authorized certain subsequent amendments and granted further
partial HSWA authorizations effective April 30, 1990, at 55 Fed. Reg. 7320 (March 1, 1990),
and June 3, 1991, at 56 Fed. Reg. 13595 (April 3, 1991); August 14, 1994, at 59 Fed. Reg.
30525 (June 14, 1994); and May 14, 1996, at 61 Fed. Reg. 10684 (Mar. 15, 1996). USEPA
codified its approvals of the Illinois program at 40 CFR 272.700 and 272.701 on November
13, 1989, at 54 Fed. Reg. 37649 (Sep. 12, 1989), and on March 31, 1992, at 57 Fed. Reg.
3731 (Jan. 31, 1992). The entire listing of all RCRA Subtitle C identical in substance
rulemakings follows (with the period of corresponding federal revisions indicated in
parentheses):
R81-22
45 PCB 317, September 16, 1981 & February 4, 1982; 6 Ill. Reg. 4828,
April 23, 1982, effective May 17, 1982. (5/19/80 through 10/1/81)
R82-18
51 PCB 31, January 13, 1983; 7 Ill. Reg. 2518, March 4, 1983, effective
May 17, 1982. (11/11/81 through 6/24/82)
R82-19
4
53 PCB 131, July 26, 1983, 7 Ill. Reg. 13999, October 28, 1983,
effective October 2, 1983. (11/23/81 through 10/29/82)
54
R83-24
7
55 PCB 31, December 15, 1983, 8 Ill. Reg. 200, January 6, 1984,
effective December 27, 1983. (Corrections to R82-19)
R84-9
64 PCB 427 & 521, June 13 & 27, 1985; 9 Ill. Reg. 11964, August 2,
1985, effective July 8 & 24, 1985. (1/19/83 through 4/24/84)
R85-22
67 PCB 175, 479, December 20, 1985 and January 9, 1986; 10 Ill. Reg.
968, January 17, 1986, effective January 2, 1986. (4/25/84 through
6/30/85)
R86-1
71 PCB 110, July 11, 1986; 10 Ill. Reg. 13998, August 22, 1986,
effective August 12, 1986. (7/1/85 through 1/31/86)
R86-19
73 PCB 467, October 23, 1986; 10 Ill. Reg. 20630, December 12, 1986,
effective December 2, 1986. (2/1/86 through 3/31/86)
R86-28
75 PCB 306, February 5, 1987; and 76 PCB 195, March 5, 1987; 11 Ill.
Reg. 6017, April 3, 1987, effective March 23, 1987. Correction at 77
PCB 235, April 16, 1987; 11 Ill. Reg. 8684, May 1, 1987, effective
April 21, 1987. (4/1/86 through 6/30/86)
R86-46
79 PCB 676, July 16, 1987; 11 Ill. Reg. 13435, August 14, 1987,
effective August 4, 1987. (7/1/86 through 9/30/86)
R87-5
82 PCB 391, October 15, 1987; 11 Ill. Reg. 19280, November 30, 1987,
effective November 10 & 12, 1987. (10/1/86 through 12/31/86)
R87-26
84 PCB 491, December 3, 1987; 12 Ill. Reg. 2450, January 29, 1988,
effective January 15, 1988. (1/1/87 through 6/30/87)
R87-32
Correction to R86-1; 81 PCB 163, September 4, 1987; 11 Ill. Reg.
16698, October 16, 1987, effective September 30, 1987.
R87-39
90 PCB 267, June 16, 1988; 12 Ill. Reg. 12999, August 12, 1988,
effective July 29, 1988. (7/1/87 through 12/31/87)
R88-16
93 PCB 513, November 17, 1988; 13 Ill. Reg. 447, January 13, 1989,
effective December 28, 1988. (1/1/88 through 7/31/88)
7
On September 6, 1984, the Third District Appellate Court upheld the Board's actions in
adopting R82-19 and R83-24. (Commonwealth Edison Co. v. PCB, 127 Ill. App. 3d 446; 468
N.E.2d 1339 (3d Dist. 1984).)
55
R89-1
103 PCB 179, September 13, 1989; 13 Ill. Reg. 18278, November 27,
1989, effective November 13, 1989. (8/1/88 through 12/31/88)
R89-9
109 PCB 343, March 8, 1990; 14 Ill. Reg. 6225, April 27, 1990,
effective April 16, 1990. (1/1/89 through 6/30/89)
R90-2
113 PCB 131, July 3, 1990; 14 Ill. Reg. 14401, September 7, 1990,
effective August 22, 1990. (7/1/89 through 12/31/89)
R90-11
121 PCB 97, April 11, 1991; corrected at 122 PCB 305, May 23, 1991;
corrected at 125 PCB 117, August 8, 1991; uncorrected at 125 PCB 435,
August 22, 1991; 15 Ill. Reg. 9323, effective June 17, 1991. (Third
Third Land Disposal Restrictions) (4/1/90 through 6/30/90)
R90-17
Delisting Procedures (See below)
R91-1
125 PCB 119, August 8, 1991; 15 Ill. Reg. 14446, effective September
30, 1991. (Wood Preserving Rules) (7/1/90 through 12/30/90)
R91-13
132 PCB 263, April 9, 1992; 16 Ill. Reg. 9489, effective June 9, 1992.
(Boilers and Industrial Furnaces (BIFs) Rules) (1/1/91 through 6/30/91)
R91-26
129 PCB 235, January 9, 1992; 16 Ill. Reg. 2600, effective February 3,
1992. (Wood Preserving Rules Compliance Dates)
R92-1
136 PCB 121, September 17, 1992; 16 Ill. Reg. 17636, effective
November 6, 1992. (7/1/91 through 12/31/91)
R92-10
138 PCB 549, January 21, 1993; 17 Ill. Reg. 5625, effective March 26,
1993. (Leak Detection Systems (LDS) Rules) (1/1/92 through 6/30/92)
R93-4
-- PCB --, September 23, 1993; 17 Ill. Reg. 20545, effective November
22, 1993. (Used Oil Rules) (7/1/92 through 12/31/92)
R93-16
-- PCB --, March 17, 1994, Supplemental opinion and order on April 21,
1994. (1/1/93 through 6/30/93)
R94-7
-- PCB --, June 23, 1994; 18 Ill. Reg. 12160, effective July 29, 1994.
(7/1/93 through 12/31/93)
R94-17
-- PCB --, October 20, 1994; 18 Ill. Reg. 17480, effective November 23,
1994. (1/1/94 through 6/30/94)
56
R95-6
-- PCB --, June 1 & 15, 1995; 19 Ill. Reg. 9501, effective June 27,
1995. (Consolidated with R95-4, UIC Update.) (7/1/94 through
12/31/94)
R95-20
Present docket. (1/1/95 through 6/30/95)
R96-10
Next docket. (7/1/95 through 12/31/95)
The Board added to the federal listings of hazardous waste by listing dioxins pursuant to
Section 22.4(d) of the Act:
R84-34
61 PCB 247, November 21, 1984; 8 Ill. Reg. 24562, December 21,
1984, effective December 11, 1984.
This was repealed by R85-22, which included adoption of USEPA's dioxin listings.
Section 22.4(d) was repealed by P.A. 85-1048, effective January 1, 1989.
The Board has adopted USEPA delistings at the request of Amoco, Envirite, USX, and
CSI (the date of the corresponding federal action is included in parentheses):
R85-2
69 PCB 314, April 24, 1986; 10 Ill. Reg. 8112, May 16, 1986, effective
May 2, 1986. (Amoco Corp.)
R87-30
90 PCB 665, June 30, 1988; 12 Ill. Reg. 12070, July 22, 1988, effective
July 12, 1988. (Envirite Corp.)
R91-12
128 PCB 369, December 19, 1991; 16 Ill. Reg. 2155, effective January
27, 1992. (USX Corp.)
R95-20
This docket. (CSI)
Subsequently, upon the April 30, 1990 federal authorization of Illinois granting waste
delistings, USEPA transferred pending delisting petitions to the Board. The Board docketed
these as site-specific rulemaking proceedings (the name of the petitioner waste generator
appears in parentheses):
R90-18
Dismissed at 123 PCB 65, June 6, 1991. (USX Corp., South Works)
R90-19
Dismissed at 116 PCB 199, November 8, 1990. (Woodward Governor
Co.)
R90-23
Dismissed at 124 PCB 149, July 11, 1991. (Keystone Steel & Wire Co.)
57
The Board has modified the delisting procedures to allow the use of adjusted standards
in lieu of site-specific rulemakings:
R90-17
119 PCB 181, February 28, 1991; 15 Ill. Reg. 7934, effective May 9,
1991.
Waste generators have filed Part 106 adjusted standard petitions for solid waste
determinations with the Board pursuant to Section 720.130 (generator name in parentheses):
AS89-4
Dismissed at 105 PCB 269, November 15, 1989. (Safety-Kleen Corp.)
AS89-5
Dismissed at 113 PCB 111, July 3, 1990. (Safety-Kleen Corp.)
AS90-7
Dismissed at 124 PCB 125, July 11, 1991. (Quantum Chemical Co.)
Waste generators have filed Part 106 adjusted standard petitions for hazardous waste
delistings with the Board pursuant to Section 720.122 (generator name in parentheses):
AS91-1
Granted at 130 PCB 113, February 6, 1992, and modified at 133 PCB
189, April 23, 1992. (Keystone Steel & Wire Co.)
AS91-3
Granted at 139 PCB 121, February 4, 1993; opinion issued at 140 PCB
--, March 11, 1993. (Peoria Disposal Co.)
AS93-7
Granted at -- PCB --, February 17, 1994. (Keystone Steel & Wire Co.)
AS94-10
Granted at -- PCB --, December 14, 1994. (Envirite Corporation.)
The Board has procedures to be followed in cases before it involving the RCRA Subtitle
C regulations:
R84-10
62 PCB 87, 349, December 20, 1984 and January 10, 1985; 9 Ill. Reg.
1383, effective January 16, 1985.
The Board also adopted special procedures to be followed in certain determinations
under Part 106. The Board adopted these Part 106 special procedures in R85-22 and amended
them in R86-46, listed above.
One Part 106 adjusted standard proceeding filed pursuant to 728.106 sought relief from
a prohibition against land disposal (petitioner's name in parentheses):
AS90-6
Dismissed at 136 PCB 93, September 17, 1992. (Marathon Petroleum
Co.)
58
Other adjusted standard proceedings sought relief from aspects of the land disposal unit
closure and post-closure care requirements (petitioners' names in parentheses):
AS90-8
130 PCB 349, February 27, 1992. (Olin Corp.)
AS91-4
131 PCB 43, March 11, 1992. (Amoco Oil Co.)
One adjusted standard proceeding sought relief from a RCRA Subtitle C land disposal
restriction (petitioner's name in parentheses):
AS90-6
136 PCB 6, September 17, 1992. (Marathon Petroleum Co.)
Still another adjusted standard proceeding relates to substantive treatment, storage, and
disposal facility requirements of the RCRA Subtitle C regulations (petitioner's name and
requirements involved in parentheses):
AS91-10
Dismissed at -- PCB --, May 19, 1994. (Cabot Corp.; secondary
containment for tanks)
In another regulatory proceeding, the Board has considered granting temporary relief
from the termination of an exclusion of a hazardous waste listing in the form of an emergency
rule (Petitioner's name in parentheses):
R91-11
Dismissed at 125 PCB 295, August 8, 1991. (Big River Zinc Corp.)
The Board has also adopted requirements limiting and restricting the landfilling of
liquid hazardous wastes, hazardous wastes containing halogenated compounds, and hazardous
wastes generally:
R81-25
60 PCB 381, October 25, 1984; 8 Ill. Reg. 24124, December 14, 1984,
effective December 4, 1984.
R83-28
68 PCB 295, February 26, 1986; 10 Ill. Reg. 4875, March 21, 1986,
effective March 7, 1986.
R86-9
Emergency regulations adopted at 73 PCB 427, October 23, 1986; 10 Ill.
Reg. 19787, November 21, 1986, effective November 5, 1986.
The Board's action in adopting emergency regulations in R86-9 was reversed by the
First District Court of Appeals. (Citizens for a Better Environment v. PCB, 152 Ill. App. 3d
105, 504 N.E.2d 166 (1st Dist. 1987).)
History of UIC Rules Adoption
59
The Board has adopted and amended Underground Injection Control (UIC) regulations
in several dockets to correspond with the federal regulations. One such docket, R82-18, was a
RCRA Subtitle C docket. USEPA authorized the Illinois UIC program on March 3, 1984, at
49 Fed. Reg. 3991 (Feb. 1, 1984); codified that approval as 40 CFR 147, Subpart O, at 49
Fed. Reg. 20197 (May 11, 1984); and amended the authorization at 53 Fed. Reg. 43087 (Oct.
25, 1988). The entire listing of all UIC rulemakings follows (with the period of corresponding
federal revisions indicated in parentheses):
R81-32
47 PCB 93, May 13, 1982; 6 Ill. Reg. 12479, October 15, 1982,
effective February 1, 1984. (7/7/81 through 11/23/81)
R82-18
51 PCB 31, January 13, 1983; 7 Ill. Reg. 2518, March 4, 1983, effective
May 17, 1982. (11/11/81 through 6/24/82)
R83-39
55 PCB 319, December 15, 1983; 7 Ill. Reg. 17338, December 20,
1983, effective December 19, 1983. (4/1/83)
R85-23
70 PCB 311 & 71 PCB 108, June 20 & July 11, 1986; 10 Ill. Reg.
13274, August 8, 1986, effective July 28 & 29, 1986. (5/11/84 through
11/15/84)
R86-27
Dismissed at 77 PCB 234, April 16, 1987. (No USEPA amendments
through 12/31/86).
R87-29
85 PCB 307, January 21, 1988; 12 Ill. Reg. 6673, April 8, 1988,
effective March 28, 1988. (1/1/87 through 6/30/87)
R88-2
90 PCB 679, June 30, 1988; 12 Ill. Reg. 13700, August 26, 1988,
effective August 16, 1988. (7/1/87 through 12/31/87)
R88-17
94 PCB 227, December 15, 1988; 13 Ill. Reg. 478, January 13, 1989,
effective December 30, 1988. (1/1/88 through 6/30/88)
R89-2
107 PCB 369, January 25, 1990; 14 Ill. Reg. 3059, March 2, 1990,
effective February 20, 1990. (7/1/88 through 12/31/88)
R89-11
111 PCB 489, May 24, 1990; 14 Ill. Reg. 11948, July 20, 1990,
effective July 9, 1990. (1/1/89 through 11/30/89)
R90-5
Dismissed at 109 PCB 627, March 22, 1990. (No USEPA amendments
12/1/89 through 12/31/89)
R90-14
122 PCB 335, May 23, 1991; 15 Ill. Reg. 11425, effective July 24,
1991. (1/1/90 through 6/30/90)
60
R91-4
Dismissed at 119 PCB 219, February 28, 1991. (No USEPA
amendments 9/1/90 through 12/31/90)
R91-16
Dismissed at 128 PCB 229, December 6, 1991. (No USEPA
amendments 1/1/90 through 6/30/91)
R92-4
Dismissed at 133 PCB 107, April 9, 1992. (No USEPA amendments
7/1/91 through 12/31/91)
R92-13
139 PCB 361, February 4, 1993; 17 Ill. Reg. 6190, effective April 5,
1993. (1/1/92 through 6/30/92)
R93-6
-- PCB --, August 5, 1993; 17 Ill. Reg. 15641, effective September 14,
1993. (7/1/92 through 12/31/92)
R93-17
Dismissed at -- PCB --, September 23, 1993. (No USEPA amendments
1/1/93 through 6/30/93)
R94-5
-- PCB --, November 3, 1994; 18 Ill. Reg. 18244, effective December
20, 1994. (7/1/93 through 12/31/93)
R94-24
-- PCB --, October 6, 1994. (USEPA amendments 7/1/93 through
12/31/94 included in RCRA Subtitle C docket R94-17)
R95-4
-- PCB --, June 1 & 15, 1995; 19 Ill. Reg. 9501, effective June 27,
1995. (Consolidated with R95-6, RCRA Subtitle C Update.) (7/1/94
through 12/31/94)
R95-18
Dismissed -- PCB --, October 5, 1995. (No USEPA amendments 1/1/95
through 6/30/95)
R96-8
Next docket. (7/1/95 through 12/31/95)
In one proceeding filed, the Board granted an adjusted standard from a UIC land
disposal restriction, pursuant to the procedures outlined above with respect to the RCRA
Subtitle C program (petitioner name in parentheses):
AS92-8
Granted at -- PCB --, February 17, 1994. (Cabot Corp.; no migration
exception)
AGENCY OR BOARD ACTION?
61
Section 7.2(a)(5) of the Act requires the Board to specify which decisions USEPA will
retain. In addition, the Board is to specify which State agency is to make decisions, based on
the general division of functions within the Act and other Illinois statutes.
In situations in which the Board has determined that USEPA will retain decision-
making authority, the Board has replaced "Regional Administrator" with USEPA, so as to
avoid specifying which office within USEPA is to make a decision.
In a few instances in identical in substance rules, decisions are not appropriate for
Agency action pursuant to a permit application. Among the considerations in determining the
general division of authority between the Agency and the Board are:
1. Is the person making the decision applying a Board regulation, or taking action
contrary to ("waiving") a Board regulation? It generally takes some form of Board
action to "waive" a Board regulation.
2. Is there a clear standard for action such that the Board can give meaningful review
to an Agency decision?
3. Does the action result in exemption from the permit requirement itself? If so,
Board action is generally required.
4. Does the decision amount to "determining, defining or implementing
environmental control standards" within the meaning of Section 5(b) of the Act. If so,
it must be made by the Board.
There are four common classes of Board decision: variance, adjusted standard, site
specific rulemaking, and enforcement. The first three are methods by which a regulation can
be temporarily postponed (variance) or adjusted to meet specific situations (adjusted standard
or site specific rulemaking). Note that there often are differences in the nomenclature for
these decisions between the USEPA and Board regulations.
EDITORIAL CONVENTIONS
As a final note, the federal rules have been edited to establish a uniform usage
throughout the Board's regulations. For example, with respect to "shall", "will", and "may" -
"shall" is used when the subject of a sentence has to do something. "Must" is used when
someone has to do something, but that someone is not the subject of the sentence. "Will" is
used when the Board obliges itself to do something. "May" is used when choice of a provision
is optional. "Or" is used rather than "and/or", and denotes "one or both". "Either"..."or"
denotes "one but not both". "And" denotes "both".
62
I, Dorothy M. Gunn, Clerk of the Illinois Pollution Control Board, certify that the
above opinion was adopted on the ________ day of ______________________, 1996, by a
vote of ________.
Dorothy M. Gunn, Clerk
Illinois Pollution Control Board
63
ILLINOIS POLLUTION CONTROL BOARD
June 20, 1996
IN THE MATTER OF:
)
)
R95-20
RCRA UPDATE, USEPA REGULATIONS
)
(Identical in Substance Rules-
(1-1-95 THROUGH 6-30-95, 7-7-95,
)
RCRA Subtitle C)
9-29-95, 11-13-95 & 6-6-96)
)
Adopted Rule.
Final Order.
ORDER OF THE BOARD (by E. Dunham):
Pursuant to Section 13(c) and 22.4(a) of the Environmental Protection Act (Act) [415
ILCS 5/13(c) & 22.4(a) (1994)], the Board adopts amendments to the RCRA Subtitle C
hazardous waste (RCRA) regulations.
Section 22.4(a) provides for quick adoption of regulations that are "identical in
substance" to federal regulations adopted by USEPA to implement Sections 3001 through 3005
of the Resource Conservation and Recovery Act of 1976 (RCRA, 42 U.S.C. §§ 6921-6925)
and that Title VII of the Act and Section 5 of the Administrative Procedure Act (APA) [5
ILCS 100/5-35 & 5-40 (1994)] shall not apply. Because this rulemaking is not subject to
Section 5 of the APA, it is not subject to first notice or to second notice review by the Joint
Committee on Administrative Rules (JCAR). The federal RCRA Subtitle C regulations are
found at 40 CFR 260 through 268, 270 through 271, 279, and, more recently, 273.
This order is supported by an opinion adopted on the same day. The Board will delay
filing the adopted amendments with the Office of the Secretary of State for 30 days to allow
time for the U.S. Environmental Protection Agency to review them prior to filing. The
amendments will become effective upon filing, and Notices of Adopted Amendments (or
Rules, as appropriate) will appear in the Illinois Register. The complete text of the adopted
rules follows.
IT IS SO ORDERED.
64
I, Dorothy M. Gunn, Clerk of the Illinois Pollution Control Board, certify that the
above order was adopted by the Board on the ________ day of _________________________,
1996, by a vote of ________.
__________________________________________
Dorothy M. Gunn, Clerk
Illinois Pollution Control Board
65
TITLE 35: ENVIRONMENTAL PROTECTION
SUBTITLE G: WASTE DISPOSAL
CHAPTER I: POLLUTION CONTROL BOARD
SUBCHAPTER b: PERMITS
PART 702
RCRA AND UIC PERMIT PROGRAMS
SUBPART A: GENERAL PROVISIONS
Section
702.101 Purpose, Scope, and Applicability
702.102 Purpose and Scope (Repealed)
702.103 Confidentiality of Information Submitted to the Agency or Board
702.104 References
702.105 Rulemaking
702.106 Adoption of Agency Criteria
702.107 Permit Appeals and Review of Agency Determinations
702.108 Variances and Adjusted Standards
702.109 Enforcement Actions
702.110 Definitions
SUBPART B: PERMIT APPLICATIONS
Section
702.120 Permit Application
702.121 Who Applies
702.122 Completeness
702.123 Information Requirements
702.124 Recordkeeping
702.125 Continuation of Expiring Permits
702.126 Signatories to Permit Applications and Reports
SUBPART C: PERMIT CONDITIONS
Section
702.140 Conditions Applicable to all Permits
702.141 Duty to Comply
702.142 Duty to Reapply
702.143 Need to Halt or Reduce Activity Not a Defense
702.144 Duty to Mitigate
702.145 Proper Operation and Maintenance
702.146 Permit Actions
702.147 Property Rights
702.148 Duty to Provide Information
702.149 Inspection and Entry
702.150 Monitoring and Records
702.151 Signature Requirements
702.152 Reporting Requirements
702.160 Establishing Permit Conditions
702.161 Duration of Permits
702.162 Schedules of Compliance
702.163 Alternative Schedules of Compliance
702.164 Recording and Reporting
66
SUBPART D: ISSUED PERMITS
Section
702.181 Effect of a Permit
702.182 Transfer
702.183 Modification
702.184 Causes for Modification
702.185 Facility Siting
702.186 Revocation
702.187 Minor Modifications
AUTHORITY: Implementing Section 13 and 22.4 and authorized by Section 27 of the Environmental
Protection Act [415 ILCS 5/13, 22.4 and 27].
SOURCE: Adopted in R81-32, 47 PCB 93, at 6 Ill. Reg. 12479, effective May 17, 1982; amended in R82-19,
at 53 PCB 131, 7 Ill. Reg. 14352, effective May 17, 1982; amended in R84-9 at 9 Ill. Reg. 11926, effective
July 24, 1985; amended in R85-23 at 10 Ill. Reg. 13274, effective July 29, 1986; amended in R86-1 at 10 Ill.
Reg. 14083, effective August 12, 1986; amended in R86-28 at 11 Ill. Reg. 6131, effective March 24, 1987;
amended in R87-5 at 11 Ill. Reg. 19376, effective November 12, 1987; amended in R87-26 at 12 Ill. Reg. 2579,
effective January 15, 1988; amended in R87-29 at 12 Ill. Reg. 6673, effective March 28, 1988; amended in
R87-39 at 12 Ill. Reg. 13083, effective July 29, 1988; amended in R89-1 at 13 Ill. Reg. 18452, effective
November 13, 1989; amended in R89-2 at 14 Ill. Reg. 3089, effective February 20, 1990; amended in R89-9 at
14 Ill. Reg. 6273, effective April 16, 1990; amended in R92-10 at 17 Ill. Reg. 5769, effective March 26, 1993;
amended in R93-16 at 18 Ill. Reg. 6918, effective April 26, 1994; amended in R94-5 at 18 Ill. Reg. 18284,
effective December 20, 1994; amended in R95-6 at 19 Ill. Reg. 9913, effective June 27, 1995; amended in R95-
20 at 20 Ill. Reg. ________, effective ______________________.
SUBPART A: GENERAL PROVISIONS
Section 702.110 Definitions
The following definitions apply to 35 Ill. Adm. Code 702, 703, 704, and 705. Terms not defined in this Section
have the meaning given by the appropriate Act. When a defined term appears in a definition, the defined term is
sometimes placed within quotation marks as to an aid to readers. When a definition applies primarily to one or
more programs, those programs appear in parentheses after the defined terms.
"Act" or "Environmental Protection Act" means the Environmental Protection Act [415 ILCS
5].
"Administrator" means the Administrator of the United States Environmental Protection
Agency, or an authorized representative.
"Agency" means the Illinois Environmental Protection Agency.
"Application" means the Agency forms for applying for a permit. For RCRA, application also
includes the information required by the Agency under 35 Ill. Adm. Code 703.182 through
703.212 (contents of Part B of the RCRA application).
67
"Appropriate act and regulations" means the Resource Conservation and Recovery Act
(RCRA); Safe Drinking Water Act (SDWA); or the "Environmental Protection Act,",
whichever is applicable; and applicable regulations promulgated under those statutes.
"Approved program or approved State" means a State or interstate program that has been
approved or authorized by EPA under 40 CFR 271 (1992) (RCRA) or Section 1422 of the
SDWA (UIC).
"Aquifer" (RCRA and UIC) means a geological "formation", group of formations, or part of a
formation that is capable of yielding a significant amount of water to a well or spring.
"Area of review" (UIC) means the area surrounding an injection well described according to
the criteria set forth in 35 Ill. Adm. Code 730.106, or in the case of an area permit, the project
area plus a circumscribing area the width of that is either 402 meters (1/4 of a mile) or a
number calculated according to the criteria set forth in 35 Ill. Adm. Code 730.106.
"Board" means the Illinois Pollution Control Board.
"Closure" (RCRA) means the act of securing a "Hazardous Waste Management Facility"
pursuant to the requirements of 35 Ill. Adm. Code 724.
"Component" (RCRA) means any constituent part of a unit or any group of constituent parts of
a unit that are assembled to perform a specific function (e.g., a pump seal, pump, kiln liner, or
kiln thermocouple).
"Contaminant" (UIC) means any physical, chemical, biological, or radiological substance or
matter in water.
"Corrective action management unit" or "CAMU" means an area within a facility that is
designated by the Agency under 35 Ill. Adm. Code 724.Subpart S for the purpose of
implementing corrective action requirements under 35 Ill. Adm. Code 724.201 and RCRA
section 3008(h). A CAMU shall only be used for the management of remediation wastes
pursuant to implementing such corrective action requirements at the facility.
BOARD NOTE: U.S. EPA must also designate a CAMU until it grants this authority to the
Agency. See the note following 35 Ill. Adm. Code 724.652.
"CWA" means the Clean Water Act (formerly referred to as the Federal Water Pollution
Control Act or Federal Water Pollution Control Act Amendments of 1972), P.L. 92-500, as
amended by P.L. 95-21, and P.L. 95-576; 33 U.S.C. 1251 et seq. (1992).
"Date of approval by U.S. EPA of the Illinois UIC program" means March 3, 1984.
"Director" means the Director of the Illinois Environmental Protection Agency or the
Director's designee.
"Disposal" (RCRA) means the discharge, deposit, injection, dumping, spilling, leaking, or
placing of any "hazardous waste" into or on any land or water so that such hazardous waste or
any constituent of the waste may enter the environment or be emitted into the air or discharged
into any waters, including groundwater.
68
"Disposal Facility" (RCRA) means a facility or part of a facility at which "hazardous waste" is
intentionally placed into or on the land or water, and at which hazardous waste will remain
after closure. The term disposal facility does not include a corrective action management unit
into which remediation wastes are placed.
"Draft Permit" means a document prepared under 35 Ill. Adm. Code 705.141 indicating the
Agency's tentative decision to issue, deny, modify, terminate, or reissue a "permit". A notice
of intent to deny a permit, as discussed in 35 Ill. Adm. Code 705.141, is a type of "draft
permit". A denial of a request for modification, as discussed in 35 Ill. Adm. Code 705.128, is
not a "draft permit". A "proposed permit" is not a "draft permit".
"Drilling Mud" (UIC) means a heavy suspension used in drilling an "injection well",
introduced down the drill pipe and through the drill bit.
"Elementary neutralization unit" means a device which:
Is used for neutralizing wastes that are hazardous wastes only because they exhibit the
corrosivity characteristics 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 35
Ill. Adm. Code 720.110.
"Emergency Permit" means a RCRA or UIC "permit" issued in accordance with 35 Ill. Adm.
Code 703.221 or 704.163, respectively.
"Environmental Protection Agency" ("EPA" or "U.S. EPA") means the United States
Environmental Protection Agency.
"Exempted aquifer" (UIC) means an "aquifer" or its portion that meets the criteria in the
definition of "underground source of drinking water" but which has been exempted according
to the procedures in 35 Ill. Adm. Code 702.105, 704.104, and 704.123(b).
"Existing hazardous waste management (HWM) facility" or "existing facility" means a facility
that was in operation or for which construction commenced on or before November 19, 1980.
A facility has commenced construction if:
The owner or operator has obtained the Federal, State, and local approvals or permits
necessary to begin physical construction; and
Either:
A continuous on-site, physical construction program has begun; or
The owner or operator has entered into contractual obligations--that cannot be
cancelled or modified without substantial loss--for physical construction of the
facility to be completed within a reasonable time.
"Existing injection well" (UIC) means an "injection well" other than a "new injection well".
69
"Facility or activity" means any "HWM facility", UIC "injection well", or any other facility or
activity (including land or appurtenances thereto) that is subject to regulations under the Illinois
RCRA or UIC program.
"Facility mailing list" (RCRA) means the mailing list for a facility maintained by the Agency
in accordance with 35 Ill. Adm. Code 705.163.
"Federal, State, and local approvals or permits necessary to begin physical construction" means
permits and approvals required under Federal, State, or local hazardous waste control statutes,
regulations, or ordinances. (See 35 Ill. Adm. Code 700.102.)
"Final authorization" (RCRA) means approval by EPA of the Illinois Hazardous Waste
Management Program that has met the requirements of Section 3006(b) of RCRA and the
applicable requirements of 40 CFR 271, Subpart A (1992). EPA granted initial final
authorization on January 31, 1986.
"Fluid" (UIC) means any material or substance that flows or moves whether in a semisolid,
liquid, sludge, gas, or any other form or state.
"Formation" (UIC) means a body of rock characterized by a degree of lithologic homogeneity
that is prevailingly, but not necessarily, tabular and is mappable on the earth's surface or
traceable in the subsurface.
"Formation fluid" (UIC) means "fluid" present in a "formation" under natural conditions, as
opposed to introduced fluids, such as "drilling mud".
"Functionally equivalent component" (RCRA) means a component that performs the same
function or measurement and which meets or exceeds the performance specifications of another
component.
"Generator" (RCRA) means any person, by site location, whose act or process produces
"hazardous waste" identified or listed in 35 Ill. Adm. Code 721.
"Groundwater" (RCRA and UIC) means a water below the land surface in a zone of saturation.
"Hazardous Waste" (RCRA and UIC) means a hazardous waste as defined in 35 Ill. Adm.
Code 721.103.
"Hazardous waste management facility" ("HWM 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 (for example, one or more landfills, surface impoundments, or
combinations of them).
"HWM facility" (RCRA) means "Hazardous Waste Management facility".
"Injection well" (RCRA and UIC) means a "well" into which "fluids" are being injected.
"Injection zone" (UIC) means a geological "formation", group of formations, or part of a
formation receiving fluids through a "well".
70
"In operation" (RCRA) means a facility that is treating, storing, or disposing of "hazardous
waste".
"Interim authorization" (RCRA) means approval by EPA of the Illinois Hazardous Waste
Management program that has met the requirements of Section 3006(cg)(2) of RCRA and
applicable requirements of 40 CFR 271 (1992). This happened on May 17, 1982.
"Interstate agency" means an agency of two or more states established by or under an
agreement or compact approved by the Congress, or any other agency of two or more states
having substantial powers or duties pertaining to the control of pollution as determined and
approved by the Administrator under the "appropriate Act and regulations".
"Major facility" means any RCRA or UIC "facility or activity" classified as such by the
Regional Administrator or the Agency.
"Manifest" (RCRA and UIC) means the shipping document originated and signed by the
"generator" that contains the information required by 35 Ill. Adm. Code 722.Subpart B.
"National Pollutant Discharge Elimination System" means the program for issuing, modifying,
revoking and reissuing, terminating, monitoring, and enforcing permits and imposing and
enforcing pretreatment requirements under Section 12(f) of the Environmental Protection Act
and 35 Ill. Adm. Code 309.Subpart A and 310. The term includes an "approved program".
"New HWM facility" (RCRA) means a "Hazardous Waste Management facility" that began
operation or for which construction commenced after November 19, 1980.
"New injection well" (UIC) means a "well" that began injection after the UIC program for the
State of Illinois applicable to the well is approved.
"Off-site" (RCRA) means any site that is not "on-site".
"On-site" (RCRA) means on the same or geographically contiguous property that may be
divided by public or private right(s)-of-way, provided 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(s)-of-way. Non-contiguous properties owned by the same person but connected by a
right-of-way that the person controls and to which the public does not have access, is also
considered on-site property.
"Owner or operator" means the owner or operator of any "facility or activity" subject to
regulation under the RCRA or UIC programs.
"Permit" means an authorization, license, or equivalent control document issued to implement
the requirements of this Part and 35 Ill. Adm. Code 703, 704, and 705.
"Permit" includes RCRA "permit by rule" (35 Ill. Adm. Code 703.141), UIC area permit (35
Ill. Adm. Code 704.162), and RCRA or UIC "Emergency Permit" (35 Ill. Adm. Code 703.221
and 704.163). "Permit" does not include RCRA interim status (35 Ill. Adm. Code 703.153
through 703.157), UIC authorization by rule (35 Ill. Adm. Code 704.Subpart C), or any permit
that has not yet been the subject of final Agency action, such as a "Draft Permit" or a
"Proposed Permit.".
71
"Person" means any individual, partnership, co-partnership, firm, company, corporation,
association, joint stock company, trust, estate, political subdivision, state agency, or any other
legal entity, or their legal representative, agency, or assigns.
"Phase I" (RCRA) means, as used in the corresponding federal regulations, the period of time
commencing May 19, 1980. For Illinois purposes, Phase I began on May 17, 1982.
"Phase II" (RCRA) means, as used in the corresponding federal regulations, the period of time
commencing May 19, 1980. For Illinois purposes, Phase II commenced when U.S. EPA
granted final authorization to the Agency to issue RCRA permits for any class of facility or
unit. This occurred on January 31, 1986.
"Physical construction" (RCRA) means excavation, movement of earth, erection of forms or
structures or similar activity to prepare an "HWM facility" to accept "hazardous waste".
"Plugging" (UIC) means the act or process of stopping the flow of water, oil, or gas into or out
of a formation through a borehole or well penetrating that formation.
"POTW" means "publicly owned treatment works".
"Project" (UIC) means a group of wells in a single operation.
"Publicly owned treatment works" ("POTW") is as defined in 35 Ill. Adm. Code 310.
"Radioactive waste" (UIC) means any waste that contains radioactive material in
concentrations that exceed those listed in 10 CFR 20, Appendix B, Table II, Column 2,
incorporated by reference in 35 Ill. Adm. Code 720.111.
"RCRA" means the Solid Waste Disposal Act as amended by the Resource Conservation and
Recovery Act of 1976 (P.L. 94-580, as amended by P.L. 95-609, P.L. 96-510, 42 U.S.C. 6901
et seq. (1992)). For the purposes of regulation under 35 Ill. Adm. Code 700 through 705, 720
through 728, and 739, "RCRA" refers only to RCRA Subtitle C. This does not include the
RCRA Subtitle D (municipal solid waste landfill) regulations, found in 35 Ill. Adm. Code 810
through 815, and the RCRA Subtitle I (underground storage tank) regulations found in 35 Ill.
Adm. Code 731 and 732.
"RCRA permit" means a permit required under Section 21(f) of the Environmental Protection
Act.
"Regional Administrator" means the Regional Administrator for the EPA Region in which the
facility is located or the Regional Administrator's designee.
"Schedule of compliance" means a schedule of remedial measures included in a "permit",
including an enforceable sequence of interim requirements (for example, actions, operations,
or milestone events) leading to compliance with the "appropriate Act and regulations".
"SDWA" means the Safe Drinking Water Act (P.L. 93-523, as amended, 42 U.S.C. 300f et
seq. (1992)).
"Site" means the land or water area where any "facility or activity" is physically located or
conducted, including adjacent land used in connection with the facility or activity.
72
"SIC Code" means codes pursuant to the Standard Industrial Classification Manual
incorporated by reference in 35 Ill. Adm. Code 720.111.
"State" means the State of Illinois.
"State Director" means the Director of the Illinois Environmental Protection Agency.
"State/EPA Agreement" means an agreement between the Regional Administrator and the State
that coordinates EPA and State activities, responsibilities, and programs including those under
the RCRA and SDWA.
"Storage" (RCRA) means the holding of "hazardous waste" for a temporary period, at the end
of which the hazardous waste is treated, disposed, or stored elsewhere.
"Stratum (plural strata)" (UIC) means a single sedimentary bed or layer, regardless of
thickness, that consists of generally the same kind of rock material.
"Total dissolved solids" (UIC) means the total dissolved (filterable) solids as determined by use
of the method specified in 40 CFR 136, incorporated by reference in 35 Ill. Adm. Code
720.111.
"Transfer facility" means any transportation related facility including loading docks, parking
areas, storage areas, and other similar areas where shipments of hazardous wastes are held
during the normal course of transportation.
"Transferee" (UIC) means the owner or operator receiving ownership or operational control of
the well.
"Transferor" (UIC) means the owner or operator transferring ownership or operational control
of the well.
"Transporter" (RCRA) means a person engaged in the off-site transportation of "hazardous
waste" by air, rail, highway, or water.
"Treatment" (RCRA) means any method, technique, process, including neutralization,
designed to change the physical, chemical, or biological character or composition of any
"hazardous waste" so as to neutralize such wastes, or so as to recover energy or material
resources from the waste, or so as to render such wastes non-hazardous, or less hazardous;
safer to transport, store, or dispose of; or amenable for recovery, amenable for storage, or
reduced in volume.
"UIC" means the Underground Injection Control program.
"Underground Injection" (UIC) means a "well injection".
"Underground source of drinking water" ("USDW") (RCRA and UIC) means an "aquifer" or
its portion:
Which:
73
Supplies any public water system; or
Contains a sufficient quantity of groundwater to supply a public water system;
and
Currently supplies drinking water for human consumption; or
Contains less than 10,000 mg/1 total dissolved solids; and
That is not an "exempted aquifer".
"USDW" (RCRA and UIC) means an "underground source of drinking water".
"Wastewater treatment unit" means a device which:
Is part of a wastewater treatment facility that is subject to regulation under 35 Ill.
Adm. Code 309.Subpart A or 310; and
Receives and treats or stores an influent wastewater that is a hazardous waste as
defined in 35 Ill. Adm. Code 721.103, or generates and accumulates a wastewater
treatment sludge that is a hazardous waste as defined in 35 Ill. Adm. Code 721.103, or
treats or stores a wastewater treatment sludge that is a hazardous waste as defined in
35 Ill. Adm. Code 721.103,; and
Meets the definition of tank or tank system in 35 Ill. Adm. Code 720.110.
"Well" (UIC) means a bored, drilled, or driven shaft, or a dug hole, whose depth is greater
than the largest surface dimension.
"Well injection" (UIC) 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.
BOARD NOTE: Derived from 40 CFR 144.3 (1994), as amended at 58 Fed. Reg. 63895
(Dec. 3, 1993), and 270.2 (19924), as amended at 5860 Fed. Reg. 868533914 (Feb. 16,
1993June 29, 1995).
(Source: Amended at 20 Ill. Reg. ________, effective ________________________)
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
74
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
SUBPART D: APPLICATIONS
Section
703.180 Applications in General
703.181 Contents of Part A
703.182 Contents of Part B
703.183 General Information
703.184 Facility Location Information
703.185 Groundwater Protection Information
703.186 Exposure Information
703.187 Solid Waste Management Units
703.188 Other Information
703.200 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
75
703.210 Process Vents
703.211 Equipment
703.212 Drip Pads
703.213 Air Emission Controls for Tanks, Surface Impoundments, and Containers
SUBPART E: SHORT TERM AND PHASED PERMITS
Section
703.221 Emergency Permits
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
SUBPART F: PERMIT CONDITIONS OR DENIAL
Section
703.240 Permit Denial
703.241 Establishing Permit Conditions
703.242 Noncompliance Pursuant to Emergency Permit
703.243 Monitoring
703.244 Notice of Planned Changes (Repealed)
703.245 Twenty-four Hour Reporting
703.246 Reporting Requirements
703.247 Anticipated Noncompliance
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
703.Appendix A Classification of Permit Modifications
AUTHORITY: Implementing Section 22.4 and authorized by Section 27 of the Environmental Protection Act
[415 ILCS 5/22.4 and 27].
SOURCE: Adopted in R82-19, 53 PCB 131, 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,
76
1988; amended in R87-39 at 12 Ill. Reg. 13069, effective July 29, 1988; amended in R88-16 at 13 Ill. Reg. 447,
effective December 27, 1988; amended in R89-1 at 13 Ill. Reg. 18477, effective November 13, 1989; amended
in R89-9 at 14 Ill. Reg. 6278, effective April 16, 1990; amended in R90-2 at 14 Ill. Reg. 14492, effective
August 22, 1990; amended in R90-11 at 15 Ill. Reg. 9616, effective June 17, 1991; amended in R91-1 at 15 Ill.
Reg. 14554, effective September 30, 1991; amended in R91-13 at 16 Ill Reg. 9767, effective June 9, 1992;
amended in R92-10 at 17 Ill. Reg. 5774, effective March 26, 1993; amended in R93-4 at 17 Ill. Reg. 20794,
effective November 22, 1993; amended in R93-16 at 18 Ill. Reg. 6898, effective April 26, 1994; amended in
R94-7 at 18 Ill. Reg. 12392, effective July 29, 1994; amended in R94-5 at 18 Ill. Reg. 18316, effective
December 20, 1994; amended in R95-6 at 19 Ill. Reg. 9920, effective June 27, 1995; amended in R95-20 at 20
Ill. Reg. ________, effective _____________________.
SUBPART B: PROHIBITIONS
Section 703.123
Specific Exclusions from Permit Program
The following persons are among those who are not required to obtain a RCRA permit:
a)
Generators who accumulate hazardous waste on-site for less than the time periods provided in
35 Ill. Adm. Code 722.134;
b)
Farmers who dispose of hazardous waste pesticides from their own use as provided in 35 Ill.
Adm. Code 722.170;
c)
Persons who 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;
fe)
Owners and operators of elementary neutralization units or wastewater treatment units as
defined in 35 Ill. Adm. Code 720.110;
gf)
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;
hg)
Persons adding absorbent material to waste in a container (as defined in 35 Ill. 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; and
77
3)
Thermostats, as described in 35 Ill. Adm. Code 733.104.
(Board NoteBOARD NOTE: SeeDerived from 40 CFR 270.1(c)(2) (1994), as
amended at 5360 Fed. Reg. 2716525542, July 19, 1988May 11, 1995.)
(Source: Amended at 20 Ill. Reg. ________, effective ______________________)
SUBPART C: AUTHORIZATION BY RULE AND INTERIM STATUS
Section 703.150
Application by Existing HWM Facilities and Interim Status Qualifications
a)
The owner or operator of an existing HWM facility or of an HWM facility in existence on the
effective date of statutory or regulatory amendments that render the facility subject to the
requirement to have a RCRA permit must submit Part A of the permit application to the
Agency no later than the following times, whichever comes first:
1)
Six months after the date of publication of regulations which first require the owner or
operator to comply with standards in 35 Ill. Adm. Code 725 or 726; or
2)
Thirty days after the date the owner or operator first becomes subject to the standards
in 35 Ill. Adm. Code 725 or 726; or
3)
For generators which generate greater than 100 kilograms but less than 1000
kilograms of hazardous waste in a calendar month and treat, store or dispose of these
wastes on-site, by March 24, 1987.
BOARD NOTE: Derived from 40 CFR 270.10(e)(1) and 270.1(b) (19914), amended
at 56 Fed. Reg. 32688, July 17, 1991.
b)
In granting a variance under subsection (c), below, the Board will consider whether there has
been substantial confusion as to whether the owner or operator of such facilities were required
to file a Part A application and whether such confusion was attributable to ambiguities in 35 Ill.
Adm. Code 720, 721 or 725.
BOARD NOTE: Derived from 40 CFR 270.10(e)(2) (19904).
c)
The time for filing Part A of the permit application may be extended only by a Board Order
entered pursuant to a variance petition.
BOARD NOTE: Derived from 40 CFR 270.10(e)(3) (19904).
d)
The owner or operator of an existing HWM facility may be required to submit Part B of the
permit application at any time after the effective date of standards in 35 Ill. Adm. Code 724
applicable to any TSD unit at the facility. The Agency will notify the owner or operator that a
Part B application is required, and set a date for receipt of the application, not less than six
months after the date the notice is sent. The owner or operator my voluntarily submit a Part B
application for all or part of the HWM facility at any time. Notwithstanding the above, any
owner or operator of an existing HWM facility must submit a Part B permit application in
accordance with the dates specified in Section 703.157. Any owner or operator of a land
disposal facility in existence on the effective date of statutory or regulatory amendments which
78
render the facility subject to the requirement to have a RCRA permit must submit a Part B
application in accordance with the dates specified in Section 703.157.
BOARD NOTE: Derived from 40 CFR 270.10(e)(4) (19904), as amended at 60 Fed. Reg.
33914 (June 29, 1995).
e)
Interim status may be terminated as provided in Section 703.157.
BOARD NOTE: Derived from 40 CFR 270.10(e)(5) (19904).
(Source: Amended at 20 Ill. Reg. ________, effective ______________________)
Section 703.151
Application by New HWM Facilities
a)
Except as provided in subsection (c), no person shall begin physical construction of a new
HWM facility without having submitted Part A and Part B of the permit application and having
received a finally effective RCRA permit;
b)
An application for a permit for a new HWM facility (including both Part A and Part B) may be
filed at any time after promulgation of standards in 35 Ill. Adm. Code 724 applicable to any
TSD unit in the facility; Except as provided in subsection (c), all applications must be
submitted to the Agency at least 180 days before physical construction is expected to
commence;
c)
Notwithstanding subsection (a), a person may construct a facility for the incineration of
polychlorinated biphenyls pursuant to an approval issued by the Administrator of USEPA under
Section (6)(e) of the Toxic Substances Control Act (42 U.S.C. 9601 et seq.) and any person
owning or operating such facility may, at any time after construction of operation of such
facility has begun, file an application for a RCRA permit to incinerate hazardous waste
authorizing such facility to incinerate waste identified or listed under 35 Ill. Adm. Code 721.
d)
Such persons may continue physical construction of the HWM facility after the effective date
of the standards applicable to it if the person submits Part B of the permit application on or
before the effective date of such standards (or on some later date specified by the Agency.)
Such person must not operate the HWM facility without having received a finally effective
RCRA permit.
(Board NoteBOARD NOTE: SeeDerived from 40 CFR 270.10(f) (1994), as amended at 60
Fed. Reg. 33914 (June 29, 1995).)
(Source: Amended at 20 Ill. Reg. ________, effective ______________________)
Section 703.152
Amended Part A Application
a)
If any owner or operator of an HWM facility has filed Part A of a permit application and has
not yet filed Part B, the owner or operator shall file an amended Part A application with the
Agency:
1)
No later than the effective date of revised regulations under 35 Ill. Adm. Code 721
listing or identifying additional hazardous wastes, if the facility is treating, storing or
disposing of any of those newly listed or identified wastes;
79
2)
As necessary to comply with provisions of Section 703.155 for changes during interim
status;.
b)
The owner or operator of a facility who fails to comply with the updating requirements of
paragraphsubsection (a) does not receive interim status as to the wastes not covered by duly
filed Part A applications.
(Board NoteBOARD NOTE: SeeDerived from 40 CFR 270.10(g) (1994), as amended at 60
Fed. Reg. 33914 (June 29, 1995).)
(Source: Amended at 20 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
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 Section 22.4 and authorized by Section 27 of the Environmental Protection Act
[415 ILCS 5/22.4 and 27].
80
SOURCE: Adopted in R81-22, 43 PCB 427, at 5 Ill. Reg. 9781, effective May 17, 1982; amended and codified
in R81-22, 45 PCB 317, 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, 53 PCB 131 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. ________, _______________________.
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" 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 U.S.C. 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. 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), between hazardous
81
waste storage and treatment tanks to a point of disposal onsite, or to a point of shipment for
disposal off-site.
"Aquifer" means a geologic formation, group of formations or part of a formation capable of
yielding a significant amount of groundwater to wells or springs.
"Authorized representative" means the person responsible for the overall operation of a facility
or an operational unit (i.e., part of a facility), e.g., the plant manager, superintendent or person
of equivalent responsibility.
"Battery" means a device consisting of one or more electrically connected electrochemical cells
that is designed to receive, store, and deliver electric energy. An electrochemical cell is a
system consisting of an anode, cathode, and an electrolyte, plus such connections (electrical
and mechanical) as may be needed to allow the cell to deliver or receive electrical energy. The
term battery also includes an intact, unbroken battery from which the electrolyte has been
removed.
"Board" means the Illinois Pollution Control Board.
"Boiler" means an enclosed device using controlled flame combustion and having the following
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) must be of integral design. To be of integral
design, the combustion chamber and the primary energy recovery Section(s) (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) 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 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
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.
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"Certification" means a statement of professional opinion based upon knowledge and belief.
"Closed Portion" means that portion of a facility which 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 could threaten human health or the environment.
"Corrective action management unit" or "CAMU" means an area within a facility that is
designated by the Agency under 35 Ill. Adm. Code 724.Subpart S for the purpose of
implementing corrective action requirements under 35 Ill. Adm. Code 724.201 and RCRA
section 3008(h). A CAMU shall only be used for the management of remediation wastes
pursuant to implementing such corrective action requirements at the facility.
BOARD NOTE: U.S. EPA must also designate a CAMU until it grants this authority to the
Agency. See the note following 35 Ill. Adm. Code 724.652.
"Corrosion expert" means a person who, by reason of knowledge of the physical sciences and
the principles of engineering and mathematics, acquired by a professional education and related
practical experience, is qualified to engage in the practice of corrosion control on buried or
submerged metal piping systems and metal tanks. Such a person must be certified as being
qualified by the National Association of Corrosion Engineers (NACE) or be a registered
professional engineer who has certification or licensing that includes education and experience
in corrosion control on buried or submerged metal piping systems and metal tanks.
"Designated facility" means a hazardous waste treatment, storage or disposal facility,
Which:
Has received a RCRA permit (or interim status) pursuant to 35 Ill. Adm.
Code 702, 703 and 705;
Has received a RCRA permit from U.S. EPA pursuant to 40 CFR 124 and
270 (1992);
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Has received a RCRA permit from a state authorized by U.S. EPA pursuant
to 40 CFR 271 (1992); or
Is regulated under 35 Ill. Adm. Code 721.106(c)(2) or 266.Subpart F; and
Which 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 has been
authorized by U.S. EPA 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.
"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 run-on to an associated collection system at
wood preserving plants.
"Elementary neutralization unit" means a device which:
Is used for neutralizing wastes which are hazardous only because they exhibit the
corrosivity characteristic defined in 35 Ill. Adm. Code 721.122 or are listed in 35 Ill.
Adm. Code 721.Subpart D only for this reason; and
Meets the definition of tank, tank system, container, transport vehicle or vessel in this
Section.
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"EPA" or "U.S. EPA" or "USEPA" means United States Environmental Protection Agency.
"EPA hazardous waste number" or "U.S. EPA hazardous waste number" or "USEPA
hazardous waste number" means the number assigned by EPA to each hazardous waste listed in
35 Ill. Adm. Code 721.Subpart D and to each characteristic identified in 35 Ill. Adm. Code
721.Subpart C.
"EPA identification number" or "U.S. EPA identification number" or "USEPA identification
number" means the number assigned by U.S. EPA pursuant to 35 Ill. Adm. Code 722 through
725 to each generator, transporter and treatment, storage or disposal facility.
"EPA 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 was in operation or for which construction commenced on or before November 19,
1980. A facility had commenced construction if the owner or operator had obtained the
federal, state and local approvals or permits necessary to begin physical construction and
either:
A continuous on-site, physical construction program had begun or
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The owner or operator had entered into contractual obligations -- which could not be
cancelled 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 that is in operation, or for which
installation has 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
A continuous on-site physical construction or installation program has begun; or
The owner or operator has entered into contractual obligations -- which 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.
"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 3008(h).
"Final closure" means the closure of all hazardous waste management units at the facility in
accordance with all applicable closure requirements so that hazardous waste management
activities under 35 Ill. Adm. Code 724 and 725 are no longer conducted at the facility unless
subject to the provisions of 35 Ill. Adm. Code 722.134.
"Federal agency" means any department, agency or other instrumentality of the federal
government, any independent agency or establishment of the federal government including any
government corporation and the Government Printing Office.
"Federal, state, and local approvals or permits necessary to begin physical construction" means
permits and approvals required under federal, state, or local hazardous waste control statutes,
regulations or ordinances.
"Final closure" means the closure of all hazardous waste management units at the facility in
accordance with all applicable closure requirements so that hazardous waste management
activities under 35 Ill. Adm. Code 724 and 725 are no longer conducted at the facility unless
subject to the provisions of 35 Ill. Adm. Code 722.134.
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"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 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 caused the hazardous waste to be
listed in 35 Ill. Adm. Code 721.Subpart D, or a constituent listed in of 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:
Uses controlled flame combustion and neither:
Meets the criteria for classification as a boiler, sludge dryer or carbon
regeneration unit, nor
Is listed as an industrial furnace; or
Meets the definition of infrared incinerator or plasma arc incinerator.
"Incompatible waste" means a hazardous waste which is suitable 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.
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(See 35 Ill. Adm. Code 725.Appendix E for examples.)
"Industrial furnace" means any of the following enclosed devices that are integral components
of manufacturing processes and that use thermal treatment to accomplish recovery of materials
or energy:
Cement kilns
Lime kilns
Aggregate kilns
Phosphate kilns
Coke ovens
Blast furnaces
Smelting, melting and refining furnaces (including pyrometallurgical devices such as
cupolas, reverberator furnaces, sintering machines, roasters and foundry furnaces)
Titanium dioxide chloride process oxidation reactors
Methane reforming furnaces
Pulping liquor recovery furnaces
Combustion devices used in the recovery of sulfur values from spent sulfuric acid
Halogen acid furnaces (HAFs) for the production of acid from halogenated hazardous
waste generated by chemical production facilities where the furnace is located on the
site of a chemical production facility, the acid product has a halogen acid content of at
least 3%, 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%, as generated.
Any other such device as the Agency determines to be an "Industrial Furnace" on the
basis of one or more of the following factors:
The design and use of the device primarily to accomplish recovery of material
products;
The use of the device to burn or reduce raw materials to make a material
product;
The use of the device to burn or reduce secondary materials as effective
substitutes for raw materials, in processes using raw materials as principal
feedstocks;
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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 uses electric powered resistance
heaters as a source of radiant heat followed by an afterburner using controlled flame
combustion and which is not listed as an industrial furnace.
"Inground tank" means a device meeting the definition of "tank" whereby a portion of the tank
wall is situated to any degree within the ground, thereby preventing visual inspection of that
external surface area of the tank that is in the ground.
"In operation" refers to a facility which 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
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.
"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 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.
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"Leachate" means any liquid, including any suspended components in the liquid, that has
percolated through or drained from hazardous waste.
"Liner" means a continuous layer of natural or manmade materials beneath or on the sides of a
surface impoundment, landfill or landfill cell, which 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 contains
the information required by 35 Ill. Adm. Code 722.Subpart B.
"Manifest document number" means the U.S. EPA 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.
"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 which is not a container, tank, tank system, 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), or a unit eligible for a
research, development and demonstration permit under 35 Ill. Adm. Code 703.231.
"Movement" means that hazardous waste transported to a facility in an individual vehicle.
"New hazardous waste management facility" or "new facility" means a facility which 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 after July 14,
1986. (See also "existing tank system".")
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"Onground tank" means a device meeting the definition of "tank" that is situated in such a way
that the bottom of the tank is on the same level as the adjacent surrounding surfaces so that the
external tank bottom cannot be visually inspected.
"On-site" means the same or geographically contiguous property which may be divided by
public or private right-of-way, provided the entrance and exit between the properties is at a
crossroads intersection and access is by crossing as opposed to going along the right-of-way.
Noncontiguous properties owned by the same person but connected by a right-of-way which he
controls and to which the public does not have access is also considered on-site property.
"Open burning" means the combustion of any material without the following characteristics:
Control of combustion air to maintain adequate temperature for efficient combustion;
Containment of the combustion reaction in an enclosed device to provide sufficient
residence time and mixing for complete combustion; and
Control of emission of the gaseous combustion products.
(See also "incineration" and "thermal treatment".)
"Operator" means the person responsible for the overall operation of a facility.
"Owner" means the person who 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
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 U.S.C. § 321(v)), incorporated by reference in Section 720.111,
It is an animal drug that has been determined by regulation of the federal Secretary of
Health and Human Services pursuant to FFDCA Section 512, incorporated by
reference in Section 720.111, to be an exempted new animal drug, or
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It is an animal feed under FFDCA Section 201(w) (21 U.S.C. § 321(w)), incorporated
by reference in Section 720.111 that bears or contains any substances described in
either of the two preceding subsections 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 U.S.C. § 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 uses a high intensity electrical
discharge or arc as a source of heat followed by an afterburner using controlled flame
combustion and which is not listed as an industrial furnace.
"Point source" means any discernible, confined and discrete conveyance including, but not
limited to, any pipe, ditch, channel, tunnel, conduit, well, discrete fissure, container, rolling
stock, concentrated animal feeding operation or vessel or other floating craft from which
pollutants are or may be discharged. This term does not include return flows from irrigated
agriculture.
"Publicly owned treatment works" or "POTW" is as defined in 35 Ill. Adm. Code 310.110.
"Qualified groundwater scientist" means a scientist or engineer who has received a
baccalaureate or postgraduate degree in the natural sciences or engineering, and has sufficient
training and experience in groundwater hydrology and related fields, as demonstrated by state
registration, professional certifications or completion of accredited university courses that
enable the individual to make sound professional judgments regarding groundwater monitoring
and contaminant fate 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 Ill. Rev.
Stat. 1991, ch. 111, par. 5201 [225 ILCS 325/1] and 68 Ill. Adm. Code 1380. "Professional
certification" includes, but is not limited to, certification under the certified ground water
professional program of the National Ground Water Association.
"Regional Administrator" means the Regional Administrator for the EPA 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 are managed for the
purpose of implementing corrective action requirements under 35 Ill. Adm. Code 724.201 and
RCRA Section 3008(h). For a given facility, remediation wastes may originate only from
within the facility boundary, but may include waste managed in implementing RCRA sections
3004(v) or 3008(h) for releases beyond the facility boundary.
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"Representative sample" means a sample of a universe or whole (e.g., waste pile, lagoon,
groundwater) which can be expected to exhibit the average properties of the universe or whole.
"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 U.S. EPA or the Agency.
"Representative sample" means a sample of a universe or whole (e.g., waste pile, lagoon,
groundwater) which 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 Code as defined in Standard Industrial Classification
Manual, incorporated by reference in Section 720.111.
"Sludge" means any solid, semi-solid or liquid waste generated from a municipal, commercial
or industrial wastewater treatment plant, water supply treatment plant or air pollution control
facility exclusive of the treated effluent from a wastewater treatment plant.
"Sludge dryer" means any enclosed thermal treatment device which 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" means a generator which 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.
"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.
"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.
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"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.
"Surface impoundment" or "impoundment" means a facility or part of a facility which is a
natural topographic depression, manmade excavation or diked area formed primarily of earthen
materials (although it may be lined with manmade materials) which is designed to hold an
accumulation of liquid wastes or wastes containing free liquids and which is not an injection
well. Examples of surface impoundments are holding, storage, settling and aeration pits,
ponds and lagoons.
"Tank" means a stationary device, designed to contain an accumulation of hazardous waste
which 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.
"Thermal treatment" means the treatment of hazardous waste in a device which 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 is directly connected to an industrial production process and which is constructed and
operated in a manner which prevents the release of any hazardous waste or any constituent
thereof into the environment during treatment. An example is a pipe in which waste acid is
neutralized.
"Transfer facility" means any transportation related facility including loading docks, parking
areas, storage areas and other similar areas where shipments of hazardous waste are held
during the normal course of transportation.
"Transport vehicle" means a motor vehicle or rail car used for the transportation of cargo by
any mode. Each cargo-carrying body (trailer, railroad freight car, etc.) is a separate transport
vehicle.
"Transportation" means the movement of hazardous waste by air, rail, highway or water.
"Transporter" means a person engaged in the off-site transportation of hazardous waste by air,
rail, highway or water.
"Treatability study" means:
A study in which a hazardous waste is subjected to a treatment process to determine:
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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. Or,
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 waste, or so as to recover energy or material resources from the waste or
so as to render such waste non-hazardous or less hazardous; safer to transport, store or dispose
of; or amenable for recovery, amenable for storage or reduced in volume.
"Treatment zone" means a soil area of the unsaturated zone of a land treatment unit within
which hazardous constituents are degraded, transformed or immobilized.
"Underground injection" means the subsurface emplacement of fluids through a bored, drilled
or driven well; or through a dug well, where the depth of the dug well is greater than the
largest surface dimension. (See also "injection well".)
"Underground tank" means a device meeting the definition of "tank" whose entire surface area
is totally below the surface of and covered by the ground.
"Unfit-for-use tank system" means a tank system that has been determined through an integrity
assessment or other inspection to be no longer capable of storing or treating hazardous waste
without posing a threat of release of hazardous waste to the environment.
"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.
"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; and
95
Thermostats, as described in 35 Ill. Adm. Code 733.104.
"Universal waste handler" means either of the following:
A generator (as defined in this Section) of universal waste; or
The owner or operator of a facility, including all contiguous property, that receives
universal waste from other universal waste handlers, accumulates the universal waste,
and sends that universal waste to another universal waste handler, to a destination
facility, or to a foreign destination.
"Universal waste handler" does not mean:
A person that treats (except under the provisions of Section 733.113(a) or (c)
or 733.133(a) or (c)), disposes of, or recycles universal waste; or
A person engaged in the off-site transportation of universal waste by air, rail,
highway, or water, including a universal waste transfer facility.
"Universal waste transporter" means a person engaged in the off-site transportation of universal
waste by air, rail, highway, or water.
"Unsaturated zone" or "zone of aeration" means the zone between the land surface and the
water table.
"Uppermost aquifer" means the geologic formation nearest the natural ground surface that is an
aquifer, as well as lower aquifers that are hydraulically interconnected with this aquifer within
the facility's property boundary.
"USDOT" or "Department of Transportation" means the United States Department of
Transportation.
"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 which:
Is part of a wastewater treatment facility which 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 and treats or stores an influent wastewater which 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,
96
or treats or stores a wastewater treatment sludge which is a hazardous waste as defined
in 35 Ill. Adm. Code 721.103; and
Meets the definition of tank or tank system in this Section.
"Water (bulk shipment)" means the bulk transportation of hazardous waste which is loaded or
carried on board a vessel without containers or labels.
"Well" means any shaft or pit dug or bored into the earth, generally of a cylindrical form, and
often walled with bricks or tubing to prevent the earth from caving in.
"Well injection" (See "underground injection").
"Zone of engineering control" means an area under the control of the owner or operator that,
upon detection of a hazardous waste release, can be readily cleaned up prior to the release of
hazardous waste or hazardous constituents to groundwater or surface water.
(Source: Amended at 20 Ill. Reg. ________, effective ______________________)
Section 720.111 References
a)
The following publications are incorporated by reference:
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
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.
API. Available from the American Petroleum Institute, 1220 L Street, N.W.,
Washington, D.C. 20005, 202-682-8000:
"Cathodic Protection of Underground Petroleum Storage Tanks and Piping
Systems", API Recommended Practice 1632, Second Edition, December,
1987.
"Evaporative Loss from External Floating-Roof Tanks", API Publication
2517, Third Edition, February, 1989.
"Guide for Inspection of Refinery Equipment, Chapter XIII, Atmospheric and
Low Pressure Storage Tanks"," 4th Edition, 1981, reaffirmed December,
1987.
"Installation of Underground Petroleum Storage Systems"," API
Recommended Practice 1615, Fourth Edition, November, 1987.
97
APTI. Available from the Air and Waste Management Association, Box 2861,
Pittsburgh, PA 15230, 412-232-3444:
APTI Course 415: Control of Gaseous Emissions, U.S. EPA 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 of
Hydrocarbon Fuels by Bomb Calorimeter (High Precision Method), approved
October 31, 1988.
ASTM D 2879-86, Standard Test Method for Vapor Pressure-Temperature
Relationship and Initial Decomposition Temperature of Liquids by
Isoteniscope, approved October 31, 1986.
ASTM D 2879-92, Standard Test Method for Vapor Pressure-Temperature
Relationship and Initial Decomposition Temperature of Liquids by
Isoteniscope, approved 1992.
98
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 E 926-88 C, Standard Test Methods for Preparing Refuse-Derived
Fuel (RDF) Samples for Analysis of Metals, Bomb-Acid Digestion Method,
approved March 25, 1988.
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.
GPO. Available from the Superintendent of Documents, U.S. Government Printing
Office, Washington, D.C. 20402, 202-783-3238:
Standard Industrial Classification Manual (1972), and 1977 Supplement,
republished in 1983
"Test Methods for Evaluating Solid Waste, Physical/Chemical Methods","
U.S. EPA Publication number SW-846 (Third Edition, November, 1986), as
amended by Updates I (July, 1992), II (September, 1994), and IIA (August,
1993), and IIB (January, 1995) (Document Number 955-001-00000-1)
(contact U.S. EPA, Office of Solid Waste, or MICE, as indicated below, for
Update IIA).
MICE. Available from Methods Information Communication Service, at 703-821-
4789:
"Test Methods for Evaluating Solid Waste, Physical/Chemical Methods","
U.S. EPA Publication number SW-846 (Third Edition, November, 1986),
Update IIA (Document Number 955-001-00000-1) (contact GPO, as indicated
above, for SW-846 and Update I).
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 RP0285-
85, approved March, 1985.
99
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, 703-487-4600:
"Generic Quality Assurance Project Plan for Land Disposal Restrictions
Program", EPA/530-SW-87-011, March 15, 1987. (Document number PB
88-170766.)
"Guidance on Air Quality Models", Revised 1986. (Document number PB86-
245-248 (Guideline) and PB88-150-958 (Supplement)).
"Methods for Chemical Analysis of Water and Wastes", Third Edition,
March, 1983. (Document number PB 84-128677).
"Methods Manual for Compliance with BIF Regulations", December, 1990.
(Document number PB91-120-006).
"Petitions to Delist Hazardous Wastes -- A Guidance Manual", EPA/530-SW-
85-003, April, 1985. (Document Number PB 85-194488).
"Procedures Manual for Ground Water Monitoring at Solid Waste Disposal
Facilities", EPA-530/SW-611, 1977. (Document number PB 84-174820).
"Screening Procedures for Estimating the Air Quality Impact of Stationary
Sources", October, 1992, Publication Number EPA-450/R-92-019.
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. EPA. 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.
U.S. EPA. Available from U.S. EPA, Office of Solid Waste (Mail Code 5304), 401
M Street SW, Washington, D.C. 20460:
"Test Methods for Evaluating Solid Waste, Physical/Chemical Methods,"
U.S. EPA Publication number SW-846 (Third Edition, November, 1986),
Update IIA (Document Number 955-001-00000-1) (contact GPO, as indicated
above, for SW-846 and Update I).
100
U.S. EPA. Available from U.S. EPA, Number F-90-WPWF-FFFFF, Room M2427,
401 M Street SW, Washington, D.C. 20460, 202-475-9327:
"Test Method 8290: Procedures for the Detection and Measurement of
PCDDs and PCDFs", EPA/530-SW-91-019 (January, 1991)
U.S. EPA. Available from Receptor Analysis Branch, U.S. EPA (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.
b)
Code of Federal Regulations. Available from the Superintendent of Documents, U.S.
Government Printing Office, Washington, D.C. 20401, 202-783-3238:
10 CFR 20, Appendix B (1994)
40 CFR 51.100(ii) (1994)
40 CFR 51, Subpart W (1994)
40 CFR 60 (1994), as amended at 59 Fed. Reg. 62924 (Dec. 6, 1994)
40 CFR 61, Subpart V (1994)
40 CFR 136 (1994), as amended at 60 Fed. Reg. 17160 (Apr. 4, 1995)
40 CFR 142 (1994)
40 CFR 220 (1994)
40 CFR 260.20 (1994)
40 CFR 264 (1994)
40 CFR 268.Appendix IX (1994)
40 CFR 302.4, 302.5 and 302.6 (1994)
40 CFR 761 (1994)
49 CFR 171 (1995)
49 CFR 173 (1995)
49 CFR 178 (1994)
c)
Federal Statutes
Section 3004 of the Resource Conservation and Recovery Act (42 U.S.C. 6901 et seq.), as
amended through December 31, 1987.
101
Sections 201(v), 201(w), and 360b(j) of the Federal Food, Drug, and Cosmetic Act (FFDCA;
21 U.S.C. §§ 321(v), 321(w) & 512(j)), as amended through October 25, 1994.
d)
This Section incorporates no later editions or amendments.
(Source: Amended at 20 Ill. Reg. ________, effective ______________________)
SUBPART C: RULEMAKING PETITIONS AND OTHER PROCEDURES
Section 720.120
Rulemaking
a)
Any person may petition the Board to adopt as State regulations rules whichthat are identical in
substance with newly-adopted federal amendments or regulations. The petition shall take the
form of a proposal for rulemaking pursuant to 35 Ill. Adm. Code 102. The proposal shall
include a listing of all amendments to 40 CFR 260 through 266, and 268, or 273 whichthat
have been made since the last preceding amendment or proposal to amend 35 Ill. Adm. Code
720 through 726, and 268728, or 733, pursuant to Section 22.4(a) of the Environmental
Protection Act.
b)
Any person may petition the Board to adopt amendments or additional regulations not identical
in substance with federal regulations. Such proposal shall conform to 35 Ill. Adm. Code 102
and Title VII and Section 22.4(b) or 22.4(c) of the Environmental Protection Act.
(Source: Amended at 20 Ill. Reg. ________, effective ______________________)
Section 720.123 Petitions for Regulation as Universal Waste
a)
Any person seeking to add a hazardous waste or a category of hazardous waste to the universal
waste regulations of 35 Ill. Adm. Code 733 may petition for a regulatory amendment under this
Section, Section 720.120, and 35 Ill. Adm. Code 733.Subpart G.
b) Petition and Demonstration.
1)
To be successful, the petitioner must demonstrate each of the following:
A)
That regulation under the universal waste regulations of 35 Ill. Adm. Code
733 is appropriate for the waste or category of waste;
B)
That regulation under 35 Ill. Adm. Code 733 will improve management
practices for the waste or category of waste; and
C)
That regulation under 35 Ill. Adm. Code 733 will improve implementation of
the hazardous waste program.
2)
The petition must include the information required by Section 720.120(b). The
petition should also address as many of the factors listed in 35 Ill. Adm. Code 733.181
as are appropriate for the waste or category of waste addressed in the petition.
102
c)
The Board will grant or deny a petition using the factors listed in 35 Ill. Adm. Code 733.181.
The decision will be based on the weight of evidence that shows the following with regard to
regulation under 35 Ill. Adm. Code 733:
1)
That it is appropriate for the waste or category of waste,
2)
That it will improve management practices for the waste or category of waste, and
3)
That it will improve implementation of the hazardous waste program.
d)
The Board may request additional information to that set forth in 35 Ill. Adm. Code 733.181,
as needed to evaluate the merits of the petition.
(Source: Added at 20 Ill. Reg. ________, _______________________)
TITLE 35: ENVIRONMENTAL PROTECTION
SUBTITLE G: WASTE DISPOSAL
CHAPTER I: POLLUTION CONTROL BOARD
SUBCHAPTER c: HAZARDOUS WASTE OPERATING REQUIREMENTS
PART 721
IDENTIFICATION AND LISTING OF HAZARDOUS WASTE
SUBPART A: GENERAL PROVISIONS
Section
721.101 Purpose and Scope
721.102 Definition of Solid Waste
721.103 Definition of Hazardous Waste
721.104 Exclusions
721.105 Special Requirements for Hazardous Waste Generated by Small Quantity Generators
721.106 Requirements for Recyclable Materials
721.107 Residues of Hazardous Waste in Empty Containers
721.108 PCB Wastes Regulated under TSCA
721.109
Requirements for Universal Waste
SUBPART B: CRITERIA FOR IDENTIFYING THE CHARACTERISTICS
OF HAZARDOUS WASTE AND FOR LISTING HAZARDOUS WASTES
Section
721.110 Criteria for Identifying the Characteristics of Hazardous Waste
721.111 Criteria for Listing Hazardous Waste
SUBPART C: CHARACTERISTICS OF HAZARDOUS WASTE
Section
721.120 General
721.121 Characteristic of Ignitability
721.122 Characteristic of Corrosivity
721.123 Characteristic of Reactivity
721.124 Toxicity Characteristic
SUBPART D: LISTS OF HAZARDOUS WASTE
103
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.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 U.S. EPA 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 Z Table to Section 721.102
AUTHORITY: Implementing Section 22.4 and authorized by Section 27 of the Environmental Protection Act
[415 ILCS 5/22.4 and 27].
SOURCE: Adopted in R81-22, 43 PCB 427, at 5 Ill. Reg. 9781, effective May 17, 1982; amended and codified
in R81-22, 45 PCB 317, at 6 Ill. Reg. 4828, effective as noted in 35 Ill. Adm. Code May 17, 1982; amended in
R82-18, 51 PCB 31, at 7 Ill. Reg. 2518, effective February 22, 1983; amended in R82-19, 53 PCB 131, at 7 Ill.
Reg. 13999, effective October 12, 1983; amended in R84-34, 61 PCB 247, 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. ________, _______________________.
104
SUBPART A: GENERAL PROVISIONS
Section 721.103
Definition of Hazardous Waste
a)
A solid waste, as defined in Section 721.102, is a hazardous waste if:
1)
It is not excluded from regulation as a hazardous waste under Section 721.104(b); and
2)
It meets any of the following criteria:
A)
It exhibits any of the characteristics of hazardous waste identified in
721.Subpart C.
i)
Except that any mixture of a waste from the extraction,
beneficiation, or processing of ores or minerals excluded under
Section 721.104(b)(7) and any other solid waste exhibiting a
characteristic of hazardous waste under 721.Subpart C is a hazardous
waste only: if it exhibits a characteristic that would not have been
exhibited by the excluded waste alone if such mixture had not
occurred, or if it continues to exhibit any of the characteristics
exhibited by the non-excluded wastes prior to mixture.
ii)
Further, for the purposes of applying the toxicity characteristic to
such mixtures under subsection (a)(2)(A)(i) above, the mixture is also
a hazardous waste: if it exceeds the maximum concentration for any
contaminant listed in Section 721.124 that would not have been
exceeded by the excluded waste alone if the mixture had not
occurred, or if it continues to exceed the maximum concentration for
any contaminant exceeded by the nonexempt waste prior to mixture.
B)
It is listed in 721.Subpart D and has not been excluded from the lists in
721.Subpart D under 35 Ill. Adm. Code 720.120 and 720.122.
C)
It is a mixture of a solid waste and a hazardous waste that is listed in
721.Subpart D solely because it exhibits one or more of the characteristics of
hazardous waste identified in 721.Subpart C, unless:
i)
the resultant mixture no longer exhibits any characteristic of
hazardous waste identified in 721.Subpart C, or
ii)
the solid waste is excluded from regulation under Section
721.104(b)(7) and the resultant mixture no longer exhibits any
characteristic of hazardous waste identified in 721.Subpart C for
which the hazardous waste listed in 721.Subpart D was listed.
iii)
Nonwastewater mixtures are still subject to the requirements of 35
Ill. Adm. Code 728, even if they no longer exhibit a characteristic at
the point of land disposal.
105
D)
It is a mixture of solid waste and one or more hazardous wastes listed in
721.Subpart D and has not been excluded from this subsection (a)(2) under 35
Ill. Adm. Code 720.120 and 720.122; however, the following mixtures of
solid wastes and hazardous wastes listed in 721.Subpart D are not hazardous
wastes (except by application of subsection (a)(2)(A) or (a)(2)(B) above) if the
generator demonstrates that the mixture consists of wastewater the discharge
of which is subject to regulation under either 35 Ill. Adm. Code 309 or 310
(including wastewater at facilities that have eliminated the discharge of
wastewater) and:
i)
One or more of the following solvents listed in Section 721.131:
carbon tetrachloride, tetrachloroethylene, trichloroethylene, provided
that the maximum total weekly usage of these solvents (other than
the amounts that can be demonstrated not to be discharged to
wastewater) divided by the average weekly flow of wastewater into
the headworks of the facility's wastewater treatment or pretreatment
system does not exceed 1 part per million; or
ii)
One or more of the following spent solvents listed in Section
721.131: methylene chloride, 1,1,1-trichloroethane, chlorobenzene,
o-dichlorobenzene, cresols, cresylic acid, nitrobenzene, toluene,
methyl ethyl ketone, carbon disulfide, isobutanol, pyridine, spent
chlorofluorocarbon solvents, provided that the maximum total
weekly usage of these solvents (other than the amounts that can be
demonstrated not to be discharged to wastewater) divided by the
average weekly flow of wastewater into the headworks of the
facility's wastewater treatment or pretreatment system does not
exceed 25 parts per million; or
iii)
One of the following wastes listed in Section 721.132: heat
exchanger bundle cleaning sludge from the petroleum refining
industry (U.S. EPA hazardous waste no. K050); or
iv)
A discarded commercial chemical product or chemical intermediate
listed in Section 721.133 arising from de minimis losses of these
materials from manufacturing operations in which these materials are
used as raw materials or are produced in the manufacturing process.
For purposes of this subsection, "de minimis" losses include those
from normal material handling operations (e.g., spills from the
unloading or transfer of materials from bins or other containers,
leaks from pipes, valves, or other devices used to transfer materials);
minor leaks of process equipment, storage tanks, or containers; leaks
from well-maintained pump packings and seals; sample purgings;
relief device discharges; discharges from safety showers and rinsing
and cleaning of personal safety equipment; and rinsate from empty
containers or from containers that are rendered empty by that rinsing;
or
v)
Wastewater resulting from laboratory operations containing toxic (T)
wastes listed in 721.Subpart D, provided that the annualized average
flow of laboratory wastewater does not exceed one percent of total
106
wastewater flow into the headworks of the facility's wastewater
treatment or pretreatment system or provided that the wastes'
combined annualized average concentration does not exceed one part
per million in the headworks of the facility's wastewater treatment or
pretreatment facility. Toxic (T) wastes used in laboratories that are
demonstrated not to be discharged to wastewater are not to be
included in this calculation.;
vi)
One or more of the following wastes listed in Section 721.132:
wastewaters from the production of carbamates and carbamoyl
oximes (USEPA Hazardous Waste No. K157), provided that the
maximum weekly usage of formaldehyde, methyl chloride,
methylene chloride, and triethylamine (including all amounts that
cannot be demonstrated to be reacted in the process, destroyed
through treatment, or recovered, i.e., what is discharged or
volatilized) divided by the average weekly flow of process
wastewater prior to any dilutions into the headworks of the facility's
wastewater treatment system does not exceed a total of 5 parts per
million by weight; or
vii)
Wastewaters derived from the treatment of one or more of the
following wastes listed in Section 721.132: organic waste (including
heavy ends, still bottoms, light ends, spent solvents, filtrates, and
decantates) from the production of carbamates and carbamoyl oximes
(USEPA Hazardous Waste No. K156), provided, that the maximum
concentration of formaldehyde, methyl chloride, methylene chloride,
and triethylamine prior to any dilutions into the headworks of the
facility's wastewater treatment system does not exceed a total of 5
milligrams per liter.
E)
Rebuttable presumption for used oil. Used oil containing more than 1,000
ppm total halogens is presumed to be a hazardous waste because it has been
mixed with halogenated hazardous waste listed in 721.Subpart D. Persons
may rebut this presumption by demonstrating that the used oil does not
contain hazardous waste (for example, by using an analytical method from
SW-846, incorporated by reference at 35 Ill. Adm. Code 720.111, to show
that the used oil does not contain significant concentrations of halogenated
hazardous constituents listed in 721.Appendix H).
i)
The rebuttable presumption does not apply to metalworking oils or
fluids containing chlorinated paraffins if they are processed through a
tolling arrangement as described in 35 Ill. Adm. Code 739.124(c) to
reclaim metalworking oils or fluids. The presumption does apply to
metalworking oils or fluids if such oils or fluids are recycled in any
other manner, or disposed.
ii)
The rebuttable presumption does not apply to used oils contaminated
with chlorofluorocarbons (CFCs) removed from refrigeration units
where the CFCs are destined for reclamation. The rebuttable
presumption does apply to used oils contaminated with CFCs that
107
have been mixed with used oil from sources other than refrigeration
units.
b)
A solid waste that is not excluded from regulation under subsection (a)(1) above becomes a
hazardous waste when any of the following events occur:
1)
In the case of a waste listed in 721.Subpart D, when the waste first meets the listing
description set forth in 721.Subpart D.
2)
In the case of a mixture of solid waste and one or more listed hazardous wastes, when
a hazardous waste listed in 721.Subpart D is first added to the solid waste.
3)
In the case of any other waste (including a waste mixture), when the waste exhibits
any of the characteristics identified in 721.Subpart C.
c)
Unless and until it meets the criteria of subsection (d) below, a hazardous waste will remain a
hazardous waste.
BOARD NOTE: This subsection corresponds with 40 CFR 261.3(c)(1). The Board has
codified 40 CFR 261.3(c)(2) at subsection (e) below.
d)
Any solid waste described in subsection (c) above is not a hazardous waste if it meets the
following criteria:
1)
In the case of any solid waste, it does not exhibit any of the characteristics of
hazardous waste identified in 721.Subpart C. (However, wastes that exhibit a
characteristic at the point of generation may still be subject to the requirements of 35
Ill. Adm. Code 728, even if they no longer exhibit a characteristic at the point of land
disposal.)
2)
In the case of a waste that is a listed waste under 721.Subpart D, a waste that contains
a waste listed under 721.Subpart D, or a waste that is derived from a waste listed in
721.Subpart D, it also has been excluded from subsection (c) above under 35 Ill. Adm.
Code 720.120 and 720.122.
e)
Specific inclusions and exclusions.
1)
Except as otherwise provided in subsection (e)(2) below, any solid waste generated
from the treatment, storage, or disposal of a hazardous waste, including any sludge,
spill residue, ash, emission control dust, or leachate (but not including precipitation
run-off), is a hazardous waste. (However, materials that are reclaimed from solid
wastes and that are used beneficially are not solid wastes and hence are not hazardous
wastes under this provision unless the reclaimed material is burned for energy
recovery or used in a manner constituting disposal.)
2)
The following solid wastes are not hazardous even though they are generated from the
treatment, storage, or disposal of a hazardous waste unless they exhibit one or more of
the characteristics of hazardous waste:
A)
Waste pickle liquor sludge generated by lime stabilization of spent pickle
liquor from the iron and steel industry (SIC Codes 331 and 332).
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B)
Wastes from burning any of the materials exempted from regulation by any of
Section 721.106(a)(3)(D) through (a)(3)(F).
C)
Nonwastewater residues, such as slag, resulting from high temperature metal
recovery (HTMR) processing of K061, K062, or F006 waste in the units
identified in this subsection that are disposed of in non-hazardous waste units,
provided that these residues meet the generic exclusion levels identified in the
tables in this subsection for all constituents and the residues exhibit no
characteristics of hazardous waste. The types of units identified are rotary
kilns, flame reactors, electric furnaces, plasma arc furnaces, slag reactors,
rotary hearth furnace/electric furnace combinations, or the following types of
industrial furnaces (as defined in 35 Ill. Adm. Code 720.110): blast furnaces,
smelting, melting and refining furnaces (including pyrometallurgical devices
such as cupolas, reverberator furnaces, sintering machines, roasters, and
foundry furnaces), and other furnaces designated by the Agency pursuant to
that definition.
(i)
Testing requirements must be incorporated in a facility's waste
analysis plan or a generator's self-implementing waste analysis plan;
at a minimum, composite samples of residues must be collected and
analyzed quarterly and when the process or operation generating the
waste changes.
(ii)
Persons claiming this exclusion in an enforcement action will have
the burden of proving by clear and convincing evidence that the
material meets all of the exclusion requirements. The generic
exclusion levels are:
Constituent
Maximum for any single composite sample
(mg/L)
Generic exclusion levels for K061 and K062 nonwastewater HTMR
residues.
Antimony...................................................
0.10
Arsenic .....................................................
0.50
Barium......................................................
7.6
Beryllium...................................................
0.010
Cadmium...................................................
0.050
Chromium (total) .........................................
0.33
Lead.........................................................
0.15
Mercury ....................................................
0.009
Nickel.......................................................
1.0
Selenium....................................................
0.16
Silver........................................................
0.30
Thallium....................................................
0.020
Vanadium ..................................................
1.26
Zinc .........................................................
70.
Generic exclusion levels for F006 nonwastewater HTMR residues
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Antimony...................................................
0.10
Arsenic .....................................................
0.50
Barium......................................................
7.6
Beryllium...................................................
0.010
Cadmium...................................................
0.050
Chromium (total) .........................................
0.33
Cyanide (total) (mg/kg)..................................
1.8
Lead.........................................................
0.15
Mercury ....................................................
0.009
Nickel.......................................................
1.0
Selenium....................................................
0.16
Silver........................................................
0.30
Thallium....................................................
0.020
Zinc .........................................................
70.
(iii)
A one-time notification and certification must be placed in the
facility's files and sent to the Agency (or, for out-of-State shipments,
to the appropriate Regional Administrator of U.S. EPA or the state
agency authorized to implement 40 CFR 268 requirements) for
K061, K062, or F006 HTMR residues that meet the generic
exclusion levels for all constituents and do not exhibit any
characteristics and which are sent to RCRA Subtitle D (municipal
solid waste landfill) units. The notification and certification that is
placed in the generator's or treater's files must be updated if the
process or operation generating the waste changes or if the RCRA
Subtitle D unit receiving the waste changes. However, the generator
or treater need only notify the Agency on an annual basis if such
changes occur. Such notification and certification should be sent to
the Agency by the end of the calendar year, but no later than
December 31. The notification must include the following
information: the name and address of the nonhazardous waste
management unit receiving the waste shipment; the U.S. EPA
hazardous waste number and treatability group at the initial point of
generation; and the treatment standards applicable to the waste at the
initial point of generation. The certification must be signed by an
authorized representative and must state as follows:
"I certify under penalty of law that the generic exclusion
levels for all constituents have been met without
impermissible dilution and that no characteristic of
hazardous waste is exhibited. I am aware that there are
significant penalties for submitting a false certification,
including the possibility of fine and imprisonment."
BOARD NOTE: This subsection would normally
correspond with 40 CFR 261.3(e), a subsection which has
been deleted and marked "reserved" by U.S. EPA. Rather,
this subsection corresponds with 40 CFR 261.3(c)(2), which
the Board codified here to comport with codification
requirements and enhance clarity.
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D)
Biological treatment sludge from the treatment of one of the following wastes
listed in Section 721.132: organic waste (including heavy ends, still bottoms,
light ends, spent solvents, filtrates, and decantates) from the production of
carbamates and carbamoyl oximes (USEPA Hazardous Waste No. K156) and
wastewaters from the production of carbamates and carbamoyl oximes
(USEPA Hazardous Waste No. K157).
f)
Notwithstanding subsections (a) through (e) above and provided the debris, as defined in 35 Ill.
Adm. Code 728.102, does not exhibit a characteristic identified at 721.Subpart C, the
following materials are not subject to regulation under 35 Ill. Adm. Code 720, 721 to 726,
728, or 730:
1)
Hazardous debris as defined in 35 Ill. Adm. Code 728.102 that has been treated using
one of the required extraction or destruction technologies specified in 35 Ill. Adm.
Code 728.Table F; persons claiming this exclusion in an enforcement action will have
the burden of proving by clear and convincing evidence that the material meets all of
the exclusion requirements; or
2)
Debris as defined in 35 Ill. Adm. Code 728.102 that the Agency, considering the
extent of contamination, has determined is no longer contaminated with hazardous
waste.
(Source: Amended at 20 Ill. Reg. ________, effective ______________________)
Section 721.104
Exclusions
a)
Materials that are not solid wastes. The following materials are not solid wastes for the
purpose of this Part:
1)
Sewage:
A)
Domestic sewage; and
B)
Any mixture of domestic sewage and other waste that passes through a sewer
system to publicly-owned treatment works for treatment.
C)
"Domestic sewage" means untreated sanitary wastes that pass through a sewer
system.
2)
Industrial wastewater discharges that are point source discharges with NPDES permits
issued by the Agency pursuant to Section 12(f) of the Environmental Protection Act
and 35 Ill. Adm. Code 309.
BOARD NOTE: This exclusion applies only to the actual point source discharge. It
does not exclude industrial wastewaters while they are being collected, stored, or
treated before discharge, nor does it exclude sludges that are generated by industrial
wastewater treatment.
3)
Irrigation return flows.
111
4)
Source, special nuclear, or by-product material as defined by the Atomic Energy Act
of 1954, as amended (42 U.S.C. 2011 et seq.)
5)
Materials subjected to in-situ mining techniques that are not removed from the ground
as part of the extraction process.
6)
Pulping liquors (i.e., black liquor) that are reclaimed in a pulping liquor recovery
furnace and then reused in the pulping process, unless accumulated speculatively, as
defined in Section 721.101(c).
7)
Spent sulfuric acid used to produce virgin sulfuric acid unless it is accumulated
speculatively, as defined in Section 721.101(c).
8)
Secondary materials that are reclaimed and returned to the original process or
processes in which they were generated where they are reused in the production
process, provided:
A)
Only tank storage is involved, and the entire process through completion of
reclamation is closed by being entirely connected with pipes or other
comparable enclosed means of conveyance;
B)
Reclamation does not involve controlled flame combustion (such as occurs in
boilers, industrial furnaces or incinerators);
C)
The secondary materials are never accumulated in such tanks for over twelve
months without being reclaimed; and
D)
The reclaimed material is not used to produce a fuel or used to produce
products that are used in a manner constituting disposal.
9)
Wood preserving wastes.
A)
Spent wood preserving solutions that have been used and which are reclaimed
and reused for their original intended purpose; and
B)
Wastewaters from the wood preserving process that have been reclaimed and
which are reused to treat wood.
10)
Hazardous waste numbers K060, K087, K141, K142, K143, K144, K145, K147, and
K148, and any wastes from the coke by-products processes that are hazardous only
because they exhibit the toxicity characteristic specified in Section 721.124, when
subsequent to generation these materials are recycled to coke ovens, to the tar
recovery process as a feedstock to produce coal tar, or are mixed with coal tar prior to
the tar's sale or refining. This exclusion is conditioned on there being no land disposal
of the waste from the point it is generated to the point it is recycled to coke ovens, to
tar recovery, to the tar refining processes, or prior to when it is mixed with coal.
11)
Nonwastewater splash condenser dross residue from the treatment of hazardous waste
number K061 in high temperature metals recovery units, provided it is shipped in
drums (if shipped) and not land disposed before recovery.
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12)
Recovered oil from petroleum refining, exploration, and production and from
transportation incident thereto that is to be inserted into the petroleum refining process
(SIC Code 2911) along with normal process streams prior to crude distillation or
catalytic cracking. This exclusion applies to recovered oil stored or transported prior
to insertion, except that the oil must not be stored in a manner involving placement on
the land and the oil must not be accumulated speculatively before being recycled.
Recovered oil is oil that has been reclaimed from secondary materials (such as
wastewater) generated from normal petroleum refining, exploration and production,
and transportation practices. Recovered oil includes oil that is recovered from
refinery wastewater collection and treatment systems, oil recovered from oil and gas
drilling operations, and oil recovered from wastes removed from crude oil storage
tanks. Recovered oil does not include (among other things) oil-bearing hazardous
wastes listed in 721.Subpart D (e.g., K048 through K052, F037, and F038).
However, oil recovered from such wastes may be considered recovered oil.
Recovered oil also does not include used oil as defined in 35 Ill. Adm. Code 739.100.
b)
Solid wastes that are not hazardous wastes. The following solid wastes are not hazardous
wastes:
1)
Household waste, including household waste that has been collected, transported,
stored, treated, disposed, recovered (e.g., refuse-derived fuel), or reused. "Household
waste" means any waste material (including garbage, trash, and sanitary wastes in
septic tanks) derived from households (including single and multiple residences,
hotels, and motels, bunkhouses, ranger stations, crew quarters, campgrounds, picnic
grounds, and day-use recreation areas). A resource recovery facility managing
municipal solid waste shall not be deemed to be treating, storing, disposing of, or
otherwise managing hazardous wastes for the purposes of regulation under this Part, if
such facility:
A)
Receives and burns only:
i)
Household waste (from single and multiple dwellings, hotels, motels,
and other residential sources); and
ii)
Solid waste from commercial or industrial sources that does not
contain hazardous waste, and
B)
Such facility does not accept hazardous waste and the owner or operator of
such facility has established contractual requirements or other appropriate
notification or inspection procedures to assure that hazardous wastes are not
received at or burned in such facility.
BOARD NOTE: The U.S. Supreme Court determined, in City of Chicago v.
Envronmental Defense Fund, Inc., no. 92-1639-- U.S. --, 114 S. Ct. 1588
(May 2, 1994), that this exclusion and RCRA section 3001(i) (42 U.S.C.
§ 6921(i)) do not exclude the ash from facilities covered by this subsection
from regulation as a hazardous waste. At 59 Fed. Reg. 29372 (June 7, 1994),
U.S. EPA granted facilities managing ash from such facilities that is
determined a hazardous waste under 721.Subpart C until December 7, 1994
to file a Part A permit application pursuant to 35 Ill. Adm. Code 703.181. At
60 Fed. Reg. 6666 (Feb. 3, 1995), USEPA stated that it interpreted that the
113
point at which ash becomes subject to RCRA Subtitle C regulation is when
that material leaves the combustion building (including connected air
pollution control equipment).
2)
Solid wastes generated by any of the following that are returned to the soil as
fertilizers:
A)
The growing and harvesting of agricultural crops, or
B)
The raising of animals, including animal manures.
3)
Mining overburden returned to the mine site.
4)
Fly ash waste, bottom ash waste, slag waste, and flue gas emission control waste
generated primarily from the combustion of coal or other fossil fuels, except as
provided in 35 Ill. Adm. Code 726.212 for facilities that burn or process hazardous
waste.
5)
Drilling fluids, produced waters, and other wastes associated with the exploration,
development, or production of crude oil, natural gas, or geothermal energy.
6)
Chromium wastes:
A)
Wastes that fail the test for the toxicity characteristic (Sections 721.124 and
721.Appendix B) because chromium is present or which are are listed in
721.Subpart D due to the presence of chromium, that do not fail the test for
the toxicity characteristic for any other constituent or which are not listed due
to the presence of any other constituent, and that do not fail the test for any
other characteristic, if it is shown by a waste generator or by waste generators
that:
i)
The chromium in the waste is exclusively (or nearly exclusively)
trivalent chromium;
ii)
The waste is generated from an industrial process that uses trivalent
chromium exclusively (or nearly exclusively) and the process does
not generate hexavalent chromium; and
iii)
The waste is typically and frequently managed in non-oxidizing
environments.
B)
Specific wastes that meet the standard in subsection (b)(6)(A) above (so long
as they do not fail the test for the toxicity characteristic for any other
constituent and do not exhibit any other characteristic) are:
i)
Chrome (blue) trimmings generated by the following subcategories of
the leather tanning and finishing industry: hair pulp/chrome
tan/retan/wet finish, hair save/chrome tan/retan/wet finish, retan/wet
finish, no beamhouse, through-the-blue, and shearling;
114
ii)
Chrome (blue) shavings generated by the following subcategories of
the leather tanning and finishing industry: hair pulp/chrome
tan/retan/wet finish, hair save/chrome tan/retan/wet finish, retan/wet
finish, no beamhouse, through-the-blue, and shearling;
iii)
Buffing dust generated by the following subcategories of the leather
tanning and finishing industry: hair pulp/chrome tan/retan/wet
finish, hair save/chrome tan/retan/wet finish, retan/wet finish, no
beamhouse, through-the-blue;
iv)
Sewer screenings generated by the following subcategories of the
leather tanning and finishing industry: hair pulp/chrome
tan/retan/wet finish, hair save/chrome tan/retan/wet finish, retan/wet
finish, no beamhouse, through-the-blue, and shearling;
v)
Wastewater treatment sludges generated by the following
subcategories of the leather tanning and finishing industry: hair
pulp/chrome tan/retan/wet finish, hair save/chrome tan/retan/wet
finish, retan/wet finish, no beamhouse, through-the-blue, and
shearling;
vi)
Wastewater treatment sludges generated by the following
subcategories of the leather tanning and finishing industry: hair
pulp/chrome tan/retan/wet finish, hair save/chrome tan/retan/wet
finish, and through-the-blue;
vii)
Waste scrap leather from the leather tanning industry, the shoe
manufacturing industry, and other leather product manufacturing
industries; and
viii)
Wastewater treatment sludges from the production of titanium
dioxide pigment using chromium-bearing ores by the chloride
process.
7)
Solid waste from the extraction, beneficiation, and processing of ores and minerals
(including coal, phosphate rock, and overburden from the mining of uranium ore),
except as provided by 35 Ill. Adm. Code 726.212 for facilities that burn or process
hazardous waste. For purposes of this subsection, beneficiation of ores and minerals
is restricted to the following activities: crushing, grinding, washing, dissolution,
crystallization, filtration, sorting, sizing, drying, sintering, pelletizing, briquetting,
calcining to remove water or carbon dioxide, roasting, autoclaving or chlorination in
preparation for leaching (except where the roasting or autoclaving or chlorination and
leaching sequence produces a final or intermediate product that does not undergo
further beneficiation or processing), gravity concentration, magnetic separation,
electrostatic separation, floatation, ion exchange, solvent extraction, electrowinning,
precipitation, amalgamation, and heap, dump, vat tank, and in situ leaching. For the
purposes of this subsection, solid waste from the processing of ores and minerals
includes only the following wastes:
A)
Slag from primary copper processing,
115
B)
Slag from primary lead processing,
C)
Red and brown muds from bauxite refining,
D)
Phosphogypsum from phosphoric acid production,
E)
Slag from elemental phosphorus production,
F)
Gasifier ash from coal gasification,
G)
Process wastewater from coal gasification,
H)
Calcium sulfate wastewater treatment plant sludge from primary copper
processing,
I)
Slag tailings from primary copper processing,
J)
Fluorogypsum from hydrofluoric acid production,
K)
Process wastewater from hydrofluoric acid production,
L)
Air pollution control dust or sludge from iron blast furnaces,
M)
Iron blast furnace slag,
N)
Treated residue from roasting and leaching of chrome ore,
O)
Process wastewater from primary magnesium processing by the anhydrous
process,
P)
Process wastewater from phosphoric acid production,
Q)
Basic oxygen furnace and open hearth furnace air pollution control dust or
sludge from carbon steel production,
R)
Basic oxygen furnace and open hearth furnace slag from carbon steel
production,
S)
Chloride processing waste solids from titanium tetrachloride production, and
T)
Slag from primary zinc smelting.
8)
Cement kiln dust waste, except as provided by 35 Ill. Adm. Code 726.212 for
facilities that burn or process hazardous waste.
9)
Solid waste that consists of discarded arsenical-treated wood or wood products that
fails the test for the toxicity characteristic for hazardous waste codes D004 through
D017 and which is not a hazardous waste for any other reason if the waste is generated
by persons that utilize the arsenical-treated wood and wood products for these
materials' intended end use.
116
10)
Petroleum-contaminated media and debris that fail the test for the toxicity
characteristic of Section 721.124 (hazardous waste codes D018 through D043 only)
and which are subject to corrective action regulations under 35 Ill. Adm. Code 731.
11)
This subsection corresponds with 40 CFR 261.4(b)(11), which expired by its own
terms on January 25, 1993. This statement maintains structural parity with U.S. EPA
regulations.
12)
Used chlorofluorocarbon refrigerants from totally enclosed heat transfer equipment,
including mobile air conditioning systems, mobile refrigeration, and commercial and
industrial air conditioning and refrigeration systems, that uses chlorofluorocarbons as
the heat transfer fluid in a refrigeration cycle, provided the refrigerant is reclaimed for
further use.
13)
Non-terne plated used oil filters that are not mixed with wastes listed in 721.Subpart
D, if these oil filters have been gravity hot-drained using one of the following
methods:
A)
Puncturing the filter anti-drain back valve or the filter dome end and hot-
draining;
B)
Hot-draining and crushing;
C)
Dismantling and hot-draining; or
D)
Any other equivalent hot-draining method that will remove used oil.
14)
Used oil re-refining distillation bottoms that are used as feedstock to manufacture
asphalt products.
c)
Hazardous wastes that are exempted from certain regulations. A hazardous waste that is
generated in a product or raw material storage tank, a product or raw material transport vehicle
or vessel, a product or raw material pipeline, or in a manufacturing process unit, or an
associated non-waste-treatment manufacturing unit, is not subject to regulation under 35 Ill.
Adm. Code 702, 703, 705, and 722 through 725, and 728 or to the notification requirements of
Section 3010 of RCRA until it exits the unit in which it was generated, unless the unit is a
surface impoundment, or unless the hazardous waste remains in the unit more than 90 days
after the unit ceases to be operated for manufacturing or for storage or transportation of product
or raw materials.
d)
Samples
1)
Except as provided in subsection (d)(2) below, a sample of solid waste or a sample of
water, soil, or air that is collected for the sole purpose of testing to determine its
characteristics or composition is not subject to any requirements of this Part or 35 Ill.
Adm. Code 702, 703, 705, and 722 through 728. The sample qualifies when:
A)
The sample is being transported to a laboratory for the purpose of testing;
B)
The sample is being transported back to the sample collector after testing;
117
C)
The sample is being stored by the sample collector before transport to a
laboratory for testing;
D)
The sample is being stored in a laboratory before testing;
E)
The sample is being stored in a laboratory for testing but before it is returned
to the sample collector; or
F)
The sample is being stored temporarily in the laboratory after testing for a
specific purpose (for example, until conclusion of a court case or enforcement
action where further testing of the sample may be necessary).
2)
In order to qualify for the exemption in subsection (d)(1)(A) or (d)(1)(B) above, a
sample collector shipping samples to a laboratory and a laboratory returning samples
to a sample collector shall:
A)
Comply with U.S. Department of Transportation (DOT), U.S. Postal Service
(USPS), or any other applicable shipping requirements; or
B)
Comply with the following requirements if the sample collector determines
that DOT, USPS, or other shipping requirements do not apply to the shipment
of the sample:
i)
Assure that the following information accompanies the sample: The
sample collector's name, mailing address, and telephone number; the
laboratory's name, mailing address, and telephone number; the
quantity of the sample; the date of the shipment; and a description of
the sample.
ii)
Package the sample so that it does not leak, spill, or vaporize from
its packaging.
3)
This exemption does not apply if the laboratory determines that the waste is hazardous
but the laboratory is no longer meeting any of the conditions stated in subsection (d)(1)
above.
e)
Treatability study samples.
1)
Except as is provided in subsection (e)(2) below, a person that generates or collects
samples for the purpose of conducting treatability studies, as defined in 35 Ill. Adm.
Code 720.110, are not subject to any requirement of 35 Ill. Adm. Code 721 through
723 or to the notification requirements of Section 3010 of the Resource Conservation
and Recovery Act. Nor are such samples included in the quantity determinations of
Section 721.105 and 35 Ill. Adm. Code 722.134(d) when:
A)
The sample is being collected and prepared for transportation by the generator
or sample collector;
B)
The sample is being accumulated or stored by the generator or sample
collector prior to transportation to a laboratory or testing facility; or
118
C)
The sample is being transported to the laboratory or testing facility for the
purpose of conducting a treatability study.
2)
The exemption in subsection (e)(1) above is applicable to samples of hazardous waste
being collected and shipped for the purpose of conducting treatability studies provided
that:
A)
The generator or sample collector uses (in "treatability studies") no more than
10,000 kg of media contaminated with non-acute hazardous waste, 1000 kg of
non-acute hazardous waste other than contaminated media, 1 kg of acute
hazardous waste, or 2500 kg of media contaminated with acute hazardous
waste for each process being evaluated for each generated wastestream;
B)
The mass of each shipment does not exceed 10,000 kg; the 10,000 kg quantity
may be all media contaminated with non-acute hazardous waste, or may
include 2500 kg of media contaminated with acute hazardous waste, 1000 kg
of hazardous waste, and 1 kg of acute hazardous waste;
C)
The sample must be packaged so that it does not leak, spill, or vaporize from
its packaging during shipment and the requirements of subsections (e)(2)(C)(i)
or (e)(2)(C)(ii), below, are met.
i)
The transportation of each sample shipment complies with U.S.
Department of Transportation (DOT), U.S. Postal Service (USPS),
or any other applicable shipping requirements; or
ii)
If the DOT, USPS, or other shipping requirements do not apply to
the shipment of the sample, the following information must
accompany the sample: The name, mailing address, and telephone
number of the originator of the sample; the name, address, and
telephone number of the facility that will perform the treatability
study; the quantity of the sample; the date of the shipment; and, a
description of the sample, including its U.S. EPA hazardous waste
number;
D)
The sample is shipped to a laboratory or testing facility that is exempt under
subsection (f) below, or has an appropriate RCRA permit or interim status;
E)
The generator or sample collector maintains the following records for a
period ending three years after completion of the treatability study:
i)
Copies of the shipping documents;
ii)
A copy of the contract with the facility conducting the treatability
study;
iii)
Documentation showing: The amount of waste shipped under this
exemption; the name, address, and U.S. EPA identification number
of the laboratory or testing facility that received the waste; the date
the shipment was made; and, whether or not unused samples and
residues were returned to the generator; and
119
F)
The generator reports the information required in subsection (e)(2)(E)(iii)
above in its report under 35 Ill. Adm. Code 722.141.
3)
The Agency may grant requests on a case-by-case basis for up to an additional two
years for treatability studies involving bioremediation. The Agency may grant
requests, on a case-by-case basis, for quantity limits in excess of those specified in
subsection (e)(2)(A) and (e)(2)(B) above and (f)(4) below, for up to an additional 5000
kg of media contaminated with non-acute hazardous waste, 500 kg of non-acute
hazardous waste, 2500 kg of media contaminated with acute hazardous waste, and 1
kg of acute hazardous waste:
A)
In response to requests for authorization to ship, store, and conduct further
treatability studies on additional quantities in advance of commencing
treatability studies. Factors to be considered in reviewing such requests
include the nature of the technology, the type of process (e.g., batch versus
continuous), the size of the unit undergoing testing (particularly in relation to
scale-up considerations), the time or quantity of material required to reach
steady-state operating conditions, or test design considerations, such as mass
balance calculations.
B)
In response to requests for authorization to ship, store, and conduct
treatability studies on additional quantities after initiation or completion of
initial treatability studies when: There has been an equipment or mechanical
failure during the conduct of the treatability study, there is need to verify the
results of a previously-conducted treatability study, there is a need to study
and analyze alternative techniques within a previously-evaluated treatment
process, or there is a need to do further evaluation of an ongoing treatability
study to determine final specifications for treatment.
C)
The additional quantities allowed and timeframes allowed in subsections
(e)(3)(A) and (e)(3)(B) above are subject to all the provisions in subsections
(e)(1) and (e)(2)(B) through (e)(2)(F) above. The generator or sample
collector shall apply to the Agency and provide in writing the following
information:
i)
The reason why the generator or sample collector requires additional
time or quantity of sample for the treatability study evaluation and
the additional time or quantity needed;
ii)
Documentation accounting for all samples of hazardous waste from
the wastestream that have been sent for or undergone treatability
studies, including the date each previous sample from the waste
stream was shipped, the quantity of each previous shipment, the
laboratory or testing facility to which it was shipped, what
treatability study processes were conducted on each sample shipped,
and the available results of each treatability study;
iii)
A description of the technical modifications or change in
specifications that will be evaluated and the expected results;
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iv)
If such further study is being required due to equipment or
mechanical failure, the applicant shall include information regarding
the reason for the failure or breakdown and also include what
procedures or equipment improvements have been made to protect
against further breakdowns; and
v)
Such other information as the Agency determines is necessary.
4)
Final Agency determinations pursuant to this subsection may be appealed to the Board.
f)
Samples undergoing treatability studies at laboratories or testing facilities. Samples undergoing
treatability studies and the laboratory or testing facility conducting such treatability studies (to
the extent such facilities are not otherwise subject to RCRA requirements) are not subject to
any requirement of this Part, or of 35 Ill. Adm. Code 702, 703, 705, 722 through 726, and 728
or to the notification requirements of Section 3010 of the Resource Conservation and Recovery
Act, provided that the requirements of subsections (f)(1) through (f)(11) below are met. A
mobile treatment unit may qualify as a testing facility subject to subsections (f)(1) through
(f)(11) below. Where a group of mobile treatment units are located at the same site, the
limitations specified in subsections (f)(1) through (f)(11) below apply to the entire group of
mobile treatment units collectively as if the group were one mobile treatment unit.
1)
No less than 45 days before conducting treatability studies, the facility notifies the
Agency in writing that it intends to conduct treatability studies under this subsection.
2)
The laboratory or testing facility conducting the treatability study has a U.S. EPA
identification number.
3)
No more than a total of 10,000 kg of "as received" media contaminated with non-acute
hazardous waste, 2500 kg of media contaminated with acute hazardous waste, or 250
kg of other "as received" hazardous waste is subject to initiation of treatment in all
treatability studies in any single day. "As received" waste refers to the waste as
received in the shipment from the generator or sample collector.
4)
The quantity of "as received" hazardous waste stored at the facility for the purpose of
evaluation in treatability studies does not exceed 10,000 kg, the total of which can
include 10,000 kg of media contaminated with non-acute hazardous waste, 2500 kg of
media contaminated with acute hazardous waste, 1000 kg of non-acute hazardous
wastes other than contaminated media, and 1 kg of acute hazardous waste. This
quantity limitation does not includetreatment materials (including nonhazardous solid
waste) added to "as received" hazardous waste.
5)
No more than 90 days have elapsed since the treatability study for the sample was
completed, or no more than one year (two years for treatability studies involving
bioremediation) has elapsed since the generator or sample collector shipped the sample
to the laboratory or testing facility, whichever date first occurs. Up to 500 kg of
treated material from a particular waste stream from treatability studies may be
archived for future evaluation up to five years from the date of initial receipt.
Quantities of materials archived are counted against the total storage limit for the
facility.
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6)
The treatability study does not involve the placement of hazardous waste on the land
or open burning of hazardous waste.
7)
The facility maintains records for three years following completion of each study that
show compliance with the treatment rate limits and the storage time and quantity
limits. The following specific information must be included for each treatability study
conducted:
A)
The name, address, and U.S. EPA identification number of the generator or
sample collector of each waste sample;
B)
The date the shipment was received;
C)
The quantity of waste accepted;
D)
The quantity of "as received" waste in storage each day;
E)
The date the treatment study was initiated and the amount of "as received"
waste introduced to treatment each day;
F)
The date the treatability study was concluded;
G)
The date any unused sample or residues generated from the treatability study
were returned to the generator or sample collector or, if sent to a designated
facility, the name of the facility and the U.S. EPA identification number.
8)
The facility keeps, on-site, a copy of the treatability study contract and all shipping
papers associated with the transport of treatability study samples to and from the
facility for a period ending three years from the completion date of each treatability
study.
9)
The facility prepares and submits a report to the Agency by March 15 of each year
that estimates the number of studies and the amount of waste expected to be used in
treatability studies during the current year, and includes the following information for
the previous calendar year:
A)
The name, address, and U.S. EPA identification number of the facility
conducting the treatability studies;
B)
The types (by process) of treatability studies conducted;
C)
The names and addresses of persons for whom studies have been conducted
(including their U.S. EPA identification numbers);
D)
The total quantity of waste in storage each day;
E)
The quantity and types of waste subjected to treatability studies;
F)
When each treatability study was conducted; and
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G)
The final disposition of residues and unused sample from each treatability
study.
10)
The facility determines whether any unused sample or residues generated by the
treatability study are hazardous waste under Section 721.103 and, if so, are subject to
35 Ill. Adm. Code 702, 703, and 721 through 728, unless the residues and unused
samples are returned to the sample originator under the subsection (e) exemption
above.
11)
The facility notifies the Agency by letter when the facility is no longer planning to
conduct any treatability studies at the site.
(Source: Amended at 20 Ill. Reg. ________, effective ______________________)
Section 721.105
Special Requirements for Hazardous Waste Generated by Small Quantity Generators
a)
A generator is a conditionally exempt small quantity generator in a calendar month if it
generates no more than 100 kilograms of hazardous waste in that month. 35 Ill. Adm. Code
700 explains the relation of this to the 100 kg/mo exception of 35 Ill. Adm. Code 809.
b)
Except for those wastes identified in subsections (e), (f), (g) and (j) below, a conditionally
exempt small quantity generator's hazardous wastes are not subject to regulation under 35 Ill.
Adm. Code 702, 703, 705 and 722 through 726 and 728, and the notification requirements of
Section 3010 of Resource Conservation and Recovery Act, provided the generator complies
with the requirements of subsections (f), (g) and (j) below.
c) Hazardous waste that is not subject to regulation or that is subject only to 35 Ill. Adm. Code
722.111, 722.112, 722.140(c) and 722.141 is not included in When making the quantity
determinations of this Part and 35 Ill. Adm. Code 722 through 726 and 728, and is not subject
to any requirements of those Parts. Hazardous waste that is subject to the requirements of
Section 721.106(b) and (c) and 35 Ill. Adm. Code 726.Subparts C, D and F is included in the
quantity determinations of this Part and is subject to the requirements of this Part and 35 Ill.
Adm. Code 722 through 726 and 728., the generator must include all hazardous waste that it
generates, except the following hazardous waste:
1)
Hazardous waste that is exempt from regulation under Section 721.104(c) through (f),
721.106(a)(3), 721.107(a)(1), or 721.108;
2)
Hazardous waste that is managed immediately upon generation only in on-site
elementary neutralization units, wastewater treatment units, or totally enclosed
treatment facilities, as defined in 35 Ill. Adm. Code 720.110;
3)
Hazardous waste that is recycled, without prior storage or accumulation, only in an
on-site process subject to regulation under Section 721.106(c)(2);
4)
Hazardous waste that is used oil managed under the requirements of Section
721.106(a)(4) and 35 Ill. Adm. Code 739;
5)
Hazardous waste that is spent lead-acid batteries managed under the requirements of
35 Ill. Adm. Code 726.Subpart G; and
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6)
Hazardous waste that is universal waste managed under Section 721.109 and 35 Ill.
Adm. Code 733.
d)
In determining the quantity of hazardous waste it generates, a generator need not include:
1)
Hazardous waste when it is removed from on-site storage; or
2)
Hazardous waste produced by on-site treatment (including reclamation) of its
hazardous waste so long as the hazardous waste that is treated was counted once; or,
3)
Spent materials that are generated, reclaimed and subsequently reused on-site, so long
as such spent materials have been counted once.
e)
If a generator generates acute hazardous waste in a calendar month in quantities greater than
set forth below, all quantities of that acute hazardous waste are subject to full regulation under
35 Ill. Adm. Code 702, 703, 705 and 722 through 726 and 728, and the notification
requirements of Section 3010 of the Resource Conservation and Recovery Act:
1)
A total of one kilogram of one or more of the acute hazardous wastes listed in Sections
721.131, 721.132, or 721.133(e); or
2)
A total of 100 kilograms of any residue or contaminated soil, waste or other debris
resulting from the clean-up of a spill, into or on any land or water, of any one or more
of the acute hazardous wastes listed in Sections 721.131, 721.132, or 721.133(e).
BOARD NOTE: "Full regulation" means those regulations applicable to generators of
greater than 1000 kg of non-acute hazardous waste in a calendar month.
f)
In order for acute hazardous wastes generated by a generator of acute hazardous wastes in
quantities equal to or less than those set forth in subsection (e)(1) or (e)(2) above to be
excluded from full regulation under this Section, the generator must comply with the following
requirements:
1)
35 Ill. Adm. Code 722.111.
2)
The generator may accumulate acute hazardous waste on-site. If the generator
accumulates at any time acute hazardous wastes in quantities greater than set forth in
subsections (e)(1) or (e)(2) above, all of those accumulated wastes are subject to
regulation under 35 Ill. Adm. Code 702, 703, 705 and 722 through 726 and 728, and
the applicable notification requirements of Section 3010 of the Resource Conservation
and Recovery Act. The time period of 35 Ill. Adm. Code 722.134(a), for
accumulation of wastes on-site, begins when the accumulated wastes exceed the
applicable exclusion limit.
3)
A conditionally exempt shall quantity generator may either treat or dispose of its acute
hazardous waste in an on-site facility, or ensure delivery to an off-site storage,
treatment, or disposal facility, either of whichprovided that if the on-site or off-site
facility is located in the United States, it fulfills any of the following conditions, if
located in the United States, is:
A) PThe facility is permitted under 35 Ill. Adm. Code 703;
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B) InThe facility has interim status under 35 Ill. Adm. Code 703 and 725;
C) AThe facility is authorized to manage hazardous waste by a Sstate with a
hazardous waste management program approved by U.S. EPA pursuant to 40
CFR 271;
D) PThe facility is permitted, licensed or registered by a Sstate to manage
municipal or industrial solid waste; or
E) AThe facility is a facility whichthat:
i)
Beneficially uses or reuses or legitimately recycles or reclaims its
waste; or
ii)
Treats its waste prior to beneficial use or reuse, or legitimate
recycling or reclamation.; or
F)
For universal waste managed under 35 Ill. Adm. Code 733, the facility is a
universal waste handler or destination facility subject to the requirements of
35 Ill. Adm. Code 733.
g)
In order for hazardous waste generated by a conditionally exempt small quantity generator in
quantities of less than 100 kilograms of hazardous waste during a calendar month to be
excluded from full regulation under this Section, the generator must comply with the following
requirements:
1)
35 Ill. Adm. Code 722.111;
2)
The conditionally exempt small quantity generator may accumulate hazardous waste
on-site. If it accumulates at any time more than a total of 1000 kilograms of the
generator's hazardous waste, all of those accumulated wastes are subject to regulation
under the special provisions of 35 Ill. Adm. Code 722 applicable to generators of
between 100 kg and 1000 kg of hazardous waste in a calendar month as well as the
requirements of 35 Ill. Adm. Code 702, 703, 705 and 723 through 726 and 728, and
the applicable notification requirements of Section 3010 of the Resource Conservation
and Recovery Act. The time period of 35 Ill. Adm. Code 722.134(d) for
accumulation of wastes on-site begins for a small quantity generator when the
accumulated wastes exceed 1000 kilograms;
3)
A conditionally exempt small quantity generator may either treat or dispose of its
hazardous waste in an on-site facility, or ensure delivery to an off-site storage,
treatment, or disposal facility, either of whichprovided that if the on-site or off-site
facility is located in the United States, it fulfills any of the following conditions, if
located in the United States, is:
A) PThe facility is permitted under 35 Ill. Adm. Code 702 and 703;
B) InThe facility has interim status under 35 Ill. Adm. Code 703 and 725;
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C) AThe facility is authorized to manage hazardous waste by a Sstate with a
hazardous waste management program approved by U.S. EPA under 40 CFR
271 (1986);
D) PThe facility is permitted, licensed or registered by a Sstate to manage
municipal or industrial solid waste; or
E) AThe facility is a facility whichthat:
i)
Beneficially uses or re-uses, or legitimately recycles or reclaims the
small quantity generator's waste; or
ii)
Treats its waste prior to beneficial use or re-use, or legitimate
recycling or reclamation.; or
F)
For universal waste managed under 35 Ill. Adm. Code 733, the facility is a
universal waste handler or destination facility subject to the requirements of
35 Ill. Adm. Code 733.
h)
Hazardous waste subject to the reduced requirements of this Section may be mixed with non-
hazardous waste and remain subject to these reduced requirements even though the resultant
mixture exceeds the quantity limitations identified in this Section, unless the mixture meets any
of the characteristics of hazardous wastes identified in Subpart C.
i)
If a small quantity generator mixes a solid waste with a hazardous waste that exceeds a quantity
exclusion level of this Section, the mixture is subject to full regulation.
j)
If a conditionally exempt small quantity generator's hazardous wastes are mixed with used oil,
the mixture is subject to 35 Ill. Adm. Code 739, if it is destined to be burned for energy
recovery. Any material produced from such a mixture by processing, blending, or other
treatment is also so regulated if it is destined to be burned for energy recovery.
(Source: Amended at 20 Ill. Reg. ________, effective ______________________)
Section 721.106
Requirements for Recyclable Materials
a)
Recyclable materials:
1)
Hazardous wastes that are recycled are subject to the requirements for generators,
transporters, and storage facilities of subsections (b) and (c) below, except for the
materials listed in subsections (a)(2) and (a)(3) below. Hazardous wastes that are
recycled will be known as "recyclable materials".
2)
The following recyclable materials are not subject to the requirements of this Section
but are regulated under 35 Ill. Adm. Code 726.Subparts C through H and all
applicable provisions in 35 Ill. Adm. Code 702, 703, and 705.
A)
Recyclable materials used in a manner constituting disposal (35 Ill. Adm.
Code 726.Subpart C);
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B)
Hazardous wastes burned for energy recovery in boilers and industrial
furnaces that are not regulated under 35 Ill. Adm. Code 724.Subpart O or
725.Subpart O (35 Ill. Adm. Code 726.Subpart H);
C)
Recyclable materials from which precious metals are reclaimed (35 Ill. Adm.
Code 726.Subpart F);
D)
Spent lead-acid batteries that are being reclaimed (35 Ill. Adm. Code
726.Subpart G).
3)
The following recyclable materials are not subject to regulation under 35 Ill. Adm.
Code 722 through 726, 728, or 702, 703, or 705 and are not subject to the notification
requirements of Section 3010 of the Resource Conservation and Recovery Act:
A)
Industrial ethyl alcohol that is reclaimed except that, unless provided
otherwise in an international agreement as specified in 35 Ill. Adm. Code
722.158:
i)
A person initiating a shipment for reclamation in a foreign country
and any intermediary arranging for the shipment shall comply with
the requirements applicable to a primary exporter in 35 Ill. Adm.
Code 722.153; 722.156(a)(1) through (a)(4), (a)(6), and (b); and
722.157; shall export such materials only upon consent of the
receiving country and in conformance with the U.S. EPA
Acknowledgement of Consent, as defined in 35 Ill. Adm. Code
722.Subpart E; and shall provide a copy of the U.S. EPA
Acknowledgement of Consent to the shipment to the transporter
transporting the shipment for export;
ii)
Transporters transporting a shipment for export shall not accept a
shipment if the transporter knows that the shipment does not conform
to the U.S. EPA Acknowledgement of Consent, shall ensure that a
copy of the U.S. EPA Acknowledgement of Consent accompanies
the shipment, and shall ensure that it is delivered to the facility
designated by the person initiating the shipment.;
B) Used batteries (or used battery cells) returned to a battery manufacturer for
regeneration;
CB)
Scrap metal;
DC)
Fuels produced from the refining of oil-bearing hazardous wastes along with
normal process streams at a petroleum refining facility if such wastes result
from normal petroleum refining, production, and transportation practices (this
exemption does not apply to fuels produced from oil recovered from oil-
bearing hazardous waste where such recovered oil is already excluded under
Section 721.104(a)(12));
ED)
Petroleum refining wastes.
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i)
Hazardous waste fuel produced from oil-bearing hazardous wastes
from petroleum refining, production, or transportation practices or
produced from oil reclaimed from such hazardous wastes, where
such hazardous wastes are reintroduced into a process that does not
use distillation or does not produce products from crude oil, so long
as the resulting fuel meets the used oil specification under 35 Ill.
Adm. Code 726.140(e) and so long as no other hazardous wastes are
used to produce the hazardous waste fuel;
ii)
Hazardous waste fuel produced from oil-bearing hazardous waste
from petroleum refining production, and transportation practices,
where such hazardous wastes are reintroduced into a refining process
after a point at which contaminants are removed, so long as the fuel
meets the used oil fuel specification under 35 Ill. Adm. Code
726.140(e); and
iii)
Oil reclaimed from oil-bearing hazardous wastes from petroleum
refining, production, and transportation practices, which reclaimed
oil is burned as a fuel without reintroduction to a refining process, so
long as the reclaimed oil meets the used oil fuel specification under
35 Ill. Adm. Code 726.140(e); and
FE)
Petroleum coke produced from petroleum refinery hazardous wastes
containing oil by the same person that generated the wastes unless the
resulting coke product exceeds one or more of the characteristics of hazardous
waste in 721.Subpart C.
4)
Used oil that is recycled and is also a hazardous waste solely because it exhibits a
hazardous characteristic is not subject to the requirements of 35 Ill. Adm. Code 720
through 728, but it is regulated under 35 Ill. Adm. Code 739. Used oil that is
recycled includes any used oil that is reused for any purpose following its original use
(including the purpose for which the oil was originally used). Such term includes, but
is not limited to, oil that is re-refined, reclaimed, burned for energy recovery, or
reprocessed.
b)
Generators and transporters of recyclable materials are subject to the applicable requirements
of 35 Ill. Adm. Code 722 and 723 and the notification requirements under Section 3010 of the
Resource Conservation and Recovery Act, except as provided in subsection (a) above.
c)
Storage and recycling:
1)
Owners or operators of facilities that store recyclable materials before they are
recycled are regulated under all applicable provisions of 35 Ill. Adm. Code 702, 703,
and 705; 724.Subparts A through L, AA, and BB; and 725.Subparts A through L, AA,
and BB; 726; 728; and the notification requirement under Section 3010 of the
Resource Conservation and Recovery Act, except as provided in subsection (a) above.
(The recycling process itself is exempt from regulation, except as provided in
subsection (d) below.)
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2)
Owners or operators of facilities that recycle recyclable materials without storing them
before they are recycled are subject to the following requirements, except as provided
in subsection (a) above:
A)
Notification requirements under Section 3010 of the Resource Conservation
and Recovery Act,
B)
35 Ill. Adm. Code 725.171 and 725.172 (dealing with the use of the manifest
and manifest discrepancies), and
C)
subsection (d) below.
d)
Owners or operators of facilities required to have a RCRA permit pursuant to 35 Ill. Adm.
Code 703 with hazardous waste management units that recycle hazardous wastes are subject to
35 Ill. Adm. Code 724.Subparts AA and BB and 725.Subparts AA and BB.
(Source: Amended at 20 Ill. Reg. ________, effective ______________________)
Section 721.109 Requirements for Universal Waste
The wastes listed in this Section are exempt from regulation under 35 Ill. Adm. Code 702 through 705, 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; and
c)
Thermostats, as described in 35 Ill. Adm. Code 733.104.
(Source: Added at 20 Ill. Reg. ________, effective _______________________)
SUBPART D: LISTS OF HAZARDOUS WASTE
Section 721.130
General
a)
A solid waste is a hazardous waste if it is listed in this Subpart, unless it has been excluded
from this list under 35 Ill. Adm. Code 720.120 and 720.122.
b)
The basis for listing the classes or types of wastes listed in this Subpart is indicated by
employing one or more of the Hazard Codes:
1)
Hazard Codes:
A)
Ignitable Waste
(I)
B)
Corrosive Waste
(C)
C)
Reactive Waste
(R)
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D)
Toxicity Characteristic
(E)
E)
Acute Hazardous Waste
(H)
F)
Toxic Waste
(T)
2)
Appendix G identifies the constituent which caused the Administrator to list the waste
as an Toxicity Characteristic (E) or Toxic Waste (T) in Sections 721.131 and 721.132.
c)
Each hazardous waste listed in this Subpart is assigned an EPA Hazardous Waste Number
which precedes the name of the waste. This number must be used in complying with the
notification requirements of Section 3010 of the Act and certain recordkeeping and reporting
requirements under 35 Ill. Adm. Code 702, 703, 722 through 725 and 728 and 40 CFR 122.
d)
The following hazardous wastes listed in Section 721.131 or 721.132 are subject to the
exclusion limits for acute hazardous wastes established in Section 721.105: hazardous wastes
numbers F020, F021, F022, F023, F026 and F027.
(Source: Amended at 20 Ill. Reg. ________, effective ______________________)
Section 721.131
Hazardous Wastes From Nonspecific Sources
a)
The following solid wastes are listed hazardous wastes from non-specific sources unless they
are excluded under 35 Ill. Adm. Code 720.120 and 720.122 and listed in Section 721.Appendix
I.
EPA
Hazardous
Waste No.
Industry and Hazardous Waste
Hazard
Code
F001
The following spent halogenated solvents used in degreasing: tetra-
chloroethylene, trichloroethylene, methylene chloride, 1,1,1-tri-
chloroethane, carbon tetrachloride and chlorinated fluorocarbons;
all spent solvent mixtures and blends used in degreasing containing,
before use, a total of ten percent or more (by volume) of one or
more of the above halogenated solvents or those solvents listed in
F002, F004 or F005; and still bottoms from the recovery of these
spent solvents and spent solvent mixtures.
(T)
F002
The following spent halogenated solvents: tetrachloroethylene,
methylene chloride, trichloroethylene, 1,1,1-trichloroethane,
chlorobenzene, 1,1,2-trichloro-1,2,2-trifluoroethane,
orthodichlorobenzene, trichlorofluoromethane and 1,1,2-trichloro-
ethane; all spent solvent mixtures and blends containing, before
use, a total of ten percent or more (by volume) of one or more of
the above halogenated solvents or those solvents listed in F001,
F004 or F005; and still bottoms from the recovery of these spent
solvents and spent solvent mixtures.
(T)
130
F003
The following spent non-halogenated solvents: xylene, acetone,
ethyl acetate, ethyl benzene, ethyl ether, methyl isobutyl ketone, n-
butyl alcohol, cyclohexanone and methanol; all spent solvent
mixtures and blends containing, before use, only the above spent
non-halogenated solvents; and all spent solvent mixtures and blends
containing, before use, one or more of the above non-halogenated
solvents and a total of ten percent or more (by volume) of one or
more of those solvents listed in F001, F002, F004 or F005; and
still bottoms from the recovery of these spent solvents and spent
solvent mixtures.
(I)
F004
The following spent non-halogenated solvents: cresols and cresylic
acid and nitrobenzene; all spent solvent mixtures and blends
containing, before use, a total of ten percent or more (by volume)
of one or more of the above non-halogenated solvents or those
solvents listed in F001, F002 or F005; and still bottoms from the
recovery of these spent solvents and spent solvent mixtures.
(T)
F005
The following spent non-halogenated solvents: toluene, methyl
ethyl ketone, carbon disulfide, isobutanol, pyridine, benzene, 2-
ethoxyethanol and 2-nitropropane; all spent solvent mixtures and
blends, containing, before use, a total of ten percent or more (by
volume) of one or more of the above non-halogenated solvents or
those solvents listed in F001, F002 or F004; and still bottoms from
the recovery of these spent solvents and spent solvent mixtures.
(I, T)
F006
Wastewater treatment sludges from electroplating operations except
from the following processes: (1) sulfuric acid anodizing of
aluminum; (2) tin plating on carbon steel; (3) zinc plating
(segregated basis) on carbon steel; (4) aluminum or zinc-aluminum
plating on carbon steel; (5) cleaning/stripping associated with tin,
zinc and aluminum plating on carbon steel; and (6) chemical
etching and milling of aluminum.
(T)
F019
See Below
F007
Spent cyanide plating bath solutions from electroplating operations.
(R, T)
F008
Plating bath residues from the bottom of plating baths from
electroplating operations where cyanides are used in the process.
(R, T)
F009
Spent stripping and cleaning bath solutions from electroplating
operations where cyanides are used in the process.
(R, T)
F010
Quenching bath residues from oil baths from metal heat treating
operations where cyanides are used in the process.
(R, T)
F011
Spent cyanide solutions from salt bath pot cleaning from metal heat
treating operations.
(R, T)
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F012
Quenching wastewater treatment sludges from metal heat treating
operations where cyanides are used in the process.
(T)
F019
Wastewater treatment sludges from the chemical conversion
coating of aluminum except from zirconium phosphating in
aluminum can washing when such phosphating is an exclusive
conversion coating process.
(T)
F020
Wastes (except wastewater and spent carbon from hydrogen
chloride purification) from the production or manufacturing use (as
a reactant, chemical intermediate or component in a formulating
process) of tri- or tetrachlorophenol, or of intermediates used to
produce their pesticide derivatives. (This listing does not include
wastes from the production of hexachlorophene from highly
purified 2,4,5-trichlorophenol.)
(H)
F021
Wastes (except wastewater and spent carbon from hydrogen
chloride purification) from the production or manufacturing use (as
a reactant, chemical intermediate or component in a formulating
process) of pentachlorophenol, or of intermediates used to produce
its derivatives.
(H)
F022
Wastes (except wastewater and spent carbon from hydrogen
chloride purification) from the manufacturing use (as a reactant,
chemical intermediate or component in a formulating process) of
tetra-, penta- or hexachlorobenzenes under alkaline conditions.
(H)
F023
Wastes (except wastewater and spent carbon from hydrogen
chloride purification) from the production of materials on
equipment previously used for the production or manufacturing use
(as a reactant, chemical intermediate or component in a
formulating process) of tri- and tetrachlorophenols. (This listing
does not include wastes from equipment used only for the
production or use of hexachlorophene from highly purified 2,4,5-
trichlorophenol.)
(H)
F024
Process wastes including but not limited to, distillation residues,
heavy ends, tars, and reactor cleanout wastes, from the production
of certain chlorinated aliphatic hydrocarbons by free radical
catalyzed processes. These chlorinated aliphatic hydrocarbons are
those having carbon chain lengths ranging from one to and
including five, with varying amounts and positions of chlorine
substitution. (This listing does not include wastewaters, wastewater
treatment sludges, spent catalysts and wastes listed in this Section
or Section 721.132.)
(T)
132
F025
Condensed light ends, spent filters and filter aids, and spent
desiccant wastes from the production of certain chlorinated
aliphatic hydrocarbons by free radical catalyzed processes. These
chlorinated aliphatic hydrocarbons are those having carbon chain
lengths ranging from one to and including five, with varying
amounts and positions of chlorine substitution.
(T)
F026
Wastes (except wastewater and spent carbon from hydrogen
chloride purification) from the production of materials on
equipment previously used for the manufacturing use (as a reactant,
chemical intermediate or component in a formulating process) of
tetra-, penta- or hexachlorobenzene under alkaline conditions.
(H)
F027
Discarded unused formulations containing tri-, tetra- or penta-
chlorophenol or discarded unused formulations containing
compounds derived from these chlorophenols. (This listing does
not include formulations containing hexachlorophene synthesized
from prepurified 2,4,5-trichlorophenol as the sole component).
(H)
F028
Residues resulting from the incineration or thermal treatment of
soil contaminated with hazardous waste numbers F020, F021,
F022, F023, F026 and F027.
(T)
F032
Wastewaters, (except those that have not come into contact with
process contaminants), process residuals, preservative drippage and
spent formulations from wood preserving processes generated at
plants that currently use or have previously used chlorophenolic
formulations (except potentially cross-contaminated wastes that
have had the F032 waste code deleted in accordance with Section
721.135 and where the generator does not resume or initiate use of
chlorophenolic formulations). This listing does not include K001
bottom sediment sludge from the treatment of wastewater from
wood preserving processes that use creosote or pentachlorophenol.
(T)
F034
Wastewaters, (except those that have not come into contact with
process contaminants), process residuals, preservative drippage and
spent formulations from wood preserving processes generated at
plants that use creosote formulations. This listing does not include
K001 bottom sediment sludge from the treatment of wastewater
from wood preserving processes that use creosote or pentachloro-
phenol.
(T)
133
F035
Wastewaters, (except those that have not come into contact with
process contaminants), process residuals, preservative drippage and
spent formulations from wood preserving processes generated at
plants that use inorganic preservatives containing arsenic or
chromium. This listing does not include K001 bottom sediment
sludge from the treatment of wastewater from wood preserving
processes that use creosote or pentachlorophenol.
(T)
F037
Petroleum refinery primary oil/water/solids separation sludge --
Any sludge generated from the gravitational separation of
oil/water/solids during the storage or treatment of process
wastewaters and oily cooling wastewaters from petroleum
refineries. Such sludges include, but are not limited to, those
generated in: oil/water/solids separators; tanks and impoundments;
ditches and other conveyances; sumps; and stormwater units
receiving dry weather flow. 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 generated in
aggressive biological treatment units as defined in subsection
(b)(2), below, (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.
(T)
F038
Petroleum refinery secondary (emulsified) oil/water/solids
separation sludge -- Any sludge or float generated from the
physical or chemical separation of oil/water/solids in process
wastewaters and oily cooling wastewaters from petroleum
refineries. Such wastes include, but are not limited to, all sludges
and floats generated in: 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 subsection (b)(2), below,
(including sludges and floats generated in one or more additional
units after wastewaters have been treated in aggressive biological
treatment units), F037, K048 and K051 wastes are not included in
this listing.
(T)
F039
Leachate (liquids which have percolated through land disposed
wastes) resulting from the disposal of more than one restricted
waste classified as hazardous under Subpart D. (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 number(s): F020, F021, F022, F026, F027 or
F028.)
(T)
134
BOARD NOTE: The primary hazardous properties of these materials have been indicated by
the letters T (Toxicity), R (Reactivity), I (Ignitability), and C (Corrosivity). The letter H
indicates Acute Hazardous Waste.
b)
Listing specific definitions.
1)
For the purpose of the F037 and F038 listings, oil/water/solids is defined as oil or
water or solids.
2)
For the purposes of the F037 and F038 listings:
A)
Aggressive biological treatment units are defined as units which employ one
of the following four treatment methods: activated sludge; trickling filter;
rotating biological contactor for the continuous accelerated biological
oxidation of wastewaters; or, high-rate aeration. High-rate aeration is a
system of surface impoundments or tanks, in which intense mechanical
aeration is used to completely mix the wastes, enhance biological activity,
and:
i)
The units employ a minimum of 6 horsepower per million gallons of
treatment volume; and either
ii)
The hydraulic retention time of the unit is no longer than 5 days; or
iii)
The hydraulic retention time is no longer than 30 days and the unit
does not generate a sludge that is a hazardous waste by the toxicity
characteristic.
B)
Generators and treatment, storage or disposal (TSD) facilities have the burden
of proving that their sludges are exempt from listing as F037 or F038 wastes
under this definition. Generators and TSD facilities shall maintain, in their
operating or other on site records, documents and data sufficient to prove
that:
i)
The unit is an aggressive biological treatment unit as defined in this
subsection; and
ii)
The sludges sought to be exempted from F037 or F038 were actually
generated in the aggressive biological treatment unit.
3)
Time of generation. For the purposes of:
A)
The F037 listing, sludges are considered to be generated at the moment of
deposition in the unit, where deposition is defined as at least a temporary
cessation of lateral particle movement.
B)
The F038 listing:
i)
Sludges are considered to be generated at the moment of deposition
in the unit, where deposition is defined as at least a temporary
cessation of lateral particle movement; and
135
ii)
Floats are considered to be generated at the moment they are formed
in the top of the unit.
(Source: Amended at 20 Ill. Reg. ________, effective ______________________)
Section 721.132
Hazardous Waste from Specific Sources
The following solid wastes are listed hazardous wastes from specific sources unless they are excluded under 35
Ill. Adm. Code 720.120 and 720.122 and listed in Section 721.Appendix I.
EPA 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 and/or pentachlorophenol.
(T)
Inorganic Pigments:
K002
Wastewater treatment sludge from the production of chrome yellow and
orange pigments.
(T)
K003
Wastewater treatment sludge from the production of molybdate orange
pigments.
(T)
K004
Wastewater treatment sludge from the production of zinc yellow pigments.
(T)
K005
Wastewater treatment sludge from the production of chrome green
pigments.
(T)
K006
Wastewater treatment sludge from the production of chrome oxide green
pigments (anhydrous and hydrated).
(T)
K007
Wastewater treatment sludge from the production of iron blue pigments.
(T)
K008
Oven residue from the production of chrome oxide green pigments.
(T)
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)
136
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 tetra-
chloride.
(T)
K017
Heavy ends (still bottoms) from the purification column in the production of
epichlorohydrin.
(T)
K018
Heavy ends from the fractionation column in ethyl chloride production.
(T)
K019
Heavy ends from the distillation of ethylene dichloride in ethylene
dichloride production.
(T)
K020
Heavy ends from the distillation of vinyl chloride in vinyl chloride
monomer production.
(T)
K021
Aqueous spent antimony catalyst waste from fluoromethanes production.
(T)
K022
Distillation bottom tars from the production of phenol/acetone from
cumene.
(T)
K023
Distillation light ends from the production of phthalic anhydride from
naphthalene.
(T)
K024
Distillation bottoms from the production of phthalic anhydride from
naphthalene.
(T)
K093
Distillation light ends from the production of phthalic anhydride from ortho-
xylene.
(T)
K094
Distillation bottoms from the production of phthalic anhydride from ortho-
xylene.
(T)
K025
Distillation bottoms from the production of nitrobenzene by the nitration of
benzene.
(T)
K026
Stripping still tails from the production of methyl ethyl pyridines.
(T)
K027
Centrifuge and distillation residues from toluene diisocyanate production.
(R,T)
K028
Spent catalyst from the hydrochlorinator reactor in the production of 1,1,1-
trichloroethane.
(T)
K029
Waste from the product stream stripper in the production of 1,1,1-trichloro-
ethane.
(T)
137
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-tri-
chloroethane.
(T)
K030
Column bottoms or heavy ends from the combined production of trichloro-
ethylene and perchloroethylene.
(T)
K083
Distillation bottoms from aniline production.
(T)
K103
Process residues from aniline extraction from the production of aniline.
(T)
K104
Combined wastewater streams generated from nitrobenzene/aniline
production.
(T)
K085
Distillation or fractionation column bottoms
from the production of chlorobenzenes.
(T)
K105
Separated aqueous stream from the reactor product washing step in the
production of chlorobenzenes.
(T)
K107
Column bottoms from product separation from the production of 1,1-di-
methylhydrazine (UDMH) from carboxylic acid hydrazides.
(C,T)
K108
Condensed column overheads from product separation and condensed
reactor vent gases from the production of 1,1-dimethylhydrazine (UDMH)
from carboxylic acid hydrazides.
(I,T)
K109
Spent filter cartridges from the product purification from the production of
1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.
(T)
K110
Condensed column overheads from intermediate separation from the
production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid
hydrazides.
(T)
K111
Product wastewaters from the production of dinitrotoluene via nitration of
toluene.
(C,T)
K112
Reaction by-product water from the drying column in the production of
toluenediamine via hydrogenation of dinitrotoluene.
(T)
K113
Condensed liquid light ends from the purification of toluenediamine in the
production of toluenediamine via hydrogenation of dinitrotoluene.
(T)
K114
Vicinals from the purification of toluene-diamine in the production of
toluenediamine via hydrogenation of dinitrotoluene.
(T)
K115
Heavy ends from the purification of toluenediamine in the production of
toluenediamine via hydrogenation of dinitrotoluene.
(T)
138
K116
Organic condensate from the solvent recovery column in the production of
toluene diisocyanate via phosgenation of toluenediamine.
(T)
K117
Wastewater from the reactor vent gas scrubber in the production of ethylene
dibromide via bromination of ethene.
(T)
K118
Spent adsorbent solids from purification of ethylene dibromide in the
production of ethylene dibromide via bromination of ethene.
(T)
K136
Still bottoms from the purification of ethylene dibromide in the production
of ethylene dibromide via bromination of ethene.
(T)
K156
Organic waste (including heavy ends, still bottoms, light ends, spent
solvents, filtrates, and decantates) from the production of carbamates and
carbamoyl oximes.
(T)
K157
Wastewaters (including scrubber waters, condenser waters, washwaters, and
separation waters) from the production of carbamates and carbamoyl
oximes.
(T)
K158
Bag house dusts and filter/separation solids from the production of
carbamates and carbamoyl oximes.
(T)
K159
Organics from the treatment of thiocarbamate wastes.
(T)
K160
Solids (including filter wastes, separation solids, and spent catalysts) from
the production of thiocarbamates and solids 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)
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)
139
K032
Wastewater treatment sludge from the production of chlordane.
(T)
K033
Wastewater and scrub water from the chlorination of cyclopentadiene in the
production of chlordane.
(T)
K034
Filter solids from the filtration of hexachlorocyclopentadiene in the
production of chlordane.
(T)
K097
Vacuum stripper discharge from the chlordane chlorinator in the production
of chlordane.
(T)
K035
Wastewater treatment sludges generated in the production of creosote.
(T)
K036
Still bottoms from toluene reclamation distillation in the production of di-
sulfoton.
(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 tetrachloro-
benzene in the production of 2,4,5-T.
(T)
K043
2,6-Dichlorophenol waste from the production of 2,4-D.
(T)
K099
Untreated wastewater from the production of 2,4-D.
(T)
K123
Process wastewater (including supernates, filtrates and washwaters) from
the production of ethylenebisdithiocarbamic acid and its salts.
(T)
K124
Reactor vent scrubber water from the production of ethylenebisdi-
thiocarbamic acid and its salts.
(C,T)
K125
Filtration, evaporation and centrifugation solids from the production of
ethylenebisdithiocarbamic acid and its salts.
(T)
K126
Baghouse dust and floor sweepings in milling and packaging operations
from the production or formulation of ethylenebisdithiocarbamic acid and its
salts.
(T)
140
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)
K052
Tank bottoms (leaded) from the petroleum refining industry.
(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)
141
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 RCRA
Act, 42 U.S.C. 6926(b), the Board RCRA rules become "less stringent"
than the USEPA rules, as this phrase is used in Section 3009, 42 U.S.C.
6929, or the Board RCRA rules are not "identical in substance" with the
federal rules as that term is intended by Ill. Rev. Stat. 1991 ch. 111½, pars.
1007.2 and 1022.4 [415 ILCS 5/7.2 and 5/22.4] 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 organoarsenic
compounds.
(T)
K102
Residue from use of activated carbon for decolorization in the production of
veterinary pharmaceuticals from arsenic or organo-arsenic compounds.
(T)
142
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, driers, 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 alpha- (or methyl-) chlorinated
toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with
mixtures of these functional groups,. (This waste does not include still
bottoms from the distillation of benzyl chloride.).
(T)
K150
Organic residuals, excluding spent carbon adsorbent, from the spent
chlorine gas and hydrochloric acid recovery processes associated with the
production of alpha- (or methyl-) chlorinated toluenes, ring-chlorinated
toluenes, benzoyl chlorides, and compounds with mixtures of these
functional groups.
(T)
143
K151
Wastewater treatment sludges, excluding neutralization and biological
sludges, generated during the treatment of wastewaters from the production
of alpha- (or methyl-) chlorinated toluenes, ring-chlorinated toluenes,
benzoyl chlorides, and compounds with mixtures of these functional groups.
(T)
(Source: Amended at 20 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 subsections (e) or (f) below.
b)
Any off-specification commercial chemical product or manufacturing chemical intermediate
which, if it met specifications, would have the generic name listed in subsections (e) or (f)
below.
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) below, 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 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) below, 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, if it met specifications, would have the generic name listed in subsection
(e) or (f) below.
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.
144
It does not refer to a material, such as a manufacturing process waste, that contains any of the
substances listed in subsections (e) or (f) below. Where a manufacturing process waste is
deemed to be a hazardous waste because it contains a substance listed in subsections (e) or (f)
below, 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.
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) above, 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 EPA Hazardous Waste Numbers are:
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 listed for acute
toxicity.
145
Hazardous
Waste No.
Chemical
Abstracts No.
Substance
P023
107-20-0
Acetaldehyde, chloro-
P002
591-08-2
Acetamide, N-(aminothioxomethyl)
P057
640-19-7
Acetamide, 2-fluoro-
P058
62-74-8
Acetic acid, fluoro-, sodium salt
P002
591-08-2
1-Acetyl-2-thiourea
P003
107-02-8
Acrolein
P070
116-06-3
Aldicarb
P203
1646-88-4
Aldicarb sulfone
P004
309-00-2
Aldrin
P005
107-18-6
Allyl alcohol
P006
20859-73-8
Aluminum phosphide (R,T)
P007
2763-96-4
5-(Aminomethyl)-3-isoxazolol
P008
504-24-5
4-Aminopyridine
P009
131-74-8
Ammonium picrate (R)
P119
7803-55-6
Ammonium vanadate
P099
506-61-6
Argentate(1-), bis(cyano-C)-, potassium
P010
7778-39-4
Arsenic acid 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, alpha,alpha-dimethyl-
P014
108-98-5
Benzenethiol
P127
1563-66-2
7-Benzofuranol, 2,3-dihydro-2,2-dimethyl-,
methylcarbamate
P188
57-64-7
Benzoic acid, 2-hydroxy-, compound with (3aS-cis)-
1,2,3,3a,8,8a-hexahydro-1,3a,8-trimethylpyrrolo[2,3-b]-
indol-5-yl methylcarbamate ester (1:1)
P001
P81-81-2
*
2H-1-Benzopyran-2-one, 4-hydroxy-3-(3-oxo-1-
phenylbutyl)-, and salts, when present at concentrations
greater than 0.3%
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-[methyl-
amino)carbonyl] oxime
146
P021
592-01-8
Calcium cyanide
P021
592-01-8
Calcium cyanide Ca(CN)
2
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-methylethyl)-
1H-pyrazol-5-yl ester
P190
1129-41-5
Carbamic acid, methyl-, 3-methylphenyl ester
P127
1563-66-2
Carbofuran
P022
75-15-0
Carbon disulfide
P095
75-44-5
Carbonic dichloride
P189
55285-14-8
Carbosulfan
P023
107-20-0
Chloroacetaldehyde
147
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-hexa-
chloro-1,4,4a,5,8,8a-hexahydro-,
(1alpha,4alpha,4abeta,5alpha,8alpha,8abeta)-
P060
465-73-6
1,4,5,8-Di-methanonaphthalene, 1,2,3,4,10,10-hexa-
chloro-1,4,4a,5,8,8a-hexahydro-,
(1alpha,4alpha,4abeta,5beta,8beta,8abeta)-
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-,
(1aalpha,2beta,2aalpha,3beta,6beta,6aalpha,7beta,7aalph
a)-
P051
P72-20-8
*
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-,
(1aalpha,2beta,2abeta,3alpha,6alpha,6abeta,7beta,7aalph
a)-, and metabolites
P044
60-51-5
Dimethoate
P046
122-09-8
alpha,alpha-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-[[(methyl-
148
amino)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-
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-[[(methyl-
amino)-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-hexahydro-, 3-oxide
P059
76-44-8
4,7-Methano-1H-indene, 1,4,5,6,7,8,8-heptachloro-
3a,4,7,7a-tetrahydro-
P066
16752-77-5
Methomyl
P068
60-34-4
Methyl hydrazine
P064
624-83-9
Methyl isocyanate
149
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
alpha-Naphthylthiourea
P073
13463-39-3
Nickel carbonyl
P073
13463-39-3
Nickel carbonyl Ni(CO)
4
, (T-4)-
P074
557-19-7
Nickel cyanide
150
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
P034
131-89-5
Phenol, 2-cyclohexyl-4,6-dinitro-
P128
315-18-4
Phenol, 4-(dimethylamino)-3,5-dimethyl-, methyl-
carbamate (ester)
P199
2032-65-7
Phenol, (3,5-dimethyl-4-(methylthio)-, methylcarbamate
P048
51-28-5
Phenol, 2,4-dinitro-
P047
P534-52-1
*
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)-
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-(ethylthio)-
ethyl] ester
P094
298-02-2
Phosphorodithioic acid, O,O-diethyl S-[(ethylthio)-
methyl] ester
P044
60-51-5
Phosphorodithioic acid, O,O-dimethyl S-[2-(methyl-
amino)-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
151
P099
506-61-6
Potassium silver cyanide
P201
2631-37-0
Promecarb
P203
1646-88-4
Propanal, 2-methyl-2-(methyl-sulfonyl)-, O-[(methyl-
amino)carbonyl] oxime
P070
116-06-3
Propanal, 2-methyl-2-(methylthio)-, O-[(methylamino)-
carbonyl]oxime
P101
107-12-0
Propanenitrile
P027
542-76-7
Propanenitrile, 3-chloro-
P069
75-86-5
Propanenitrile, 2-hydroxy-2-methyl-
P081
55-63-0
1,2,3-Propanetriol, trinitrate- (R)
P017
598-31-2
2-Propanone, 1-bromo-
P102
107-19-7
Propargyl alcohol
P003
107-02-8
2-Propenal
P005
107-18-6
2-Propen-1-ol
P067
75-55-8
1,2-Propylenimine
P102
107-19-7
2-Propyn-1-ol
P008
504-24-5
4-Pyridinamine
P075
P54-11-5
*
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-hexahydro-
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
P57-24-9
*
Strychnidin-10-one, and salts
P018
357-57-3
Strychnidin-10-one, 2,3-dimethoxy-
P108
P57-24-9
*
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
P118
75-70-7
Trichloromethanethiol
152
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
P81-81-2
*
Warfarin, and salts, when present at concentrations
greater than 0.3%.
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% (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) above, 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 EPA Hazardous
Waste Numbers are:
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.
Hazardous
Waste No.
Chemical
Abstracts No.
Substance
U394
30558-43-1
A2213
U365
2212-67-1
H-Azepine-1-carbothioic acid, hexahydro-, S-ethyl ester
U001
75-07-0
Acetaldehyde (I)
U034
75-87-6
Acetaldehyde, trichloro-
153
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)-
UOO2
67-64-1
Acetone (I)
UOO3
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-
(1aalpha,8beta,8aalpha,8balpha)]-
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-dimethyl-
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-alpha-(4-chlorophenyl)-
alpha-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-
U028
117-81-7
1,2-Benzenedicarboxylic acid, bis(2-ethylhexyl) ester
154
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
U248
P 81-81-2
2H-1-Benzopyran-2-one, 4-hydroxy-3-(3-oxo-1-phenyl-
butyl)-, and salts, when present at concentrations of
0.3% 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-
U401
97-74-5
Bis(dimethylthiocarbamoyl) sulfide
U400
120-54-7
Bis(pentamethylene)thiuram tetrasulfide
U225
75-25-2
Bromoform
155
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-[1alpha(Z),
7(2S*,3R*), 7aalpha]]-
U031
71-36-3
n-Butyl alcohol (I)
U392
2008-41-5
Butylate
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-benzimid-
azol-2-yl]-, methyl ester
U375
55406-53-6
Carbamic acid, butyl-, 3-iodo-2-propynyl 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(iminocarbonothioyl)]-
bis-, dimethyl ester
U097
79-44-7
Carbamic chloride, dimethyl-
U379
136-30-1
Carbamodithioic acid, dibutyl, sodium salt
U277
95-06-7
Carbamodithioic acid, diethyl-, 2-chloro-2-propenyl
ester
U381
148-18-5
Carbamodithioic acid, diethyl-, sodium salt
U383
128-03-0
Carbamodithioic acid, dimethyl, potassium salt
U382
128-04-1
Carbamodithioic acid, dimethyl-, sodium salt
U376
144-34-3
Carbamodithioic acid, dimethyl-, tetraanhydrosulfide
with orthothioselenious acid
U114
P 111-54-6
Carbamodithioic acid, 1,2-ethanediylbis-, salts and esters
U378
51026-28-9
Carbamodithioic acid, (hydroxymethyl)methyl-, mono-
potassium salt
U384
137-42-8
Carbamodithioic acid, methyl-, monosodium salt
U377
137-41-7
Carbamodithioic acid, methyl,- monopotassium salt
U062
2303-16-4
Carbamothioic acid, bis(1-methylethyl)-, S-(2,3-di-
chloro-2-propenyl) ester
U389
2303-17-5
Carbamothioic acid, bis(1-methylethyl)-, S-(2,3,3-tri-
chloro-2-propenyl) ester
U392
2008-41-5
Carbamothioic acid, bis(2-methylpropyl)-, S-ethyl ester
U391
1114-71-2
Carbamothioic acid, butylethyl-, S-propyl ester
U386
1134-23-2
Carbamothioic acid, cyclohexylethyl-, S-ethyl ester
U390
759-94-4
Carbamothioic acid, dipropyl-, S-ethyl ester
U387
52888-80-9
Carbamothioic acid, dipropyl-, S-(phenylmethyl) ester
U385
1929-77-7
Carbamothioic acid, dipropyl-, S-propyl ester
156
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
Chlordanealpha and gamma 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
beta-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
U393
137-29-1
Copper, bis(dimethylcarbamodithioato-S,S')-
U393
137-29-1
Copper dimethyldithiocarbamate
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
U386
1134-23-2
Cycloate
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-,
(1alpha,2alpha,3beta,4alpha,5alpha,6beta)-
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
U366
533-74-4
Dazomet
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
U069
84-74-2
Dibutyl phthalate
U070
95-50-1
o-Dichlorobenzene
U071
541-73-1
m-Dichlorobenzene
U072
106-46-7
p-Dichlorobenzene
157
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
alpha, alpha-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
U403
97-77-8
Disulfiram
U041
106-89-8
Epichlorohydrin
U390
759-94-4
EPTC
U001
75-07-0
Ethanal (I)
U404
121-44-8
Ethanamine, N,N-diethyl-
U174
55-18-5
Ethanamine, N-ethyl-N-nitroso-
U155
91-80-5
1,2-Ethanediamine, N,N-dimethyl-N'-2-pyridinyl-N'-(2-
thienylmethyl)-
U067
106-93-4
Ethane, 1,2-dibromo-
U076
75-34-3
Ethane, 1,1-dichloro-
U077
107-06-2
Ethane, 1,2-dichloro-
U131
67-72-1
Ethane, hexachloro-
158
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[(methylimino)-
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
U407
14324-55-1
Ethyl Ziram
U396
14484-64-1
Ferbam
U120
206-44-0
Fluoranthene
U122
50-00-0
Formaldehyde
U123
64-18-6
Formic acid (C,T)
U124
110-00-9
Furan (I)
U125
98-01-1
2-Furancarboxaldehyde (I)
U147
108-31-6
2,5-Furandione
U213
109-99-9
Furan, tetrahydro- (I)
U125
98-01-1
Furfural (I)
U124
110-00-9
Furfuran (I)
U206
18883-66-4
Glucopyranose, 2-deoxy-2-(3-methyl-3-nitrosoureido)-,
D-
U206
18883-66-4
D-Glucose, 2-deoxy-2-[[(methylnitrosoamino)-carbonyl]-
amino]-
159
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
U375
55406-53-6
3-Iodo-2-propynyl n-butylcarbamate
U396
14484-64-1
Iron, tris(dimethylcarbamodithioato-S,S')-
U190
85-44-9
1,3-Isobenzofurandione
U140
78-83-1
Isobutyl alcohol (I,T)
U141
120-58-1
Isosafrole
U142
143-50-0
Kepone
U143
303-34-4
Lasiocarpene
U144
301-04-2
Lead acetate
U146
1335-32-6
Lead, bis(acetato-O)tetrahydroxytri-
U145
7446-27-7
Lead phosphate
U146
1335-32-6
Lead subacetate
U129
58-89-9
Lindane
U163
70-25-7
MNNG
U147
108-31-6
Maleic anhydride
U148
123-33-1
Maleic hydrazide
U149
109-77-3
Malononitrile
U150
148-82-3
Melphalan
U151
7439-97-6
Mercury
U384
137-42-8
Metam Sodium
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)
160
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
U365
2212-67-1
Molinate
U059
20830-81-3
5,12-Naphthacenedione, 8-acetyl-10-[(3-amino-2,3,6-tri-
deoxy)-alpha-L-lyxo-hexapyranosyl)oxyl]-7,8,9,10-tetra-
hydro-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'-dimethyl-
[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
alpha-Naphthylamine
U168
91-59-8
beta-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
161
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-chloro-
ethyl)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
U391
1114-71-2
Pebulate
U183
608-93-5
Pentachlorobenzene
U184
76-01-7
Pentachloroethane
U185
82-68-8
Pentachloronitrobenzene (PCNB)
See F027
87-86-5
Pentachlorophenol
U161
108-10-1
Pentanol, 4-methyl-
U186
504-60-9
1,3-Pentadiene (I)
U187
62-44-2
Phenacetin
U188
108-95-2
Phenol
U048
95-57-8
Phenol, 2-chloro-
U039
59-50-7
Phenol, 4-chloro-3-methyl-
U081
120-83-2
Phenol, 2,4-dichloro-
U082
87-65-0
Phenol, 2,6-dichloro-
U089
56-53-1
Phenol, 4,4'-(1,2-diethyl-1,2-ethenediyl)bis-, (E)-
U101
105-67-9
Phenol, 2,4-dimethyl-
U052
1319-77-3
Phenol, methyl-
U132
70-30-4
Phenol, 2,2'-methylenebis[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-
U400
120-54-7
Piperidine, 1,1'-(tetrathiodicarbonothioyl)-bis-
U383
128-03-0
Potassium dimethyldithiocarbamate
U378
51026-28-9
Potassium n-hydroxymethyl-n-methyldi-thiocarbamate
U377
137-41-7
Potassium n-methyldithiocarbamate
U192
23950-58-5
Pronamide
U194
107-10-8
1-Propanamine (I,T)
U111
621-64-7
1-Propanamine, N-nitroso-N-propyl-
162
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
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-chloroethyl)-
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)
U376
144-34-3
Selenium, tetrakis(dimethyldithiocarbamate)
U015
115-02-6
L-Serine, diazoacetate (ester)
See F027
93-72-1
Silvex (2,4,5-TP)
U379
136-30-1
Sodium dibutyldithiocarbamate
U381
148-18-5
Sodium diethyldithiocarbamate
U382
128-04-1
Sodium dimethyldithiocarbamate
U206
18883-66-4
Streptozotocin
U277
95-06-7
Sulfallate
U103
77-78-1
Sulfuric acid, dimethyl ester
U189
1314-80-3
Sulfur phosphide (R)
163
See F027
93-76-5
2,4,5-T
U402
1634-02-2
Tetrabutylthiuram disulfide
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)
U401
97-74-5
Tetramethylthiuram monosulfide
U366
533-74-4
2H-1,3,5-Thiadiazine- 2-thione, tetrahydro-3,5-dimethyl-
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)
U402
1634-02-2
Thioperoxydicarbonic diamide, tetrabutyl
U403
97-77-8
Thioperoxydicarbonic diamide, tetraethyl
U244
137-26-8
Thioperoxydicarbonic diamide [(H
2
N)C(S)]
2
S
2
, tetra-
methyl-
U409
23564-05-8
Thiophanate-methyl
U219
62-56-6
Thiourea
U244
137-26-8
Thiram
U220
108-88-3
Toluene
U221
25376-45-8
Toluenediamine
U223
26471-62-5
Toluene diisocyanate (R,T)
U328
95-53-4
o-Toluidine
U353
106-49-0
p-Toluidine
U222
636-21-5
o-Toluidine hydrochloride
U389
2303-17-5
Triallate
U011
61-82-5
1H-1,2,4-Triazol-3-amine
U227
79-00-5
1,1,2-Trichloroethane
U228
79-01-6
Trichloroethylene
U121
75-69-4
Trichloromonofluoromethane
See F027
95-95-4
2,4,5-Trichlorophenol
See F027
88-06-2
2,4,6-Trichlorophenol
U404
121-44-8
Triethylamine
U234
99-35-4
1,3,5-Trinitrobenzene (R,T)
U182
123-63-7
1,3,5-Trioxane, 2,4,6-trimethyl-
U235
126-72-7
Tris(2,3-dibromopropyl) phosphate
U236
72-57-1
Trypan blue
U237
66-75-1
Uracil mustard
U176
759-73-9
Urea, N-ethyl-N-nitroso-
U177
684-93-5
Urea, N-methyl-N-nitroso-
U385
1929-77-7
Vernolate
U043
75-01-4
Vinyl chloride
U248
P 81-81-2
Warfarin, and salts, when present at concentrations of
0.3% or less
U239
1330-20-7
Xylene (I)
164
U200
50-55-5
Yohimban-16-carboxylic acid, 11,17-dimethoxy-18-
[(3,4,5-trimethoxybenzoyl)oxy]-, methyl ester,
(3beta,16beta,17alpha,18beta,20alpha)-
U407
14324-55-1
Zinc, bis(diethylcarbamodithioato-S,S')-
U249
1314-84-7
Zinc phosphide Zn
3
P
2
, when present at concentrations of
10% or less
(Source: Amended at 20 Ill. Reg. ________, effective ______________________)
Section 721.Appendix G
Basis for Listing Hazardous Wastes
EPA
hazardous
waste No.
Hazardous constituents for which listed
F001
Tetrachloroethylene, methylene chloride, trichloroethylene, 1,1,1-trichloroethane, carbon tetrachloride,
chlorinated fluorocarbons.
F002
Tetrachloroethylene, methylene chloride, trichloroethylene, 1,1,1-trichloroethane, 1,1,2-trichlorethane,
chlorobenzene, 1,1,2-trichloro-1,2,2-trifluoroethane, ortho-dichlorobenzene, trichlorofluoromethane.
F003
N.A.
F004
Cresols and cresylic acid, nitrobenzene.
F005
Toluene, methyl ethyl ketone, carbon disulfide, isobutanol, pyridine, 2-ethoxyethanol, benzene, 2-
nitropropane.
F006
Cadmium, hexavalent chromium, nickel, cyanide (complexed).
F007
Cyanide (salts).
F008
Cyanide (salts).
F009
Cyanide (salts).
F010
Cyanide (salts).
F011
Cyanide (salts).
F012
Cyanide (complexed).
F019
Hexavalent chromium, cyanide (complexed).
F020
Tetra- and pentachlorodibenzo-p-dioxins; tetra- and pentachlorodibenzofurans; tri- and
tetrachlorophenols and their clorophenoxy derivative acids, esters, ethers, amines and other salts.
F021
Penta- and hexachlorodibenzo-p-dioxins; penta- and hexachlorodibenzofurans; pentachlorophenol and
its derivatives.
F022
Tetra-, penta- and hexachlorodibenzo-p-dioxins; tetra-, penta- and hexachlorodibenzofurans.
F023
Tetra- and pentachlorodibenzo-p-dioxins; tetra- and pentachlorodibenzofurans; tri- and tetra-
chlorophenols and their chlorophenoxy derivative acids, esters, ethers, amines and other salts.
F024
Chloromethane, dichloromethane, trichloromethane, carbon tetrachloride, chloroethylene, 1,1-
dichloroethane, 1,2-dichloroethane, trans-1,2-dichloroethylene, 1,1-dichloroethylene, 1,1,1-
trichloroethane, 1,1,2-trichloroethane, trichloroethylene, 1,1,1,2-tetrachloroethane, 1,1,2,2-
tetrachloroethane, tetrachloroethylene, pentachloroethane, hexachloroethane, allyl chloride (3-
chloropropene), dichloropropane, dichloropropene, 2-chloro-1,3-butadiene, hexachloro-1,3-butadiene,
hexachlorochylopentadiene, hexachlorocylohexane, benzene, chlorobenzene, dichlorobenzenes, 1,2,4-
trichlorobenzene, tetrachlorobenzenes, pentachlorobenzene, hexachlorobenzene, toluene, naphthalene.
F025
Chloromethane, dicloromethane, trichloromethane; carbon tetrachloride; chloroethylene; 1,1-
dichloroethane; 1,2-dichloroethane; trans-1,2-dichloroethylene; 1,1-dichloroethylene; 1,1,1-
trichloroethane; 1,1,2-trichloroethane; trichloroethylene; 1,1,1,2-tetrachloroethane; 1,1,2,2-
tetrachloroethane; tetrachloroethylene; pentachloroethane; hexachloroethane; allyl chloride (3-
chloropropene); dichloropropane; dichloropropene; 2-chloro-1,3-butadiene; hexachloro-1,3-butadiene;
165
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-dixons;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.
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, tetrachloro-ethanes (1,1,2,2-
tetrachloroethane and 1,1,1,2-tetrachloroethane), trichloroethylene, tetrachloroethylene, carbon
tetrachloride, chloroform, vinyl chloride, vinylidene chloride.
K021
Antimony, carbon tetrachloride, chloroform.
K022
Phenol, tars (polycyclic aromatic hydrocarbons).
K023
Phthalic anhydride, maleic anhydride.
K024
Phthalic anhydride, 1,4-naphthoguinone.
K025
Meta-dinitrobenzene, 2,4-dinitrotoluene.
K026
Paraldehyde, pyridines, 2-picoline.
166
K027
Toluene diisocyanate, toluene-2,4-diamine.
K028
1,1,1-trichloroethane, vinyl chloride.
K029
1,2-dichloroethane, 1,1,1-trichloroethane, vinyl chloride, vinylidene chloride, chloroform.
K030
Hexachlorobenzene, hexachlorobutadiene, hexachloroethane, 1,1,1,2-tetrachloroethane, 1,1,2,2-
tetrachloroethane, ethylene dichloride.
K031
Arsenic.
K032
Hexachlorocyclopentadiene.
K033
Hexachlorocyclopentadiene.
K034
Hexachlorocyclopentadiene.
K035
Creosote, chrysene, naphthalene, fluoranthene, benzo(b) fluoranthene, benzo(a)-pyrene, indeno(1,2,3-
cd) pyrene, benzo(a)anthracene, dibenzo(a)anthracene, acenaphthalene.
K036
Toluene, phosphorodithioic and phosphorothioic acid esters.
K037
Toluene, phosphorodithioic and phosphorothioic acid esters.
K038
Phorate, formaldehyde, phosphorodithioic and phosphorothioic acid esters.
K039
Phosphorodithioic and phosphorothioic acid esters.
K040
Phorate, formaldehyde, phosphorodithioic and phosphorothioic acid esters.
K041
Toxaphene.
K042
Hexachlorobenzene, ortho-dichlorobenzene.
K043
2,4-dichlorophenol, 2,6-dichlorophenol, 2,4,6-trichlorophenol.
K044
N.A.
K045
N.A.
K046
Lead.
K047
N.A.
K048
Hexavalent chromium, lead.
K049
Hexavalent chromium, lead.
K050
Hexavalent chromium.
K051
Hexavalent chromium, lead.
K052
Lead.
K060
Cyanide, naphthalene, phenolic compounds, arsenic.
K061
Hexavalent chromium, lead, cadmium.
K062
Hexavalent chromium, lead.
K064
Lead, cadmium.
K065
Lead, cadmium.
K066
Lead, cadmium.
K069
Hexavalent chromium, lead, cadmium.
K071
Mercury.
K073
Chloroform, carbon tetrachloride, hexachloroethane, trichloroethane, tetrachloroethylene,
dichloroethylene, 1,1,2,2-tetrachloroethane.
K083
Aniline, diphenylamine, nitrobenzene, phenylenediamine.
K084
Arsenic.
K085
Benzene, dichlorobenzenes, trichlorobenzenes, tetrachlorobenzenes, pentachlorobenzene,
hexachlorobenzene, benzyl chloride.
K086
Lead, hexavalent chromium.
K087
Phenol, naphthalene.
K088
Cyanide (complexes).
K090
Chromium.
K091
Chromium.
K093
Phthalic anhydride, maleic anhydride.
K094
Phthalic anhydride.
K095
1,1,2-trichloroethane, 1,1,1,2-tetrachloroethane, 1,1,2,2-tetrachloroethane.
K096
1,2-dichloroethane, 1,1,1-trichloroethane, 1,1,2-trichloroethane.
167
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 Ttetrachloride, tetrachloroethylene, chloroform, phosgene.
K117
Ethylene dibromide.
K118
Ethylene dibromide.
K123
Ethylene thiourea.
K124
Ethylene thiourea.
K125
Ethylene thiourea.
K126
Ethylene thiourea.
K131
Dimethyl sulfate, methyl bromide.
K132
Methyl bromide.
K136
Ethylene dibromide.
K141
Benzene, benz(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, benzo(k)fluoranthene,
dibenz(a,h)anthracene, indeno(1,2,3-cd)pyrene.
K142
Benzene, benz(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, benzo(k)fluoranthene,
dibenz(a,h)anthracene, indeno(1,2,3-cd)pyrene.
K143
Benzene, benz(a)anthracene, benzo(b)fluoranthene, benzo(k)fluoranthene.
K144
Benzene, benz(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, benzo(k)fluoranthene,
dibenz(a,h)anthracene.
K145
Benzene, benz(a)anthracene, benzo(a)pyrene, dibenz(a,h)anthracene, naphthalene.
K147
Benzene, benz(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, benzo(k)fluoranthene,
dibenz(a,h)anthracene, indeno(1,2,3-cd)pyrene.
K148
Benz(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, benzo(k)fluoranthene,
dibenz(a,h)anthracene, indeno(1,2,3-cd)pyrene.
K149
Benzotrichloride, benzyl chloride, chloroform, chloromethane, chlorobenzene, 1,4-dichlorobenzene,
hexachlorobenzene, pentachlorobenzene, 1,2,4,5-tetrachlorobenzene, toluene.
K150
Carbon tetrachloride, chloroform, chloromethane, 1,4-dichlorobenzene, hexachlorobenzene,
pentachlorobenzene, 1,2,4,5-tetrachlorobenzene, 1,1,2,2-tetrachloroethane, tetrachloroethylene, 1,2,4-
trichlorobenzene.
K151
Benzene, carbon tetrachloride, chloroform, hexachlorobenzene, pentachlorobenzene, toluene, 1,2,4,5-
tetrachlorobenzene, tetrachloroethylene.
K156
Benomyl, carbaryl, carbendazim, carbofuran, carbosulfan, formaldehyde, methylene chloride,
triethylamine.
K157
Carbon tetrachloride, formaldehyde, methyl chloride, methylene chloride, pyridine, triethylamine.
K158
Benomyl, carbendazim, carbofuran, carbosulfan, chloroform, methylene chloride.
K159
Benzene, butylate, EPTC, molinate, pebulate, vernolate.
K160
Benzene, butylate, EPTC, molinate, pebulate, vernolate.
K161
Antimony, arsenic, metam-sodium, ziram.
168
N.A.--Waste is hazardous because it fails the test for the
characteristic of ignitability, corrosivity or reactivity.
(Source: Amended at 20 Ill. Reg. ________, effective ______________________)
Section 721.Appendix H Hazardous Constituents
Common Name
Chemical Abstracts Name
Chemical
Abstracts
Number
Hazard-
ous
Waste
Number
A2213
Ethanimidothioic acid, 2- (dimethyl-
amino)-N-hydroxy-2-oxo-, methyl
ester
30558-43-1
U394
169
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
UOO5
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-alpha,4-
alpha,4a-beta,5-alpha,8-alpha,8a-
beta)-
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-(aminomethyl)-
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
PO11
Arsenic trioxide
Arsenic oxide As
2
O
3
1327-53-3
P012
Auramine
Benzenamine, 4,4'-carbonimidoyl-
bis[N, N-dimethyl-
492-80-8
U014
Azaserine
L-Serine, diazoacetate (ester)
115-02-6
U015
Barban
Carbamic acid, (3-chlorophenyl)-,
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
170
Benomyl
Carbamic acid, [1- [(butylamino)-
carbonyl]-1H-benzimidazol-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'-(tetrathiodicarbono-
thioyl)-bis-
120-54-7
U400
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-methyl-
propyl)-, S-ethyl ester
2008-41-5
U392
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
Carbaryl
1-Naphthalenol, methylcarbamate
63-25-2
U279
Carbendazim
Carbamic acid, 1H-benzimidazol-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-
57-74-9
U036
171
2,3,3a,4,7,7a-hexahydro-
Chlordane, alpha and gamma 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-chloro-
ethyl)-
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-alpha-
(4-chlorophenyl)-alpha-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
beta-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
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-dimethoxy-
phenyl)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
U393
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
Beta-D-glucopyranoside, (methyl-
ONN-azoxy)methyl-
14901-08-7
Cycloate
Carbamothioic acid, cyclohexyl-
ethyl-, S-ethyl ester
1134-23-2
U386
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-chloroethyl)tetrahydro-, 2-
50-18-0
U058
172
oxide
2,4-D
Acetic acid, (2,4-dichlorophenoxy)-
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-alpha-L-
lyxo-hexopyranosyl)oxy]-7,8,9,10-
tetrahydro-6,8,11-trihydroxy-l-meth-
oxy-, 8S-cis)-
20830-81-3
U059
Dazomet
2H-1,3,5-thiadiazine-2-thione, tetra-
hydro-3,5-dimethyl
533-74-4
U366
DDD
Benzene, 1,1'-(2,2-dichloroethyl-
idene)bis[4-chloro-
72-54-8
U060
DDE
Benzene, 1,1'-(dichloroethenyl-
idene)bis[4-chloro-
72-55-9
DDT
Benzene, 1,1'-(2,2,2-trichloro-
ethylidene)bis[4-chloro-
50-29-3
U061
Diallate
Carbamothioic acid, bis(1-methyl-
ethyl)-, 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
173
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]oxi-
rene,3,4,5,6,9,9-hexachloro-
1a,2,2a,3,6, 6a,7,7a-octahydro-,
(1aalpha,2beta,2aalpha,3beta,6beta,6
aalpha,7beta,7aalpha)-
60-57-1
P037
1,2:3,4-Diepoxybutane
2,2'-Bioxirane
1464-53-5
U085
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 dithiophosphate
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-ethene-
diyl)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
alpha,alpha-Dimethylphenethylamine
Benzeneethanamine, alpha, alpha-
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
4,6-Dinitro-o-cresol salts
P047
174
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
U403
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-benzodioxathie-
pen,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-di-
carboxylic acid
145-73-3
P088
Endrin
2,7:3,6-Dimethanonaphth[2,3-b]oxi-
rene, 3,4,5,6,9,9-hexachloro-
1a,2,2a,3,6,6a,7,7a-octahydro-, (1a
alpha,2beta,2abeta,3alpha,6alpha,6ab
eta,7beta,7aalpha)-,
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
U390
Ethyl carbamate (urethane)
Carbamic acid, ethyl ester
51-79-6
U238
Ethyl cyanide
Propanenitrile
107-12-0
P101
Ethylenebisdithiocarbamic acid
Carbamodithioic acid, 1,2-ethane-
diylbis-
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
U077
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-
52-85-7
P097
175
[(dimethylamino)sulfonyl]phenyl]
O,O-dimethyl ester
Ferbam
Iron, tris(dimethylcarbamo-
dithioato-S,S')-,
14484-64-1
U396
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]-, monohydrochloride
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-tetrahydro-
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-hexahydro-,
(1aalpha,1bbeta,2alpha,5alpha,5abeta
,6beta,6aalpha)-
1024-57-3
Heptachlor epoxide (alpha, beta, and
gamma isomers)
Heptachlorodibenzofurans
Heptachlorodibenzo-p-dioxins
Hexachlorobenzene
Benzene, hexachloro-
118-74-1
U127
Hexachlorobutadiene
1,3-Butadiene, 1,1,2,3,4,4-hexa-
chloro-
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'-methylenebis[3,4,6-tri-
chloro-
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 H2S
7783-06-4
U135
Indeno[1,2,3-cd]pyrene
Same
193-39-5
U137
3-Iodo-2-propynyl-n-butylcarbamate
Carbamic acid, butyl-, 3-iodo-2-
propynyl ester
55406-53-6
U375
Isobutyl alcohol
1-Propanol, 2-methyl-
78-83-1
U140
Isodrin
1,4:5,8-Dimethanonaph-
465-73-6
P060
176
thalene,1,2,3,4,10,10-hexachloro-
1,4,4a,5,8,8a-hexahydro-,
(1alpha,4alpha,4abeta,5beta,8beta,8a
beta)-,
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-
alpha(Z),7(2S*,3R*),7aalpha]]-
303-34-1
U143
Lead
Same
7439-92-1
Lead and compounds, N.O.S.
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)tetrahydroxytri-
1335-32-6
U146
Lindane
Cyclohexane, 1,2,3,4,5,6-hexa-
chloro-,
1alpha,2alpha,3beta,4alpha,5alpha,6b
eta)-
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 dimethyldithiocarbamate
Manganese, bis(dimethylcarbamo-
dithioato-S,S')-,
15339-36-3
P196
Melphalan
L-Phenylalanine, 4-[bis(2-chloro-
ethyl)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
U384
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-[[(methyl-
amino)carbonyl]oxy]-, methyl ester
16752-77-5
P066
Methoxychlor
Benzene, 1,1'-(2,2,2-trichloroethyl-
idene)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
177
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-chloroaniline)
Benzenamine, 4,4'-methylenebis[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
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-methyl-
phenyl 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-
(1aalpha,8beta,8aalpha,8balpha)]-,
50-07-7
U010
Molinate
1H-Azepine-1-carbothioic acid,
hexahydro-, S-ethyl ester
2212-67-1
U365
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
alpha-Naphthylamine
1-Naphthalenamine
134-32-7
U167
beta-Naphthylamine
2-Naphthalenamine
91-59-8
U168
alpha-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
Nitrobenzene
Benzene, nitro-
98-95-3
P078
Nitrogen dioxide
Nitrogen oxide NO
2
10102-44-0
P078
178
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-chloro-
ethyl)-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-(dimethyl-
amino)-N-[[(methylamino)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
Pebulate
Carbamothioic acid, butylethyl-,
S-propyl ester
1114-71-2
U391
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
179
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-, methylcarbamate (ester),
(3aS-cis)-
57-47-6
P204
Physostigmine salicylate
Benzoic acid, 2-hydroxy-, compound
with (3aS-cis)-1,2,3,3a,8,8a-hexa-
hydro-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 dimethyldithiocarbamate
Carbamodithioc acid, dimethyl,
potassium salt
128-03-0
U383
Potassium hydroxymethyl-n-methyl-dithio-
carbamate
Carbamodithioc acid, (hydroxy-
methyl)methyl-, monopotassium salt
51026-28-9
U378
Potassium n-methyldithiocarbamate
Carbamodithioc acid, methyl-mono-
potassium salt
137-41-7
U377
Potassium silver cyanide
Argentate(1-), bis(cyano-C)-,
potassium)
506-61-6
P099
Potassium pentachlorophenate
Pentachlorophenol, potassium salt
7778736
None
Promecarb
Phenol, 3-methyl-5-(1-methylethyl)-,
methyl carbamate
2631-37-0
P201
Pronamide
Benzamide, 3,5-dichloro-N-(1,1-di-
methyl-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-methyl-
ethyl ester
122-42-9
U373
Propoxur
Phenol, 2-(1-methylethoxy)-, methyl-
carbamate
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-trimethoxy-
benzoyl)oxy]-, methyl ester,
(3beta,16beta,17alpha,18beta,20alpha
)-,
50-55-5
U200
Resorcinol
1,3-Benzenediol
108-46-3
U201
Saccharin
1,2-Benzisothiazol-3(2H)-one, 1,1-
81-07-2
U202
180
dioxide
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 orthothio-
selenious acid
144-34-3
U376
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
U379
Sodium diethyldithiocarbamate
Carbamodithioic acid, diethyl-,
sodium salt
148-18-5
U381
Sodium dimethyldithiocarbamate
Carbamodithioic acid, dimethyl-,
sodium salt
128-04-1
U382
Sodium pentachlorophenate
Pentachlorophenol, sodium salt
131522
None
Streptozotocin
D-Glucose, 2-deoxy-2-[[methyl-
nitrosoamino)carbonyl]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
U277
TCDD
Dibenzo[b,e][1,4]dioxin, 2,3,7,8-
tetrachloro-
1746-01-6
Tetrabutylthiuram disulfide
Thioperoxydicarbonic diamide, tetra-
butyl
1634-02-2
U402
Tetrabutylthiuram monosulfide
Bis(dimethylthiocarbamoyl) sulfide
97-74-5
U401
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
181
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
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-(methyl-
thio)-, 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-carboxaldehyde,
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-diisocyanatomethyl-
26471-62-5
U223
o-Toluidine
Benzenamine, 2-methyl-
95-53-4
U328
o-Toluidine hydrochloride
Benzeneamine, 2-methyl-, hydro-
chloride
636-21-5
U222
p-Toluidine
Benzenamine, 4-methyl-
106-49-0
U353
Toxaphene
Same
8001-35-2
P123
Triallate
Carbamothioic acid, bis(1-methyl-
ethyl)-, S-(2,3,3-trichloro-2-propenyl)
ester
2303-17-5
U389
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
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
182
2,4,5-T
Acetic acid, (2,4,5-trichlorophenoxy)-
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"-phosphinothioyl-
idynetris-
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
U385
Vinyl chloride
Ethene, chloro-
75-01-4
U043
Warfarin
2H-1-Benzopyran-2-one, 4-hydroxy-
3-(3-oxo-1-phenylbutyl)-, when
present at concentrations less than
0.3%.
81-81-2
U248
Warfarin
2H-1-Benzopyran-2-one, 4-hydroxy-
3-(3-oxo-1-phenylbutyl)-, when
present at concentrations greater than
0.3%.
81-81-2
P001
Warfarin salts, when present at
concentrations less than 0.3%.
U248
Warfarin salts, when present at
concentrations greater than 0.3%.
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%.
1314-84-7
P122
Zinc phosphide
Zinc phosphide P
2
Zn
3
, when present
at concentrations of 10% 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 not
specifically listed by name in this Section.
(Source: Amended at 20 Ill. Reg. ________, effective ______________________)
Section 721.Appendix I
Wastes Excluded by Administrative Action
Table B Wastes Excluded by U.S. EPA under 40 CFR 260.20 and 260.22 from Specific Sources
183
Facility Address
Waste Description
Amoco Oil Company
Wood River, Illinois
150 million gallons of DAF float from petroleum refining contained
in four surge ponds after treatment with the Chemfix stabilization
process. This waste contains U.S. EPA hazardous waste number
K048. This exclusion applies to the 150 million gallons of waste
after chemical stabilization as long as the mixing ratios of the reagent
with the waste are monitored continuously and do not vary outside of
the limits presented in the demonstration samples and one grab
sample is taken each hour from each treatment unit, composited, and
EP toxicity tests performed on each sample. If the levels of lead or
total chromium exceed 0.5 ppm in the EP extract, then the waste that
was processed during the compositing period is considered
hazardous; the treatment residue shall be pumped into bermed cells
to ensure that the waste is identifiable in the event that removal is
necessary.
USX Steel Corporation
Chicago, Illinois
Fully-cured chemically stabilized electric arc furnace dust/sludge
(CSEAFD) treatment residue (U.S. EPA hazardous waste number
K061) generated from the primary production of steel after April 29,
1991. This exclusion (for 35,000 tons of CSEAFD per year) is
conditioned on the data obtained from USX's full-scale CSEAFD
treatment facility. To ensure that hazardous constituents are not
present in the waste at levels of regulatory concern once the full-
scale treatment facility is in operation, USX shall implement a
testing program for the petitioned waste. This testing program must
meet the following conditions for the exclusion to be valid:
1.
Testing: Sample collection and analyses (including quality
control (QC) procedures) must be performed according to
SW-846 methodologies, incorporated by reference in 35 Ill.
Adm. Code 720.111.
A.
Initial Testing: During the first four weeks of
operation of the full scale treatment system, USX
shall collect representative grab samples of each
treated batch of the CSEAFD and composite the
grab samples daily. The daily composites, prior to
disposal, must be analyzed for the EP leachate
concentrations of all the EP toxic metals, nickel,
and cyanide (using distilled water in the cyanide
extractions), and the total concentrations of reactive
sulfide and reactive cyanide. USX must report the
analytical test data, including quality control
information, obtained during this initial period no
later than 90 days after the treatment of the first
full-scale batch.
B.
Subsequent Testing: USX shall collect
representative grab samples from every treated
batch of CSEAFD generated daily and composite
184
all of the grab samples to produce a weekly
composite sample. USX then shall analyze each
weekly composite sample for all of the EP toxic
metals and nickel. The analytical data, including
quality control information, must be compiled and
maintained on site for a minimum of three years.
These data must be furnished upon request and
made available for inspection by any employee or
representative of U.S. EPA or the Agency.
2.
Delisting levels: If the EP extract concentrations for
chromium, lead, arsenic, or silver exceed 0.315 mg/l;
barium exceeds 6.3 mg/l; cadmium or selenium exceed
0.063 mg/l; mecury exceeds 0.0126 mg/l; nickel exceeds
3.15 mg/l; or cyanide exceeds 4.42 mg/l or total reactive
cyanide or total reactive sulfide levels exceed 250 mg/kg
and 500 mg/kg, respectively, the waste must either be re-
treated until it meets these levels or managed and disposed
of in accordance with Subpart C of Resource Conservation
and Recovery Act (42 U.S.C. 6901 et seq.).
3.
Data submittal to and enforcement by U.S. EPA: Within
one week of system start-up USX must notify the Section
Chief, Delisting Section (see address below) when their full-
scale stabilization system is on-line and waste treatment has
begun. The data obtained through condition (1)(A) shall be
submitted to the Section Chief, Delisting Section,
CAD/OSW (OS-333), U.S. EPA, 401 M Street, S.W.,
Washington, DC 20460 within the time period specified. At
U.S. EPA's request, USX must submit any other analytical
data obtained through conditions (1)(A) or (1)(B) within the
time peirod specified by the Section Chief. Failure to
submit the required data obtained from conditions (1)(A) or
(1)(B) within the specified time period or maintain the
required records for the specified time will be considered by
U.S. EPA, at its decision, sufficient basis to revoke USX's
Federal exclusion to the extent directed by U.S. EPA. All
data must be accompanied by the following certification
statement: "Under civil and criminal penalty of law for the
making or submission of false or fraudulent statements or
representations (pursuant to the applicable provisions of the
Federal Code which include, but may not be limited to, 18
U.S.C. Section 6928), I certify that the information
contained in or accompanying this document is true,
accurate and complete. As to the (those) identified
section(s) of this document for which I cannot personally
verify its (their) truth and accuracy, I certify as the company
official having supervisory responsibility for the persons
who, acting under my direct instructions, made the vertifica-
tion that this information is true, accurate and complete. In
the event that any of this information is determined by U.S.
185
EPA in its sole discretion to be false, inaccurate or
incomplete, and upon conveyance of this fact to the
company, I recognize and agree that this federal exclusion
of wastes will be void as if it never had effect or to the
extent directed by U.S. EPA and that the company will be
liable for any actions taken in contravention of the
company's RCRA and CERCLA obligations premised upon
the company's reliance on the void exclusion."
4.
Data Submittal to Agency: The data obtained through
condition (1)(A) must be submitted to the Illinois
Environmental Protection Agency, Planning and Reporting
Section, 2200 Churchill Road, P.O. Box 19276, Springfield,
IL 62794-9276 within the time period specified. At
Agency's request, USX must submit any other analytical
data obtained through conditions (1)(A) or (1)(B) within the
time period specified by the Agency. All data must be
accompanied by the following certification statement:
"Under civil and criminal penalty of law for the making or
submission of false or fraudulent statements or
representations (pursuant to the applicable provisions of
Illinois' Environmental Protection Act), I certify that the
information contained in or accompanying this document is
true, accurate and complete. As to the (those) identified
section(s) of this document for which I cannot personally
verify its (their) truth and accuracy, I certify as the company
official having supervisory responsibility for the persons
who, acting under my direct instructions, made the
verification that this information is true, accurate and
complete."
5.
Enforcement by the Agency: Whenever the Agency finds
that USX has violated the standards in this exclusion, has
failed to submit the required data obtained from conditions
(1)(A) or (1)(B) within the specified time period, has failed
to maintain the required records for the specified time or has
submitted false, inaccurate or incomplete data, the Agency
may take such action as is allowed by Title VIII of the Act.
6.
Notification to the Board: Upon modification, termination,
revocation, or other alteration of this exemption by U.S.
EPA, USX shall file a petition, pursuant to Part 102, with
this Board requesting that the Board follow the U.S. EPA
action.
Conversion Systems, Inc.
Horsham, Pennsylvania (Sterling,
Illinois operations)
Chemically stabilized electric arc furnace dust (CSEAFD) that is
generated by Conversion Systems, Inc. (CSI) (using the Super
Detox
Ô
treatment process, as modified by CSI to treat electric arc
furnace dust (EAFD) (USEPA hazardous waste no. K061)), at the
following site and which is disposed of in a RCRA Subtitle D
municipal solid waste landfill (MSWLF): Northwestern Steel,
186
Sterling, Illinois.
CSI must implement a testing program for each site that meets the
following conditions:
1. Verification testing requirements: Sample collection and analyses,
including quality control procedures, must be performed according to
SW-846 methodologies, incorporated by reference in 35 Ill. Adm.
Code 720.111.
A. Initial verification testing: During the first 20 days of
full-scale operation of a newly-constructed Super Detox
Ô
treatment facility, CSI shall analyze a minimum of four
composite samples of CSEAFD representative of the full 20-
day period. Composite samples must be composed of
representative samples collected from every batch
generated. The CSEAFD samples must be analyzed for the
constituents listed in condition 3 below. CSI shall report the
operational and analytical test data, including quality control
information, obtained during this initial period no later than
60 days after the generation of the first batch of CSEAFD.
B. Addition of new Super Detox
Ô
treatment facilities to the
exclusion:
Option 1: If USEPA approves additional facilities, CSI may
petition the Board for identical-in substance amendment of
this exclusion pursuant to Section 22.4 for the Act and 35
Ill. Adm. Code 102 and 720.120(a), or
Option 2: If USEPA has not approved such amendment,
CSI may petition the Board for amendment pursuant to the
general rulemaking procedures of Section 27 of the Act and
35 Ill. Adm. Code 102 and 720.120(b); or
Option 3: Alternatively to options 1 or 2 above, CSI may
petition the Board for a hazardous waste delisting pursuant
to Section 28.1 of the Act and 35 Ill. Adm. Code 106 and
720.122.
If CSI pursues general rulemaking (option 2 above) or
hazardous waste delisting (option 3 above), it must
demonstrate that the CSEAFD generated by a specific Super
Detox
Ô
treatment facility consistently meets the delisting
levels specified in condition 3 below.
C. Subsequent verification testing: For the approved
facility, CSI shall collect and analyze at least one composite
sample of CSEAFD each month. The composite samples
must be composed of representative samples collected from
all batches treated in each month. These monthly
187
representative samples must be analyzed, prior to the
disposal of the CSEAFD, for the constituents listed in
condition 3 below. CSI may, at its discretion, analyze
composite samples gathered more frequently to demonstrate
that smaller batches of waste are nonhazardous.
2. Waste holding and handling: CSI shall store as hazardous all
CSEAFD generated until verification testing, as specified in
condition 1A or 1C above, as appropriate, is completed and valid
analyses demonstrate that condition 3 below is satisfied. If the levels
of constituents measured in the samples of CSEAFD do not exceed
the levels set forth in condition 3, then the CSEAFD is nonhazardous
and may be disposed of in a RCRA Subtitle D municipal solid waste
landfill. If constituent levels in a sample exceed any of the delisting
levels set forth in condition 3 below, the CSEAFD generated during
the time period corresponding to this sample must be retreated until
it meets these levels or managed and disposed of as hazardous waste,
in accordance with 35 Ill. Adm. Code 702 through 705, 720 through
726, 728, and 733. CSEAFD generated by a new CSI treatment
facility must be managed as a hazardous waste prior to the addition
of the name and location of the facility to this exclusion pursuant to
condition 1C above. After addition of the new facility to the
exclusion pursuant to condition 1B above, CSEAFD generated during
the verification testing in condition 1A is also non-hazardous if the
delisting levels in condition 3 are satisfied.
3. Delisting levels: All leachable concentrations for metals must not
exceed the following levels (in parts per million (ppm)): antimony--
0.06; arsenic --0.50; barium--7.6; beryllium--0.010; cadmium--
0.050; chromium--0.33; lead--0.15; mercury--0.009; nickel--1;
selenium--0.16; silver--0.30; thallium--0.020; vanadium--2; and
zinc--70. Metal concentrations must be measured in the waste
leachate by the method specified in Section 721.124.
4. Changes in operating conditions: After initiating subsequent
testing, as described in condition 1C, if CSI significantly changes the
stabilization process established under condition 1 (e.g., use of new
stabilization reagents), CSI shall seek amendment of this exclusion
using one of the options set forth in condition 1B above. After
written amendment of this exclusion, CSI may manage CSEAFD
wastes generated from the new process as nonhazardous if the wastes
meet the delisting levels set forth in condition 3 above.
5. Data submittals: At least one month prior to operation of a new
Super Detox
Ô
treatment facility, CSI must notify the Agency in
writing when the Super Detox
Ô
treatment facility is scheduled to be
on-line. The data obtained through condition 1A must be submitted
to the Agency within the time period specified. Records of operating
conditions and analytical data from condition 1 must be compiled,
summarized, and maintained on site for a minimum of five years.
These records and data must be furnished to the Agency upon request
188
and made available for inspection. Failure to submit the required
data within the specified time period or to maintain the required
records on site for the specified time will be considered a violation of
the Act and Board regulations. All data submitted must be
accompanied by a signed copy of the following certification
statement to attest to the truth and accuracy of the data submitted:
"Under civil and criminal penalty of law for the making or
submission of false or fraudulent statements or representations, I
certify that the information contained in or accompanying this
document is true, accurate, and complete.
"As to (those) identified section(s) of this document for which I
cannot personally verify its (their) truth and accuracy, I certify as the
company official having supervisory responsibility for the persons
who, acting under my direct instructions, made the verification that
this information is true, accurate, and complete.
"In the event that any of this information is determined by the Board
or a court of law to be false, inaccurate, or incomplete, and upon
conveyance of this fact to the company, I recognize and agree that
this exclusion of waste will be void as if it never had effect or to the
extent directed by the Board or court and that the company will be
liable for any actions taken in contravention of the company's
obligations under the federal RCRA and Comprehensive
Environmental Response, Compensation and Liability Act (42
U.S.C. §§ 9601 et seq.) and corresponding provisions of the Act
premised upon the company's reliance on the void exclusion."
BOARD NOTE: The obligations of this exclusion are derived from
but also distinct from the obligations under the corresponding
federally-granted exclusion of 40 CFR 261, Appendix IX, Table 2.
(Source: Amended at 20 Ill. Reg. ________, effective ______________________)
Section 721.Appendix Z Table to Section 721.102
Table
*1
*2
*3
*4
Spent materials (both listed and
nonlisted/characteristics
Yes
Yes
Yes
Yes
Sludges (listed in Section 721.131 or
721.132)
Yes
Yes
Yes
Yes
Sludges (nonlisted/exhibiting a
characteristic of hazardous waste)
Yes
Yes
No
Yes
189
By-products (listed in Section 721.131 or
721.132)
Yes
Yes
Yes
Yes
By-products (nonlisted/exhibiting a
characteristic of hazardous waste)
Yes
Yes
No
Yes
Commercial chemical products listed in
Section 721.133that are not ordinarily
applied to the land or burned as fuels
Yes
Yes
No
No
Scrap metal
Yes
Yes
Yes
Yes
Yes - Defined as a solid waste
No - Not defined as a solid waste
*1 - Use constituting disposal (Section 721.102(c)(1))
*2 - Burning for energy recovery or use to produce a fuel (Section 721.102(c)(2))
*3 - Reclamation (Section 721.102(c)(3))
*4 - Speculative accumulation (Section 721.102(c)(4))
BOARD NOTE: Derived from Table 1 to 40 CFR 261.2(c)(4) (1994).
(Source: Amended at 20 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
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
190
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
SUBPART F: IMPORTS OF HAZARDOUS WASTE
Section
722.160 Imports of Hazardous Waste
SUBPART G: FARMERS
Section
722.170 Farmers
722.Appendix A Hazardous Waste Manifest
AUTHORITY: Implementing Section 22.4 and authorized by Section 27 of the Environmental Protection Act
[415 ILCS 5/22.4 and 27].
SOURCE: Adopted in R81-22, 43 PCB 427, at 5 Ill. Reg. 9781, effective May 17, 1982; amended and codified
in R81-22, 45 PCB 317, at 6 Ill. Reg. 4828, effective May 17, 1982; amended in R82-18, 51 PCB 31, 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. ________,
_______________________.
191
SUBPART A: GENERAL
Section 722.110
Purpose, Scope and Applicability
a)
These regulations establish standards for generators of hazardous waste.
b)
35 Ill. Adm. Code 721.105(c) and (d) must be used to determine the applicability of provisions
of this Part that are dependent on calculations of the quantity of hazardous waste generated per
month.
bc)
A generator who treats, stores or disposes of hazardous waste on-site must only comply with
the following Sections of this Part with respect to that waste: Section 722.111 for determining
whether or not the generator has a hazardous waste, Section 722.112 for obtaining an EPA
identification number, Section 722.140(c) and (d) for recordkeeping, Section 722.143 for
additional reporting and, if applicable, Section 722.170 for farmers.
cd)
Any person who imports hazardous waste into the United States must comply with the
standards applicable to generators established in this Part.
de)
A farmer who generates waste pesticides which are hazardous waste and who complies with all
of the requirements of Section 722.151 is not required to comply with other standards in this
Part, or 35 Ill. Adm. Code 702, 703, 724 725 or 728 with respect to such pesticides.
ef)
A person who generates a hazardous waste as defined by 35 Ill. Adm. Code 721 is subject to
the compliance requirements and penalties prescribed in Title VIII and XII of the
Environmental Protection Act if he does not comply with the requirements of this Part.
fg)
An owner or operator who initiates a shipment of hazardous waste from a treatment, storage or
disposal facility must comply with the generator standards established in this Part.
BOARD NOTE: The provisions of Section 722.134 are applicable to the on-site accumulation
of hazardous waste by generators. Therefore, the provisions of Section 722.134 only apply to
owners or operators who are shipping hazardous waste which they generated at that facility. A
generator who treats, stores or disposes of hazardous waste on-site must comply with the
applicable standards and permit requirements set forth in 35 Ill. Adm. Code 702, 703, 724,
725, 726 and 728.
g) 35 Ill. Adm. Code 700 contains rules on application of other Board regulations.
(Source: Amended at 20 Ill. Reg. ________, effective ______________________)
Section 722.111
Hazardous Waste Determination
A person who generates a solid waste, as defined in 35 Ill. Adm. Code 721.102, shall determine if that waste is
a hazardous waste using the following method:
a)
The person should first determine if the waste is excluded from regulation under 35 Ill. Adm.
Code 721.104.
b)
The person should then determine if the waste is listed as a hazardous waste in 35 Ill. Adm.
Code 721.Subpart D.
192
(Board Note: Even if a waste is listed, the generator still has an opportunity under 35 Ill.
Adm. Code 720.122 and 40 CFR 260.22 (1986) to demonstrate that the waste from the
generator's particular facility or operation is not a hazardous waste.
c)
For purposes of compliance with 35 Ill. Adm. Code 728, or if the waste is not listed as a
hazardous waste in 35 Ill. Adm. Code 721.Subpart D, the generator shall then determine
whether the waste is identified in 35 Ill. Adm. Code 721.Subpart C by either:
1)
Testing the waste according to the methods set forth in 35 Ill. Adm. Code 721.Subpart
C, or according to an equivalent method approved by the Board under 35 Ill. Adm.
Code 720.121; or
2)
Applying knowledge of the hazard characteristic of the waste in light of the materials
or processes used.
d)
If the generator determines that the waste is hazardous, the generator shall refer to 35 Ill. Adm.
Code 724, 725, and 728, and 733 for possible exclusions or restrictions pertaining to the
management of the specific waste.
(Source: Amended at 20 Ill. Reg. ________, effective ______________________)
TITLE 35: ENVIRONMENTAL PROTECTION
SUBTITLE G: WASTE DISPOSAL
CHAPTER I: POLLUTION CONTROL BOARD
SUBCHAPTER c: HAZARDOUS WASTE OPERATING REQUIREMENTS
PART 724
STANDARDS FOR OWNERS AND OPERATORS OF HAZARDOUS WASTE
TREATMENT, STORAGE, AND DISPOSAL FACILITIES
SUBPART A: GENERAL PROVISIONS
Section
724.101 Purpose, Scope and Applicability
724.103 Relationship to Interim Status Standards
SUBPART B: GENERAL FACILITY STANDARDS
Section
724.110 Applicability
724.111 Identification Number
724.112 Required Notices
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
193
Section
724.130 Applicability
724.131 Design and Operation of Facility
724.132 Required Equipment
724.133 Testing and Maintenance of Equipment
724.134 Access to Communications or Alarm System
724.135 Required Aisle Space
724.137 Arrangements with Local Authorities
SUBPART D: CONTINGENCY PLAN AND EMERGENCY PROCEDURES
Section
724.150 Applicability
724.151 Purpose and Implementation of Contingency Plan
724.152 Content of Contingency Plan
724.153 Copies of Contingency Plan
724.154 Amendment of Contingency Plan
724.155 Emergency Coordinator
724.156 Emergency Procedures
SUBPART E: MANIFEST SYSTEM, RECORDKEEPING AND REPORTING
Section
724.170 Applicability
724.171 Use of Manifest System
724.172 Manifest Discrepancies
724.173 Operating Record
724.174 Availability, Retention and Disposition of Records
724.175 Annual Report
724.176 Unmanifested Waste Report
724.177 Additional Reports
SUBPART F: RELEASES FROM SOLID WASTE MANAGEMENT UNITS
Section
724.190 Applicability
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
Section
724.210 Applicability
724.211 Closure Performance Standard
724.212 Closure Plan; Amendment of Plan
724.213 Closure; Time Allowed For Closure
194
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 Plan; Amendment of Plan
724.219 Post-closure Notices
724.220 Certification of Completion of Post-closure Care
SUBPART H: FINANCIAL REQUIREMENTS
Section
724.240 Applicability
724.241 Definitions of Terms As Used In This Subpart
724.242 Cost Estimate for Closure
724.243 Financial Assurance for Closure
724.244 Cost Estimate for Post-closure Care
724.245 Financial Assurance for Post-closure Care
724.246 Use of a Mechanism for Financial Assurance of Both Closure and Post-closure Care
724.247 Liability Requirements
724.248 Incapacity of Owners or Operators, Guarantors or Financial Institutions
724.251 Wording of the Instruments
SUBPART I: USE AND MANAGEMENT OF CONTAINERS
Section
724.270 Applicability
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
195
724.321 Design and Operating Requirements
724.322 Action Leakage Rate
724.323 Response Actions
724.326 Monitoring and Inspection
724.327 Emergency Repairs; Contingency Plans
724.328 Closure and Post-closure Care
724.329 Special Requirements for Ignitable or Reactive Waste
724.330 Special Requirements for Incompatible Wastes
724.331 Special Requirements for Hazardous Wastes F020, F021, F022, F023, F026 and F027
724.332 Air Emission Standards
SUBPART L: WASTE PILES
Section
724.350 Applicability
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)
196
724.417 Special Requirements for Hazardous Wastes F020, F021, F022, F023, F026 and F027
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
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
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
197
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
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 Section 22.4 and authorized by Section 27 of the Environmental Protection Act
[415 ILCS 5/22.4 and 27].
SOURCE: Adopted in R82-19, 53 PCB 131, 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,
198
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. ________,
_______________________.
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.
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. 1431-1434, 33 U.S.C. 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 U.S. EPA rules.
g)
The requirements of this Part do not apply to:
199
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.
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.
78)
Immediate response:
A)
Except as provided in subsection (g)(8)(B) below, 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.
B)
An owner or operator of a facility otherwise regulated by this Part must
comply with all applicable requirements of 724.Subparts C and D.
C)
Any person that is covered by subsection (g)(8)(A) above and that continues
or initiates hazardous waste treatment or containment activities after the
200
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.
89)
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.
910)
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; and
C)
Thermostats, as described in 35 Ill. Adm. Code 733.104.
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.
(Source: Amended at 20 Ill. Reg. ________, effective ______________________)
SUBPART CC: AIR EMISSION STANDARDS FOR TANKS,
SURFACE IMPOUNDMENTS, AND CONTAINERS
Section 724.980 Applicability
a)
The requirements of this Subpart apply, effective December 6, 1995October 6, 1996, to owners
and operators of all facilities that treat, store, or dispose of hazardous waste in tanks, surface
impoundments, or containers subject to 724.Subparts I, J, or K, except as Section 724.101 and
subsection (b) below provide otherwise.
BOARD NOTE: U.S. EPA adopted these regulations at 59 Fed. Reg. 62896 (Dec. 6, 1994),
effective June 6, 1995. At 60 Fed. Reg. 26828 (May 19, 1995), 60 Fed. Reg. 56952 (Nov. 13,
1995), and 61 Fed. Reg. 28508 (June 5, 1996), U.S. EPA delayed the effective date until
December 6, 1995October 6, 1996. If action by U.S. EPA or a decision of a federal court
changes the effectiveness of these regulations, the Board does not intend that the 724.Subpart
CC rules be enforceable to the extent that they become more stringent that the federal
regulations upon which they are based.
b)
The requirements of this Subpart do not apply to the following waste management units at the
facility:
201
1)
A waste management unit that holds hazardous waste placed in the unit before
December 6, 1995October 6, 1996, and in which no hazardous waste is added to the
unit on or after this date.
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 generated as the result of implementing remedial activities
required pursuant to the Act or Board regulations or under the corrective action
authorities of RCRA sections 3004(u), 3004(v) or 3008(h); CERCLA authorities; or
similar federal or 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 U.S.C. 2011 et seq.) and the Nuclear Waste Policy Act.
c)
For the owner and operator of a facility subject to this Subpart and who received a final RCRA
permit prior to December 6, 1995October 6, 1996, the requirements of this Subpart shall 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. Until such date when the owner and
operator receives a final permit incorporating the requirements of this Subpart, the owner and
operator is subject to the requirements of 35 Ill. Adm. Code 725.Subpart CC.
d)
The requirements of this Subpart, except for the recordkeeping requirements specified in
Section 724.989(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.
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
sturctural 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
724.989(i), explaining why an undue safety hazard would be created if air emission
controls specified in Sections 724.984 through 724.987 are installed and operated on
the tanks and containers used at the facility to manage the hazardous waste generated
202
by the organic peroxide manufacturing process or processes meeting the conditions of
subsection (d)(1) above.
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) above are managed at the facility in tanks or containers meeting the
conditions of subsection (d)(2) above. 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 20 Ill. Reg. ________, effective ______________________)
Section 724.989 Recordkeeping Requirements
a)
Each owner or operator of a facility subject to requirements in this Subpart shall record and
maintain the following information as applicable:
1)
Documentation for each cover installed on a tank in accordance with the requirements
of Section 724.984(b)(2) or (b)(3) that includes information prepared by the owner or
operator or provided by the cover manufacturer or vendor describing the cover design,
and certification by the owner or operator that the cover meets the applicable design
specifications as listed in 35 Ill. Adm. Code 725.991(c).
2)
Documentation for each floating membrane cover installed on a surface impoundment
in accordance with the requirements of Section 724.985(c) that includes information
prepared by the owner or operator or provided by the cover manufacturer or vendor
describing the cover design, and certification by the owner or operator that the cover
meets the specifications listed in 35 Ill. Adm. Code 725.986(e).
3)
Documentation for each enclosure used to control air emissions from containers in
accordance with the requirements of Section 724.986(b)(2)(A) that includes
information prepared by the owner or operator or provided by the manufacturer or
vendor describing the enclosure design, and certification by the owner or operator that
the enclosure meets the specifications listed in Section 724.986(b)(2)(B).
4)
Documentation for each closed-vent system and control device installed in accordance
with the requirements of Section 724.987 that includes:
A)
Certification that is signed and dated by the owner or operator stating that the
control device is designed to operate at the performance level documented by
a design analysis as specified in subsection (a)(4)(B) below or by performance
tests as specified in subsection (a)(4)(C) below when the tank, surface
impoundment, or container is or would be operating at capacity or the highest
level reasonably expected to occur.
B)
If a design analysis is used, then design documentation as specified in Section
724.935(b)(4). The documentation shall include information prepared by the
owner or operator or provided by the control device manufacturer or vendor
that describes the control device design in accordance with Section
724.935(b)(4)(C) and certification by the owner or operator that the control
equipment meets the applicable specifications.
203
C)
If performance tests are used, then a performance test plan as specified in
Section 724.935(b)(3) and all test results.
D)
Information as required by Section 724.935(c)(1) and (c)(2).
5)
Records for all Method 27 tests performed by the owner or operator for each container
used to meet the requirements of Section 724.986(b)(1)(C).
6)
Records for all visual inspections conducted in accordance with the requirements of
Section 724.988.
7)
Records for all monitoring for detectable organic emissions conducted in accordance
with the requirements of Section 724.988.
8)
Records of the date of each attempt to repair a leak, repair methods applied, and the
date of successful repair.
9)
Records for all continuous monitoring conducted in accordance with the requirements
of Section 724.988.
10)
Records of the management of carbon removed from a carbon adsorption system
conducted in accordance with Section 724.987(c)(3)(B).
11)
Records for all inspections of each cover installed on a tank in accordance with the
requirements of Section 724.984(b)(2) or (b)(3) that includes information as listed in
35 Ill. Adm. Code 725.991(c).
b)
An owner or operator electing to use air emission controls for a tank in accordance with the
conditions specified in Section 724.984(c) shall record the following information:
1)
Date and time each waste sample is collected for direct measurement of maximum
organic vapor pressure in accordance with Section 724.983(c).
2)
Results of each determination of the maximum organic vapor pressure of the waste in
a tank performed in accordance with Section 724.983(c).
3)
Records specifying the tank dimensions and design capacity.
c)
An owner or operator electing to use air emission controls for a tank in accordance with the
requirements of Section 724.991 shall record the information required by Section 724.991(c).
d)
An owner or operator electing not to use air emission controls for a particular tank, surface
impoundment, or container subject to this Subpart in accordance with the conditions specified
in Section 724.982(c) shall record the information used by the owner or operator for each waste
determination (e.g., test results, measurements, calculations, and other documentation) in the
facility operating log. If analysis results for waste samples are used for the waste
determination, then the owner or operator shall record the date, time, and location that each
waste sample is collected in accordance with applicable requirements of Section 724.983.
204
e)
An owner or operator electing to comply with requirements in accordance with Section
724.982(c)(2)(E) or Section 724.982(c)(2)(F) shall record the identification number for the
incinerator, boiler, or industrial furnace in which the hazardous waste is treated.
f)
An owner or operator designating a cover as unsafe to inspect and monitor pursuant to 35 Ill.
Adm. Code 725.989(f)(5) or difficult to inspect and monitor pursuant to 35 Ill. Adm. Code
725.989(f)(6) shall record in a log that is kept in the facility operating record the following
information:
1)
A list of identification numbers for tanks with covers that are designated as unsafe to
inspect and monitor in accordance with the requirements of 35 Ill. Adm. Code
725.989(f)(5), an explanation for each cover stating why the cover is unsafe to inspect
and monitor, and the plan and schedule for inspecting and monitoring each cover.
2)
A list of identification numbers for tanks with covers that are designated as difficult to
inspect and monitor in accordance with the requirements of 35 Ill. Adm. Code
725.989(f)(6), an explanation for each cover stating why the cover is difficult to
inspect and monitor, and the plan and schedule for inspecting and monitoring each
cover.
g)
All records required by subsections (a) through (f) above, except as required in subsections
(a)(1) through (a)(4), shall be maintained in the operating record for a minimum of 3 years.
All records required by subsections (a)(1) through (a)(4) above shall be maintained in the
operating record until the air emission control equipment is replaced or otherwise no longer in
service.
h)
The owner or operator of a facility that is subject to this Subpart and to the control device
standards in 40 CFR 60, Subpart VV or 40 CFR 61, Subpart V, incorporated by reference in
35 Ill. Adm. Code 720.111, may elect to demonstrate compliance with the applicable Sections
of this Subpart by documentation either pursuant to this Subpart, or pursuant to the provisions
of 40 CFR 60, Subpart VV or 40 CFR 61, Subpart V, to the extent that the documentation
required by 40 CFR 60 or 61 duplicates the documentation required by this Section.
i)
For each tank or container not using air emission controls specified in Sections 724.984
through 724.987 in accordance with the conditions specified in Section 724.980(d), the owner
or operator shall record and maintain the following information:
1)
A list of the individual organic peroxide compounds manufactured at the facility that
meet the conditions specified in Section 724.980(d)(1).
2)
A description of how the hazardous waste containing the organic peroxide compounds
identified pursuant to subsection (i)(1) are managed at the facility in tanks and
containers. This description must include the following information:
A)
For the tanks used at the facility to manage this hazardous waste, sufficient
information must be provided to describe each tank: a facility identification
number for the tank, the purpose and placement of this tank in the
management train of this hazardous waste, and the procedures used to
ultimately dispose of the hazardous waste managed in the tanks.
205
B)
For containers used at the facility to manage this hazardous waste, sufficient
information must be provided to describe each tank: a facility identification
number for the container or group of containers, the purpose and placement
of this container or group of containers in the management train of this
hazardous waste, and the procedures used to ultimately dispose of the
hazardous waste managed in the containers.
3)
An explanation of why managing the hazardous waste containing the organic peroxide
compounds identified pursuant to subsection (i)(1) above in the tanks or containers
identified pursuant to subsection (i)(2) above would create an undue safety hazard if
the air emission controls specified in Sections 724.984 through 724.987 were installed
and operated on these waste management units. This explanation must include the
following information:
A)
For tanks used at the facility to manage this hazardous waste,
sufficient information must be provided to explain: how use of the
required air emission controls on the tanks would affect the tank
design features and facility operating procedures currently used to
prevent an undue safety hazard during management of this hazardous
waste in the tanks; and why installation of safety devices on the
required air emission controls, as allowed under Section 724.984(g),
would not address those situations in which evacuation of tanks
equipped with these air emission controls is necessary and consistent
with good engineering and safety practices for handling organic
peroxides.
B)
For containers used at the facility to manage this hazardous waste,
sufficient information must be provided to explain: how use of the
required air emission controls on the tanks would affect the container
design features and handling procedures currently used to prevent an
undue safety hazard during management of this hazardous waste in
the containers; and why installation of safety devices on the required
air emission controls, as allowed under Section 724.986(d), would
not address those situations in which evacuation of containers
equipped with these air emission controls is necessary and consistent
with good engineering and safety practices for handling organic
peroxides.
(Source: Amended at 20 Ill. Reg. ________, effective ______________________)
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
206
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
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
207
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
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
725.217 Post-closure Care and Use of Property
725.218 Post-closure Plan; Amendment of Plan
725.219 Post-Closure Notices
725.220 Certification of Completion of Post-Closure Care
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
208
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 kg/mo
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
209
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
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
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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
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
SUBPART DD: CONTAINMENT BUILDINGS
Section
725.1100
Applicability
725.1101
Design and operating standards
725.1102
Closure and Post Closure-Care
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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
AUTHORITY: Implementing Section 22.4 and authorized by Section 27 of the Environmental Protection Act
[415 ILCS 5/22.4 and 27].
SOURCE: Adopted in R81-22, 43 PCB 427, at 5 Ill. Reg. 9781, effective May 17, 1982; amended and codified
in R81-22, 45 PCB 317, at 6 Ill. Reg. 4828, effective May 17, 1982; amended in R82-18, 51 PCB 831, at 7 Ill.
Reg. 2518, effective February 22, 1983; amended in R82-19, 53 PCB 131, 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 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. ________, _______________________.
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 requirements, until post-closure
responsibilities are fulfilled.
b)
Except as provided in Section 725.980(b), the standards in this Part and 35 Ill. Adm. Code
724.652 and 724.653 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 U.S.C. 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 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
212
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, 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 U.S.C. 1431-
1434; 33 U.S.C. 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) above.
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) through
(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.
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. 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
213
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 must
comply with the requirements set out in Section 725.117(b);
11)
Immediate response:
A)
Except as provided in subsection (c)(11)(B) below, 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.
B)
An owner or operator of a facility otherwise regulated by this Part must
comply with all applicable requirements of 725.Subparts C and D.
C)
Any person that is covered by subsection (c)(11)(A) above 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.;
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; and
C)
Thermostats, as described in 35 Ill. Adm. Code 733.104.
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;
214
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;
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)
Other bodies of regulations may apply 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
(potenyially infectious medical waste), depending on the provisions of those other regulations.
(Source: Amended at 20 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, effective December 6, 1995October 6, 1996, 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 either 725.Subparts I, J, or K, except as
Section 725.101 and subsection (b) below provide otherwise.
BOARD NOTE: U.S. EPA adopted these regulations at 59 Fed. Reg. 62896 (Dec. 6, 1994),
effective June 6, 1995. At 60 Fed. Reg. 26828 (May 19, 1995), 60 Fed. Reg. 56952 (Nov. 13,
1995), and 61 Fed. Reg. 28508 (June 5, 1996), U.S. EPA delayed the effective date until
December 6, 1995October 6, 1996. If action by U.S. EPA or a decision of a federal court
changes the effectiveness of these regulations, the Board does not intend that the 725.Subpart
CC rules be enforceable to the extent that theyit become more stringent that the federal
regulations upon which they are based.
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, 1995October 6, 1996 and in which no hazardous waste is added to the
unit on or after this date.
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).
215
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 generated as the result of implementing remedial activities
required pursuant to the Act or Board regulations or under the corrective action
authorities of RCRA sections 3004(u), 3004(v) or 3008(h); CERCLA authorities; or
similar federal or 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 U.S.C. 2011 et seq.) and the Nuclear Waste Policy Act.
c)
For the owner and operator of a facility subject to this Subpart who has received a final RCRA
permit prior to December 6, 1995October 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.
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
sturctural 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
216
by the organic peroxide manufacturing process or processes meeting the conditions of
subsection (d)(1) above.
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) above are managed at the facility in tanks or containers meeting the
conditions of subsection (d)(2) above. 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 20 Ill. Reg. ________, effective ______________________)
Section 725.982 Schedule for Implementation of Air Emission Standards
a) OAn owners or operators of a facilitiesy in existingence on December 6, 1995October 6, 1996
and subject to 725.Subparts I, J, andor K shall meet the following requirements:
1)
The owner or operator shall install and begin operation of all control equipment
required by this Subpart by December 6, 1995October 6, 1996, except as provided in
subsection (a)(2) below.
2)
When control equipment required by this Subpart cannot be installed and in operation
by December 6, 1995October 6, 1996, the owner or operator shall:
A)
Install and begin operation of the control equipment as soon as possible, but
in no case later than December 8, 1997.
B)
Prepare an implementation schedule that includes the following information:
specific calendar dates for award of contracts or issuance of purchase orders
for the control equipment, initiation of on-site installation of the control
equipment, completion of the control equipment installation, and performance
of any testing to demonstrate that the installed equipment meets the applicable
standards of this Subpart.
C)
For facilities subject to the recordkeeping requirements of Section 725.173,
the owner or operator shall enter the implementation schedule specified in
subsection (a)(2)(B) above in the operating record no later than December 6,
1995October 6, 1996.
D)
For facilities not subject to Section 725.173 above, the owner or operator
shall enter the implementation schedule specified in subsection (a)(2)(B) of
this section in a permanent, readily available file located at the facility no
later than December 6, 1995October 6, 1996.
b)
An owner or operator of a facilitiesy in existence on the effective date of statutory or
regulatory amendments under the Act that render the facility subject to 725.Subparts I, J, or K
shall meet the following requirements:
1)
The owner or operator shall install and begin operation of all control equipment
required by this Subpart by the effective date of the amendment, except as provided in
subsection (b)(2) below.
217
2)
When control equipment required by this Subpart cannot be installed and begin
operation by the effective date of the amendment, the owner or operator shall:
A)
Install and operate the control equipment as soon as possible, but in no case
later than 30 months after the effective date of the amendment.; and
B) Maintenance of implementation schedule.
i) For facilities subject to the recordkeeping requirements of Section
725.173, enter and maintain the implementation schedule specified in
subsection (a)(2)(B) above in the operating record no later than the
effective date of the amendment, or
ii)
For facilities not subject to Section 725.173, the owner or operator
shall enter and maintain the implementation schedule specified in
subsection (a)(2)(B) above in a permanent, readily available file,
located at the facility site, no later than the effective date of the
amendment.
c)
The Agency may elect to extend the implementation date for control equipment at a facility, on
a case by case basis, to a date later than December 8, 1997:
1)
When special circumstances that are beyond the facility owner's or operator's control
delay installation or operation of control equipment, and
2)
The owner or operator has made all reasonable and prudent attempts to comply with
the requirements of this Subpart.
(Source: Amended at 20 Ill. Reg. ________, effective ______________________)
Section 725.990 Recordkeeping Requirements
a)
Each owner or operator of a facility subject to requirements in this Subpart shall record and
maintain the following information as applicable:
1)
Documentation for each cover installed on a tank in accordance with the requirements
of Section 725.985(b)(2) or (b)(3) that includes information prepared by the owner or
operator or provided by the cover manufacturer or vendor describing the cover design,
and certification by the owner or operator that the cover meets the applicable design
specifications as listed in Section 725.991(c).
2)
Documentation for each floating membrane cover installed on a surface impoundment
in accordance with the requirements of Section 725.986(c) that includes information
prepared by the owner or operator or provided by the cover manufacturer or vendor
describing the cover design, and certification by the owner or operator that the cover
meets the specifications listed in Section 725.986(e).
3)
Documentation for each enclosure used to control air emissions from containers in
accordance with the requirements of Section 725.987(b)(2)(A) that includes
information prepared by the owner or operator or provided by the manufacturer or
218
vendor describing the enclosure design, and certification by the owner or operator that
the enclosure meets the specifications listed in Section 725.987(b)(2)(B).
4)
Documentation for each closed-vent system and control device installed in accordance
with the requirements of Section 725.988 that includes:
A)
Certification that is signed and dated by the owner or operator stating that the
control device is designed to operate at the performance level documented by
a design analysis, as specified in subsection (a)(4)(B) below, or by
performance tests, as specified in subsection (a)(4)(C) below, when the tank,
surface impoundment, or container is or would be operating at capacity or the
highest level reasonably expected to occur.
B)
If a design analysis is used, then design documentation as specified in Section
725.935(b)(4). The documentation must include information prepared by the
owner or operator or provided by the control device manufacturer or vendor
that describes the control device design in accordance with Section
725.935(b)(4)(C) and certification by the owner or operator that the control
equipment meets the applicable specifications.
C)
If performance tests are used, then a performance test plan as specified in
Section 725.935(b)(3) and all test results.
D)
Information as required by Sections 725.935(c)(1) and 725.935(c)(2).
5)
Records for all Method 27 tests performed by the owner or operator for each container
used to meet the requirements of Section 725.987(b)(1)(C).
6)
Records for all visual inspections conducted in accordance with the requirements of
Section 725.989.
7)
Records for all monitoring for detectable organic emissions conducted in accordance
with the requirements of Section 725.989.
8)
Records of the date of each attempt to repair a leak, repair methods applied, and the
date of successful repair.
9)
Records for all continuous monitoring conducted in accordance with the requirements
of Section 725.989.
10)
Records of the management of carbon removed from a carbon adsorption system
conducted in accordance with Section 725.988(c)(3)(B).
11)
Records for all inspections of each cover installed on a tank in accordance with the
requirements of Section 725.985(b)(2) or (b)(3) that includes information as listed in
Section 725.991(c).
b)
An owner or operator electing to use air emission controls for a tank in accordance with the
conditions specified in Section 725.985(c) shall record the following information:
219
1)
The date and time each waste sample is collected for direct measurement of maximum
organic vapor pressure in accordance with Section 725.984(c).
2)
The results of each determination for the maximum organic vapor pressure of the
waste in the tank performed in accordance with Section 725.984(c).
3)
The records specifying the tank dimensions and design capacity.
c)
An owner or operator electing to use air emission controls for a tank in accordance with the
requirements of Section 725.991 shall record the information required by Section 725.991(c).
d)
An owner or operator electing not to use air emission controls for a particular tank, surface
impoundment, or container subject to this Subpart in accordance with the conditions specified
in Section 725.983(c) shall record the information used by the owner or operator for each waste
determination (e.g., test results, measurements, calculations, and other documentation) in the
facility operating log. If analysis results for waste samples are used for the waste
determination, then the owner or operator shall record the date, time, and location that each
waste sample is collected in accordance with applicable requirements of Section 725.984.
e)
An owner or operator electing to comply with requirements in accordance with Section
725.983(c)(2)(E) or (c)(2)(F) shall record the identification number for the incinerator, boiler,
or industrial furnace in which the hazardous waste is treated.
f)
An owner or operator designating a cover as unsafe to inspect and monitor pursuant to Section
725.989(f)(5) or difficult to inspect and monitor pursuant to Section 725.989(f)(6) shall record
in a log that is kept in the facility operating record the following information:
1)
A list of identification numbers for tanks with covers that are designated as unsafe to
inspect and monitor in accordance with the requirements of Section 725.989(f)(5), an
explanation for each cover stating why the cover is unsafe to inspect and monitor, and
the plan and schedule for inspecting and monitoring each cover.
2)
A list of identification numbers for tanks with covers that are designated as difficult to
inspect and monitor in accordance with the requirements of Section 725.989(f)(6), an
explanation for each cover stating why the cover is difficult to inspect and monitor,
and the plan and schedule for inspecting and monitoring each cover.
g)
All records required by subsections (a) through (f) above, except as required in subsections
(a)(1) through (a)(4) above, must be maintained in the operating record for a minimum of 3
years. All records required by subsections (a)(1) through (a)(4) above must be maintained in
the operating record until the air emission control equipment is replaced or otherwise no longer
in service.
h)
The owner or operator of a facility that is subject to this Subpart and to the control device
standards in 40 CFR 60, Subpart VV, or 40 CFR 61, Subpart V, incorporated by reference in
35 Ill. Adm. Code 270.111, may elect to demonstrate compliance with the applicable Sections
of this Subpart by documentation either pursuant to this Subpart, or pursuant to the provisions
of 40 CFR 60, Subpart VV or 40 CFR 61, Subpart V, to the extent that the documentation
required by 40 CFR 60 or 61 duplicates the documentation required by this Section.
220
i)
For each tank or container not using air emission controls specified in Sections 725.985
through 725.988 in accordance with the conditions specified in Section 725.980(d), the owner
or operator shall record and maintain the following information:
1)
A list of the individual organic peroxide compounds manufactured at the facility that
meet the conditions specified in Section 725.980(d)(1).
2)
A description of how the hazardous waste containing the organic peroxide compounds
identified pursuant to subsection (i)(1) are managed at the facility in tanks and
containers. This description must include the following information:
A)
For the tanks used at the facility to manage this hazardous waste, sufficient
information must be provided to describe each tank: a facility identification
number for the tank, the purpose and placement of this tank in the
management train of this hazardous waste, and the procedures used to
ultimately dispose of the hazardous waste managed in the tanks.
B)
For containers used at the facility to manage this hazardous waste, sufficient
information must be provided to describe each tank: a facility identification
number for the container or group of containers, the purpose and placement
of this container or group of containers in the management train of this
hazardous waste, and the procedures used to ultimately dispose of the
hazardous waste managed in the containers.
3)
An explanation of why managing the hazardous waste containing the organic peroxide
compounds identified pursuant to subsection (i)(1) above in the tanks or containers
identified pursuant to subsection (i)(2) above would create an undue safety hazard if
the air emission controls specified in Sections 725.985 through 725.988 were installed
and operated on these waste management units. This explanation must include the
following information:
A)
For tanks used at the facility to manage this hazardous waste,
sufficient information must be provided to explain: how use of the
required air emission controls on the tanks would affect the tank
design features and facility operating procedures currently used to
prevent an undue safety hazard during management of this hazardous
waste in the tanks; and why installation of safety devices on the
required air emission controls, as allowed under Section 725.985(g),
would not address those situations in which evacuation of tanks
equipped with these air emission controls is necessary and consistent
with good engineering and safety practices for handling organic
peroxides.
B)
For containers used at the facility to manage this hazardous waste,
sufficient information must be provided to explain: how use of the
required air emission controls on the tanks would affect the container
design features and handling procedures currently used to prevent an
undue safety hazard during management of this hazardous waste in
the containers; and why installation of safety devices on the required
air emission controls, as allowed under Section 725.987(d), would
not address those situations in which evacuation of containers
221
equipped with these air emission controls is necessary and consistent
with good engineering and safety practices for handling organic
peroxides.
(Source: Amended at 20 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)
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
222
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
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
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 Section 22.4 and authorized by Section 27 of the Environmental Protection Act
[415 ILCS 5/22.4 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. ________, _______________________.
SUBPART G: SPENT LEAD-ACID BATTERIES BEING RECLAIMED
223
Section 726.180
Applicability and requirements
a)
The regulations of this Subpart apply to a persons whothat reclaims (including regeneration)
spent lead-acid batteries that are recyclable materials ("spent batteries"). A Ppersons whothat
generates, transports, or collects spent batteries, or whothat stores spent batteries (other than
spent batteries that are to be regenerated), but one that does not reclaim them batteries, areis
not subject to regulation under 35 Ill. Adm. Code 722 through 726 or 35 Ill. Adm. Code 702,
703, or 705, and also are not subject to the requirements of Section 3010 of the Resource
Conservation and Recovery Act.
b)
Owners or operators of facilities that store spent batteries before reclaiming them batteries
(other than spent batteries that are to be regenerated) are subject to the following requirements.
1)
Notification requirements under Section 3010 of the Resource Conservation and
Recovery Act.;
2)
All applicable provisions in 35 Ill. Adm. Code 724.Subparts A, B (but not 35 Ill.
Adm. Code 724.113 (waste analysis)), C,D,E (but not 35 Ill. Adm. Code 724.171 or
724.172 dealing with the use of the manifest and manifest discrepancies), and F
through L;
3)
All applicable provisions in 35 Ill. Adm. Code 725.Subparts A, B (but not 35 Ill.
Adm. Code 725.113 (waste analysis)), C,D,E (but not 35 Ill. Adm. Code 725.171 and
725.172 dealing with the use of the manifest and manifest discrepancies), and F
through L;
4)
All applicable provisions in 35 Ill. Adm. Code 702, 703 and 705.
c) Spent lead-acid batteries that are not managed under this Part, are subject to management under
35 Ill. Adm. Code 733.
(Source: Amended at 20 Ill. Reg. ________, effective ______________________)
SUBPART H: HAZARDOUS WASTE BURNED IN BOILERS
AND INDUSTRIAL FURNACES
Section 726.203
Interim Status Standards for Burners
a)
Purpose, scope, applicability.
1)
General.
A)
The purpose of this Section is to establish minimum national standards for
owners and operators of "existing" BIFs that burn hazardous waste where
such standards define the acceptable management of hazardous waste during
the period of interim status. The standards of this Section apply to owners
and operators of existing facilities until either a permit is issued under Section
726.202(d) or until closure responsibilities identified in this Section are
fulfilled.
224
B)
"Existing" or "in existence" means a BIF for which the owner or operator
filed a certification of precompliance with U.S. EPA pursuant to 40 CFR
266.103(b), incorporated by reference in subsection (b) below; provided,
however, that U.S. EPA has not determined that the certification is invalid.
C)
If a BIF is located at a facility that already has a RCRA permit or interim
status, then the owner or operator shall comply with the applicable regulations
dealing with permit modifications in 35 Ill. Adm. Code 703.280 or changes in
interim status in 35 Ill. Adm. Code 703.155.
2)
Exemptions. The requirements of this Section do not apply to hazardous waste and
facilities exempt under Sections 726.200(b) or 726.208.
3)
Prohibition on burning dioxin-listed wastes. The following hazardous waste listed for
dioxin and hazardous waste derived from any of these wastes must not be burned in a
BIF operating under interim status: U.S. EPA hazardous waste numbers F020, F021,
F022, F023, F026 and F027.
4)
Applicability of 35 Ill. Adm. Code 725 standards. Owners and operators of BIFs that
burn hazardous waste and are operating under interim status are subject to the
following provisions of 35 Ill. Adm. Code 725, except as provided otherwise by this
Section:
A)
In Subpart A of this Part (General), 35 Ill. Adm. Code 725.104;
B)
In Subpart B of this Part (General facility standards), 35 Ill. Adm. Code
725.111 through 725.117;
C)
In Subpart C of this Part (Preparedness and prevention), 35 Ill. Adm. Code
725.131 through 725.137;
D)
In Subpart D of this Part (Contingency plan and emergency procedures), 35
Ill. Adm. Code 725.151 through 725.156;
E)
In Subpart E of this Part (Manifest system, recordkeeping and reporting), 35
Ill. Adm. Code 725.171 through 725.177, except that 35 Ill. Adm. Code
725.171, 725.172 and 725.176 do not apply to owners and operators of on-
site facilities that do not receive any hazardous waste from off-site sources;
F)
In Subpart G of this Part (Closure and post-closure), 35 Ill. Adm. Code
725.211 through 725.215;
G)
In Subpart H of this Part (Financial requirements), 35 Ill. Adm. Code
725.241, 725.242, 725.243 and 725.247 through 725.251, except that the
State of Illinois and the Federal government are exempt from the
requirements of 35 Ill. Adm. Code 725.Subpart H; and
H)
In Subpart BB of this Part (Air emission standards for equipment leaks),
except 35 Ill. Adm. Code 725.950(a).
225
5)
Special requirements for furnaces. The following controls apply during interim status
to industrial furnaces (e.g., kilns, cupolas) that feed hazardous waste for a purpose
other than solely as an ingredient (see subsection (a)(5)(B) above) at any location other
than the hot end where products are normally discharged or where fuels are normally
fired:
A)
Controls.
i)
The hazardous waste must be fed at a location where combustion gas
temperatures are at least 1800° F;
ii)
The owner or operator shall determine that adequate oxygen is
present in combustion gases to combust organic constituents in the
waste and retain documentation of such determination in the facility
record;
iii)
For cement kiln systems, the hazardous waste must be fed into the
kiln; and
iv)
The HC controls of Section 726.204(f) or subsection (c)(5) below
apply upon certification of compliance under subsection (c) below,
irrespective of the CO level achieved during the compliance test.
B)
Burning hazardous waste solely as an ingredient. A hazardous waste is
burned for a purpose other than "solely as an ingredient" if it meets either of
these criteria:
i)
The hazardous waste has a total concentration of nonmetal
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 nonmetal compounds in a waste
as-generated may be reduced to the 500 ppm limit by bona fide
treatment that removes or destroys nonmetal 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 facility record; or
ii)
The hazardous waste has a heating value of 5,000 Btu/lb or more, as
fired, and so is considered to be burned as fuel. The heating value of
a waste as-generated may be reduced to below the 5,000 Btu/lb limit
by bona fide treatment that removes or destroys organic constituents.
The heating value of a waste as-generated may be reduced to below
the 5,000 Btu/lb limit by bona fide treatment that removes or
destroys organic constituents. Blending to augment the heating value
to meet the 5,000 Btu/lb limit is prohibited and documentation that
the waste has not been impermissibly blended must be retained in the
facility record.
6)
Restrictions on burning hazardous waste that is not a fuel. Prior to certification of
compliance under subsection (c) below, owners and operators shall not feed hazardous
waste that has a heating value less than 5000 Btu/lb, as generated, (except that the
226
heating value of a waste as-generated may be increased to above the 5,000 Btu/lb limit
by bona fide treatment; however blending to augment the heating value to meet the
5,000 Btu/lb limit is prohibited and records must be kept to document that
impermissible blending has not occurred) in a BIF, except that:
A)
Hazardous waste may be burned solely as an ingredient; or
B)
Hazardous waste may be burned for purposes of compliance testing (or testing
prior to compliance testing) for a total period of time not to exceed 720 hours;
or
C)
Such waste may be burned if the Agency has documentation to show that,
prior to August 21, 1991:
i)
The BIF was operating under the interim status standards for
incinerators or thermal treatment units, 35 Ill. Adm. Code
725.Subparts O or P; and
ii)
The BIF met the interim status eligibility requirements under 35 Ill.
Adm. Code 703.153 for 35 Ill. Adm. Code 725.Subparts O or P; and
iii)
Hazardous waste with a heating value less than 5,000 Btu/lb was
burned prior to that date; or
D)
Such waste may be burned in a halogen acid furnace if the waste was burned
as an excluded ingredient under 35 Ill. Adm. Code 721.102(e) prior to
February 21, 1991, and documentation is kept on file supporting this claim.
7)
Direct transfer to the burner. If hazardous waste is directly transferred from a
transport vehicle to a BIF without the use of a storage unit, the owner or operator shall
comply with Section 726.211.
b)
Certification of precompliance.
1)
The Board incorporates by reference 40 CFR 266.103(b)(1992); amended at 57 Fed.
Reg. 38564, August 25, 1992. This Section incorporates no later editions or
amendments.
2)
Certain owners and operators were required to file a certification of precompliance
with U.S. EPA by August 21, 1991, pursuant to 40 CFR 266.103(b). No separate
filing is required with the Agency.
c)
Certification of compliance. The owner or operator shall conduct emissions testing to
document compliance with the emissions standards of Sections 726.204(b) through (e),
726.205, 726.206, 726.207, and subsection (a)(5)(A)(iv) above under the procedures
prescribed by this subsection, except under extensions of time provided by subsection (c)(7)
below. Based on the compliance test, the owner or operator shall submit to the Agency, on or
before August 21, 1992, a complete and accurate "certification of compliance" (under
subsection (c)(4) below) with those emission standards establishing limits on the operating
parameters specified in subsection (c)(1) below.
227
1)
Limits on operating conditions. The owner or operator shall establish limits on the
following parameters based on operations during the compliance test (under
procedures prescribed in subsection (c)(4)(D) below) or as otherwise specified and
include these limits with the certification of compliance. The BIF must be operated in
accordance with these operating limits and the applicable emissions standards of
Section 726.204(b) through (e), 726.205, 726.206, 726.207 and subsection
(a)(5)(A)(iv) above at all times when there is hazardous waste in the unit.
A)
Feed rate of total hazardous waste and (unless complying the Tier I or
adjusted Tier I metals feed rate screening limits under Section 726.206(b) or
(e)), pumpable hazardous waste;
B)
Feed rate of each metal in the following feedstreams:
i)
Total feedstreams, except that industrial furnaces that must comply
with the alternative metals implementation approach under
subsection (c)(3)(B) below must specify limits on the concentration
of each metal in collected PM in lieu of feed rate limits for total
feedstreams; and facilities that comply with Tier I or Adjusted Tier I
metals feed rate screening limits may set their operating limits at the
metal feed rate screening limits determined under subsection
726.206(b) or (e).;
BOARD NOTE: Federal subsections 266.103(c)(1)(ii)(A)(1) and
(c)(1)(ii)(A)(2) are condensed into the above subsection.
ii)
Total hazardous waste feed (unless complying with the Tier I or
adjusted Tier I metals feed rate screening limits under Section
726.206(b) or (e)); and
iii)
Total pumpable hazardous waste feed (unless complying with Tier I
or Adjusted Tier I metals feed rate screening limits under subsection
726.206 (b) or (e)).;
C)
Total feed rate of total chlorine and chloride in total feed streams, except that
facilities that comply with Tier I or Adjusted Tier I feed rate screening limits
may set their operating limits at the total chlorine and chloride feed rate
screening limits determined under subsection 726.207(b)(1) or (e);
D)
Total feed rate of ash in total feed streams, except that the ash feed rate for
cement kilns and light-weight aggregate kilns is not limited;
E)
CO concentration, and where required, HC concentration in stack gas. When
complying with the CO controls of Section 726.204(b), the CO limit is 100
ppmv, and when complying with the HC controls of Section 726.204(c), the
HC limit is 20 ppmv. When complying with the CO controls of Section
726.204(c), the CO limit is established based on the compliance test;
F)
Maximum production rate of the device in appropriate units when producing
normal product unless complying with Tier I or Adjusted Tier I feed rate
screening limits for chlorine under subsection 726.207(b)(1) or (e) and for all
228
metals under subsection 726.207(b) or (e), and the uncontrolled particulate
emissions do not exceed the standard under subsection 726.205;
G)
Maximum combustion chamber temperature where the temperature
measurement is as close to the combustion zone as possible and is upstream of
any quench water injection, (unless complying with the Tier I adjusted Tier I
metals feed rate screening limits under Section 726.206(b) or (e));
H)
Maximum flue gas temperature entering a PM control device (unless
complying with Tier I or adjusted Tier I metals feed rate screening limits
under Section 726.206(b) or (e));
I)
For systems using wet scrubbers, including wet ionizing scrubbers (unless
complying with the Tier I or adjusted Tier I metals feed rate screening limits
under Section 726.206(b) or (e) and the total chlorine and chloride feed rate
screening limits under Section 726.207(b)(1) or (e)):
i)
Minimum liquid to flue gas ratio;
ii)
Minimum scrubber blowdown from the system or maximum
suspended solids content of scrubber water; and
iii)
Minimum pH level of the scrubber water;
J)
For systems using venturi scrubbers, the minimum differential gas pressure
across the venturi (unless complying the Tier I or adjusted Tier I metals feed
rate screening limits under Section 726.206(b) or (e) and the total chlorine
and chloride feed rate screening limits under Section 726.207(b)(1) or (e));
K)
For systems using dry scrubbers (unless complying with the Tier I or adjusted
Tier I metals feed rate screening limits under Section 726.206(b) or (e) and
the total chlorine and chloride feed rate screening limits under Section
726.207(b)(1) or (e)):
i)
Minimum caustic feed rate; and
ii)
Maximum flue gas flow rate:;
L)
For systems using wet ionizing scrubbers or electrostatic precipitators (unless
complying with the Tier I or adjusted Tier I metals feed rate screening limits
under Section 726.206(b) or (e) and the total chlorine and chloride feed rate
screening limits under Section 726.207(b)(1) or (e)):
i)
Minimum electrical power in kVA to the precipitator plates; and
ii)
Maximum flue gas flow rate;
M)
For systems using fabric filters (baghouses), the minimum pressure drop
(unless complying with the Tier I or adjusted Tier I metals feed rate screening
limits under Section 726.206(b) or (e) and the total chlorine and chloride feed
rate screening limits under Section 726.207(b)(1) or (e)).
229
2)
Prior notice of compliance testing. At least 30 days prior to the compliance testing
required by subsection (c)(3) below, the owner or operator shall notify the Agency and
submit the following information:
A)
General facility information including:
i)
U.S. EPA facility ID number;
ii)
Facility name, contact person, telephone number and address;
iii)
Person responsible for conducting compliance test, including
company name, address and telephone number, and a statement of
qualifications;
iv)
Planned date of the compliance test;
B)
Specific information on each device to be tested including:
i)
A Description of BIF;
ii)
A scaled plot plan showing the entire facility and location of the BIF;
iii)
A description of the APCS;
iv)
Identification of the continuous emission monitors that are installed,
including: CO monitor; Oxygen monitor; HC monitor, specifying the
minimum temperature of the system and, if the temperature is less
than 150° C, an explanation of why a heated system is not used (see
subsection (c)(5) below) and a brief description of the sample gas
conditioning system;
v)
Indication of whether the stack is shared with another device that will
be in operation during the compliance test; and
vi)
Other information useful to an understanding of the system design or
operation.; and
C)
Information on the testing planned, including a complete copy of the test
protocol and QA/QC plan, and a summary description for each test providing
the following information at a minimum:
i)
Purpose of the test (e.g., demonstrate compliance with emissions of
PM); and
ii)
Planned operating conditions, including levels for each pertinent
parameter specified in subsection (c)(1) above.
3)
Compliance testing.
230
A)
General. Compliance testing must be conducted under conditions for which
the owner or operator has submitted a certification of precompliance under
subsection (b) above and under conditions established in the notification of
compliance testing required by subsection (c)(2) above. The owner or
operator may seek approval on a case-by-case basis to use compliance test
data from one unit in lieu of testing a similar on-site unit. To support the
request, the owner or operator shall provide a comparison of the hazardous
waste burned and other feedstreams, and the design, operation, and
maintenance of both the tested unit and the similar unit. The Agency shall
provide a written approval to use compliance test data in lieu of testing a
similar unit if the Agency finds that the hazardous wastes, devices and the
operating conditions are sufficiently similar, and the data from the other
compliance test is adequate to meet the requirements of this subsection (c).
B)
Special requirements for industrial furnaces that recycle collected PM.
Owners and operators of industrial furnaces that recycle back into the furnace
PM from the APCS shall comply with one of the following procedures for
testing to determine compliance with the metals standards of Section
726.206(c) or (d):
i)
The special testing requirements prescribed in "Alternative Method
for Implementing Metals Controls" in Section 726.Appendix I; or
ii)
Stack emissions testing for a minimum of 6 hours each day while
hazardous waste is burned during interim status. The testing must be
conducted when burning normal hazardous waste for that day at
normal feed rates for that day and when the APCS is operated under
normal conditions. During interim status, hazardous waste analysis
for metals content must be sufficient for the owner or operator to
determine if changes in metals content affect the ability of the unit to
meet the metals emissions standards established under Section
726.206(c) or (d). Under this option, operating limits (under
subsection (c)(1) above) must be established during compliance
testing under this subsection (c)(3) only on the following parameters:
Feed rate of total hazardous waste; Total feed rate of total chlorine
and chloride in total feed streams; Total feed rate of ash in total feed
streams, except that the ash feed rate for cement kilns and light-
weight aggregate kilns is not limited; CO concentration, and where
required, HC concentration in stack gas; Maximum production rate
of the device in appropriate units when producing normal product; or
iii)
Conduct compliance testing to determine compliance with the metals
standards to establish limits on the operating parameters of
subsection (c)(1) above only after the kiln system has been
conditioned to enable it to reach equilibrium with respect to metals
fed into the system and metals emissions. During conditioning,
hazardous waste and raw materials having the same metals content as
will be fed during the compliance test must be fed at the feed rates
that will be fed during the compliance test.
C)
Conduct of compliance testing.
231
i)
If compliance with all applicable emissions standards of Sections
726.204 through 726.207 is not demonstrated simultaneously during
a set of test runs, the operating conditions of additional test runs
required to demonstrate compliance with remaining emissions
standards must be as close as possible to the original operating
conditions.
ii)
Prior to obtaining test data for purposes of demonstrating compliance
with the applicable emissions standards of Sections 726.204 through
726.207 or establishing limits on operating parameters under this
Section, the facility must operate under compliance test conditions
for a sufficient period to reach steady-state operations. Industrial
furnaces that recycle collected PM back into the furnace and that
comply with subsections (c)(3)(B)(i) or (c)(3)(B)(ii) above, however,
need not reach steady state conditions with respect to the flow of
metals in the system prior to beginning compliance testing for
metals.
iii)
Compliance test data on the level of an operating parameter for
which a limit must be established in the certification of compliance
must be obtained during emissions sampling for the pollutant(s) (i.e.,
metals, PM, HCl/chlorine gas, organic compounds) for which the
parameter must be established as specified by subsection (c)(1)
above.
4)
Certification of compliance. Within 90 days of completing compliance testing, the
owner or operator shall certify to the Agency compliance with the emissions standards
of Sections 726.204(b), (c) and (e), 726.205, 726.206, 726.207, and subsection
(a)(5)(A)(iv) above. The certification of compliance must include the following
information:
A)
General facility and testing information including:
i)
U.S. EPA facility ID number;
ii)
Facility name, contact person, telephone number and address;
iii)
Person responsible for conducting compliance testing, including
company name, address and telephone number, and a statement of
qualifications;
iv)
Date(s) of each compliance test;
v)
Description of BIF tested;
vi)
Person responsible for QA/QC, title and telephone number, and
statement that procedures prescribed in the QA/QC plan submitted
under Section 726.203(c)(2)(C) have been followed, or a description
of any changes and an explanation of why changes were necessary.;
232
vii)
Description of any changes in the unit configuration prior to or
during testing that would alter any of the information submitted in
the prior notice of compliance testing under subsection (c)(2) above
and an explanation of why the changes were necessary;
viii)
Description of any changes in the planned test conditions prior to or
during the testing that alter any of the information submitted in the
prior notice of compliance testing under subsection (c)(2) above and
an explanation of why the changes were necessary; and
ix)
The complete report on results of emissions testing.
B)
Specific information on each test including:
i)
Purpose(s) of test (e.g., demonstrate conformance with the emissions
limits for PM, metals, HCl, chlorine gas and CO);
ii)
Summary of test results for each run and for each test including the
following information: Date of run; Duration of run; Time-weighted
average and highest hourly rolling average CO level for each run and
for the test; Highest hourly rolling average HC level, if HC
monitoring is required for each run and for the test; If dioxin and
furan testing is required under Section 726.204(e), time-weighted
average emissions for each run and for the test of chlorinated dioxin
and furan emissions, and the predicted maximum annual average
ground level concentration of the toxicity equivalency factor (defined
in Section 726.200(g)); Time-weighted average PM emissions for
each run and for the test; Time-weighted average HCl and chlorine
gas emissions for each run and for the test; Time-weighted average
emissions for the metals subject to regulation under Section 726.206
for each run and for the test; and QA/QC results.
C)
Comparison of the actual emissions during each test with the emissions limits
prescribed by Sections 726.204(b), (c) and (e), 726.205, 726.206 and 726.207
and established for the facility in the certification of precompliance under
subsection (b) above.
D)
Determination of operating limits based on all valid runs of the compliance
test for each applicable parameter listed in subsection (c)(1) above using
eitherone of the following procedures:
i)
Instantaneous limits. A parameter must be measured and recorded
on an instantaneous basis (i.e., the value that occurs at any time) and
the operating limit specified as the time-weighted average during all
runs of the compliance test; or.
ii)
Hourly rolling average basis. The limit for a parameter must be
established and continuously monitored on an hourly rolling average
basis, as defined in Section 726.200(g). The operating limit for the
parameter must be established based on compliance test data as the
233
average over all test runs of the highest hourly rolling average value
for each run.
iii)
Rolling average limits for carcinogenic metals and lead. Feed rate
limits for the carcinogenic metals and lead must be established either
on an hourly rolling average basis as prescribed by subsection
(c)(4)(D)(ii) above or on (up to) a 24 hour rolling average basis. If
the owner or operator elects to use an averaging period from 2 to 24
hours: The feed rate of each metal must be limited at any time to ten
times the feed rate that would be allowed on a hourly rolling average
basis; The continuous monitor is as defined in Section 726.200(g).
And the operating limit for the feed rate of each metal must be
established based on compliance test data as the average over all test
runs of the highest hourly rolling average feed rate for each run.
iv)
Feed rate limits for metals, total chlorine and chloride and ash. Feed
rate limits for metals, total chlorine and chloride and ash are
established and monitored by knowing the concentration of the
substance (i.e., metals, chloride/chlorine and ash) in each feedstream
and the flow rate of the feedstream. To monitor the feed rate of
these substances, the flow rate of each feedstream must be monitored
under the continuous monitoring requirements of subsections
(c)(4)(D)(i) through (c)(4)(D)(iii) above.
E)
Certification of compliance statement. The following statement must
accompany the certification of compliance:
"I certify under penalty of law that this information was prepared
under my direction or supervision in accordance with a system
designed to ensure that qualified personnel properly gathered and
evaluated the information and supporting documentation. Copies of
all emissions tests, dispersion modeling results and other information
used to determine conformance with the requirements of 35 Ill. Adm.
Code 726.203(c) are available at the facility and can be obtained
from the facility contact person listed above. Based on my inquiry of
the person or persons who manage the facility, or those persons
directly responsible for gathering the information, the information
submitted is, to the best of my knowledge and belief, true, accurate
and complete. I am aware that there are significant penalties for
submitting false information, including the possibility of fine and
imprisonment for knowing violations.
I also acknowledge that the operating limits established pursuant to
35 Ill. Adm. Code 726.203(c)(4)(D) are enforceable limits at which
the facility can legally operate during interim status until a revised
certification of compliance is submitted."
5)
Special requirements for HC monitoring systems. When an owner or operator is
required to comply with the HC controls provided by Sections 726.204(c) or
subsection (a)(5)(A)(iv) above, a conditioned gas monitoring system may be used in
conformance with specifications provided in Section 726.Appendix I provided that the
234
owner or operator submits a certification of compliance without using extensions of
time provided by subsection (c)(7) below. However, owners or operators of facilities
electing to comply with the alternative hydrocarbon provision of Section 726.204(f)
and requesting a time extension under Section 726.219(b) may establish the baseline
HC level and comply with the interim HC limit established by the time extension
using a conditioned gas monitoring system if the Board determines that the owner or
operator has also demonstrated a good faith effort to operate a heated monitoring
system but found it to be impracticable.
6)
Special operating requirements for industrial furnaces that recycle collected PM.
Owners and operators of industrial furnaces that recycle back into the furnace PM
from the APCS must:
A)
When complying with the requirements of subsection (c)(3)(B)(i) above,
comply with the operating requirements prescribed in "Alternative Method to
Implement the Metals Controls" in Section 726.Appendix I; and
B)
When complying with the requirements of subsection (c)(3)(B)(ii) above,
comply with the operating requirements prescribed by that subsection.
7)
Extensions of time.
A)
If the owner or operator does not submit a complete certification of
compliance for all of the applicable emissions standards of Sections 726.204,
726.205, 726.206 and 726.207 by August 21, 1992, the owner or operator
shall either:
i)
Stop burning hazardous waste and begin closure activities under
subsection (l) below for the hazardous waste portion of the facility;
or
ii)
Limit hazardous waste burning only for purposes of compliance
testing (and pretesting to prepare for compliance testing) a total
period of 720 hours for the period of time beginning August 21,
1992, submit a notification to the Agency by August 21, 1992 stating
that the facility is operating under restricted interim status and
intends to resume burning hazardous waste, and submit a complete
certification of compliance by August 23, 1993; or
iii)
Obtain a case-by-case extension of time under subsection (c)(7)(B)
below.
B)
Case-by-case extensions of time. See Section 726.219.
8)
Revised certification of compliance. The owner or operator may submit at any time a
revised certification of compliance (recertification of compliance) under the following
procedures:
A)
Prior to submittal of a revised certification of compliance, hazardous waste
must not be burned for more than a total of 720 hours under operating
conditions that exceed those established under a current certification of
235
compliance, and such burning must be conducted only for purposes of
determining whether the facility can operate under revised conditions and
continue to meet the applicable emissions standards of Sections 726.204,
726.205, 726.206 and 726.207;
B)
At least 30 days prior to first burning hazardous waste under operating
conditions that exceed those established under a current certification of
compliance, the owner or operator shall notify the Agency and submit the
following information:
i)
U.S. EPA facility ID number, and facility name, contact person,
telephone number and address;
ii)
Operating conditions that the owner or operator is seeking to revise
and description of the changes in facility design or operation that
prompted the need to seek to revise the operating conditions;
iii)
A determination that, when operating under the revised operating
conditions, the applicable emissions standards of Sections 726.204,
726.205, 726.206 and 726.207 are not likely to be exceeded. To
document this determination, the owner or operator shall submit the
applicable information required under subsection (b)(2) above; and
iv)
Complete emissions testing protocol for any pretesting and for a new
compliance test to determine compliance with the applicable
emissions standards of Sections 726.204, 726.205, 726.206 and
726.207 when operating under revised operating conditions. The
protocol shall include a schedule of pre-testing and compliance
testing. If the owner or operator revises the scheduled date for the
compliance test, the owner or operator shall notify the Agency in
writing at least 30 days prior to the revised date of the compliance
test;
C)
Conduct a compliance test under the revised operating conditions and the
protocol submitted to the Agency to determine compliance with the applicable
emissions standards of Sections 726.204, 726.205, 726.206 and 726.207; and
D)
Submit a revised certification of compliance under subsection (c)(4) above.
d)
Periodic Recertifications. The owner or operator shall conduct compliance testing and submit
to the Agency a recertification of compliance under provisions of subsection (c) above within
three years from submitting the previous certification or recertification. If the owner or
operator seeks to recertify compliance under new operating conditions, the owner or operator
shall comply with the requirements of subsection (c)(8) above.
e)
Noncompliance with certification schedule. If the owner or operator does not comply with the
interim status compliance schedule provided by subsections (b), (c) and (d) above, hazardous
waste burning must terminate on the date that the deadline is missed, closure activities must
begin under subsection (l) below, and hazardous waste burning must not resume except under
an operating permit issued under 35 Ill. Adm. Code 703.232. For purposes of compliance with
the closure provisions of subsection (l) below and 35 Ill. Adm. Code 725.212(d)(2) and
236
725.213, the BIF has received "the known final volume of hazardous waste" on the date the
deadline is missed.
f)
Start-up and shut-down. Hazardous waste (except waste fed solely as an ingredient under the
Tier I (or adjusted Tier I) feed rate screening limits for metals and chloride/chlorine) must not
be fed into the device during start-up and shut-down of the BIF, unless the device is operating
within the conditions of operation specified in the certification of compliance.
g)
Automatic waste feed cutoff. During the compliance test required by subsection (c)(3) above
and upon certification of compliance under subsection (c) above, a BIF must be operated with a
functioning system that automatically cuts off the hazardous waste feed when the applicable
operating conditions specified in subsections (c)(1)(A) and (c)(1)(E) through (c)(1)(M) above
deviate from those established in the certification of compliance. In addition:
1)
To minimize emissions of organic compounds, the minimum combustion chamber
temperature (or the indicator of combustion chamber temperature) that occurred
during the compliance test must be maintained while hazardous waste or hazardous
waste residues remain in the combustion chamber, with the minimum temperature
during the compliance test defined as either:
A)
If compliance with the combustion chamber temperature limit is based on a
hourly rolling average, the minimum temperature during the compliance test
is considered to be the average over all runs of the lowest hourly rolling
average for each run; or
B)
If compliance with the combustion chamber temperature limit is based on an
instantaneous temperature measurement, the minimum temperature during the
compliance test is considered to be the time-weighted average temperature
during all runs of the test; and
2)
Operating parameters limited by the certification of compliance must continue to be
monitored during the cutoff, and the hazardous waste feed must not be restarted until
the levels of those parameters comply with the limits established in the certification of
compliance.
h)
Fugitive emissions. Fugitive emissions must be controlled by:
1)
Keeping the combustion zone totally sealed against fugitive emissions; or
2)
Maintaining the combustion zone pressure lower than atmospheric pressure; or
3)
An alternate means of control that the owner or operator demonstrates provides
fugitive emissions control equivalent to maintenance of combustion zone pressure
lower than atmospheric pressure. Support for such demonstration must be included in
the operating record.
i)
Changes. A BIF must cease burning hazardous waste when combustion properties, or feed
rates of the hazardous waste, other fuels or industrial furnace feedstocks, or the BIF design or
operating conditions deviate from the limits specified in the certification of compliance.
j)
Monitoring and Inspections.
237
1)
The owner or operator shall monitor and record the following, at a minimum, while
burning hazardous waste:
A)
Feed rates and composition of hazardous waste, other fuels and industrial
furnace feed stocks, and feed rates of ash, metals, and total chlorine and
chloride as necessary to ensure conformance with the certification of
precompliance or certification of compliance;
B)
CO, oxygen and, if applicable, HC, on a continuous basis at a common point
in the BIF downstream of the combustion zone and prior to release of stack
gases to the atmosphere in accordance with the operating limits specified in
the certification of compliance. CO, HC and oxygen monitors must be
installed, operated and maintained in accordance with methods specified in
Section 726.Appendix I.; and
C)
Upon the request of the Agency, sampling and analysis of the hazardous
waste (and other fuels and industrial furnace feed stocks as appropriate) and
the stack gas emissions must be conducted to verify that the operating
conditions established in the certification of precompliance or certification of
compliance achieve the applicable standards of Sections 726.204, 726.205,
726.206 and 726.207.
2)
The BIF and associated equipment (pumps, valves, pipes, fuel storage tanks, etc.)
must be subjected to thorough visual inspection when they contain hazardous waste, at
least daily for leaks, spills, fugitive emissions and signs of tampering.
3)
The automatic hazardous waste feed cutoff system and associated alarms must be
tested at least once every 7 days when hazardous waste is burned to verify operability,
unless the owner or operator can demonstrate that weekly inspections will unduly
restrict or upset operations and that less frequent inspections will be adequate.
Support for such demonstration must be included in the operating record. At a
minimum, operational testing must be conducted at least once every 30 days.
4)
These monitoring and inspection data must be recorded and the records must be placed
in the operating log.
k)
Recordkeeping. The owner or operator shall keep in the operating record of the facility all
information and data required by this Section until closure of the BIF unit.
l)
Closure. At closure, the owner or operator shall remove all hazardous waste and hazardous
waste residues (including, but not limited to, ash, scrubber waters and scrubber sludges) from
the BIF and shall comply with 35 Ill. Adm. Code 725.211 through 725.215.
(Source: Amended at 20 Ill. Reg. ________, effective ______________________)
Section 726.204
Standards to Control Organic Emissions
a)
DRE standard.
238
1)
General. Except as provided in subsection (a)(3) below, a BIF burning hazardous
waste must achieve a DRE of 99.99% for all organic hazardous constituents in the
waste feed. To demonstrate conformance with this requirement, 99.99% DRE must
be demonstrated during a trial burn for each principal organic hazardous constituent
(POHC) designated (under subsection (a)(2) below) in its permit for each waste feed.
DRE is determined for each POHC from the following equation:
DRE = 100(I - O)/I
where:
I = Mass feed rate of one POHC in the hazardous waste fired to the BIF; and
O = Mass emission rate of the same POHC present in stack gas prior to release to the
atmosphere.
2)
Designation of POHCs. POHCs are those compounds for which compliance with the
DRE requirements of this Section must be demonstrated in a trial burn in conformance
with procedures prescribed in 35 Ill. Adm. Code 703.232. One or more POHCs must
be designated by the Agency for each waste feed to be burned. POHCs must be
designated based on the degree of difficulty of destruction of the organic constituents
in the waste and on their concentrations or mass in the waste feed considering the
results of waste analyses submitted with Part B of the permit application. POHCs are
most likely to be selected from among those compounds listed in 35 Ill. Adm. Code
721.Appendix H that are also present in the normal waste feed. However, if the
applicant demonstrates to the Agency that a compound not listed in 35 Ill. Adm. Code
721.Appendix H or not present in the normal waste feed is a suitable indicator of
compliance with the DRE requirements of this Section, that compound must be
designated as a POHC. Such POHCs need not be toxic or organic compounds.
3)
Dioxin-listed waste. A BIF burning hazardous waste containing (or derived from)
U.S. EPA Hazardous Wastes Nos. F020, F021, F022, F023, F026 or F027 must
achieve a destruction and removal efficiency (DRE) of 99.9999% for each POHC
designated (under subsection (a)(2) above) in its permit. This performance must be
demonstrated on POHCs that are more difficult to burn than tetra-, penta- and
hexachlorodibenzo-p-dioxins and dibenzofurans. DRE is determined for each POHC
from the equation in subsection (a)(1) above. In addition, the owner or operator of the
BIF shall notify the Agency of intent to burn U.S. EPA Hazardous Waste Nos. F020,
F021, F022, F023, F026 or F027.
4)
Automatic waiver of DRE trial burn. Owners and operators of boilers operated under
the special operating requirements provided by Section 726.210 are considered to be in
compliance with the DRE standard of subsection (a)(1) above and are exempt from the
DRE trial burn.
5)
Low risk waste. Owners and operators of BIFs that burn hazardous waste in
compliance with the requirements of Section 726.209(a) are considered to be in
compliance with the DRE standard of subsection (a)(1) above and are exempt from the
DRE trial burn.
b)
CO standard.
239
1)
Except as provided in subsection (c) below, the stack gas concentration of CO from a
BIF burning hazardous waste cannot exceed 100 ppmv on an hourly rolling average
basis (i.e., over any 60 minute period), continuously corrected to 7 percent oxygen,
dry gas basis.
2)
CO and oxygen must be continuously monitored in conformance with "Performance
Specifications for Continuous Emission Monitoring of Carbon Monoxide and Oxygen
for Incinerators, Boilers, and Industrial Furnaces Burning Hazardous Waste" in
Section 726.Appendix I.
3)
Compliance with the 100 ppmv CO limit must be demonstrated during the trial burn
(for new facilities or an interim status facility applying for a permit) or the compliance
test (for interim status facilities). To demonstrate compliance, the highest hourly
rolling average CO level during any valid run of the trial burn or compliance test must
not exceed 100 ppmv.
c)
Alternative CO standard.
1)
The stack gas concentration of CO from a BIF burning hazardous waste may exceed
the 100 ppmv limit provided that stack gas concentrations of HCs do not exceed 20
ppmv, except as provided by subsection (f) below for certain industrial furnaces.
2)
HC limits must be established under this Section on an hourly rolling average basis
(i.e., over any 60 minute period), reported as propane, and continuously corrected to 7
percent oxygen, dry gas basis.
3)
HC must be continuously monitored in conformance with "Performance Specifications
for Continuous Emission Monitoring of Hydrocarbons for Incinerators, Boilers, and
Industrial Furnaces Burning Hazardous Waste" in Section 726.Appendix I. CO and
oxygen must be continuously monitored in conformance with subsection (b)(2) above.
4)
The alternative CO standard is established based on CO data during the trial burn (for
a new facility) and the compliance test (for an interim status facility). The alternative
CO standard is the average over all valid runs of the highest hourly average CO level
for each run. The CO limit is implemented on an hourly rolling average basis, and
continuously corrected to 7 percent oxygen, dry gas basis.
d)
Special requirements for furnaces. Owners and operators of industrial furnaces (e.g., kilns,
cupolas) that feed hazardous waste for a purpose other than solely as an ingredient (see Section
726.203(a)(5)(B)) at any location other than the end where products are normally discharged
and where fuels are normally fired must comply with the HC limits provided by subsections (c)
above or (f) below irrespective of whether stack gas CO concentrations meet the 100 ppmv
limit of subsection (b) above.
e)
Controls for dioxins and furans. Owners and operators of BIFs that are equipped with a dry
PM control device that operates within the temperature range of 450 through 750° F, and
industrial furnaces operating under an alternative HC limit established under subsection (f)
below shall conduct a site-specific risk assessment as follows to demonstrate that emissions of
chlorinated dibenzo-p-dioxins and dibenzofurans do not result in an increased lifetime cancer
risk to the hypothetical maximum exposed individual (MEI) exceeding 1´10
-5
(1 in 100,000):
240
1)
During the trial burn (for new facilities or an interim status facility applying for a
permit) or compliance test (for interim status facilities), determine emission rates of
the tetra-octa congeners of chlorinated dibenzo-p-dioxins (PCDDs) and dibenzofurans
(CDDs/CDFs) using Method 23, "Determination of Polychlorinated Dibenzo-p-
Dioxins and Polychlorinated Dibenzofurans (PCDFs) from Stationary Sources", in
Section 726.Appendix I;
2)
Estimate the 2,3,7,8-TCDD toxicity equivalence of the tetra-octa CDDs/CDFs
congeners using "Procedures for Estimating the Toxicity Equivalence of Chlorinated
Dibenzo-p-Dioxin and Dibenzofuran Congeners" in Section 726.Appendix I. Multiply
the emission rates of CDD/CDF congeners with a toxicity equivalence greater than
zero (see the procedure) by the calculated toxicity equivalence factor to estimate the
equivalent emission rate of 2,3,7,8-TCDD;
3)
Conduct dispersion modeling using methods recommended in 40 CFR 51, Appendix
W, as incorporated by reference at 35 Ill. Adm. Code 720.111 ("Guideline on Air
Quality Models (Revised)" (1986) and its supplements), the "Hazardous Waste
Combustion Air Quality Screening Procedure", provided in Appendix I, or in
"Screening Procedures for Estimating Air Quality Impact of Stationary Sources,
Revised" (incorporated by reference in 35 Ill. Adm. Code 720.111) to predict the
maximum annual average off-site ground level concentration of 2,3,7,8-TCDD
equivalents determined under subsection (e)(2) above. The maximum annual average
on-site concentration must be used when a person resides on-site; and
4)
The ratio of the predicted maximum annual average ground level concentration of
2,3,7,8-TCDD equivalents to the risk-specific dose (RSD) for 2,3,7,8-TCDD provided
in Section 726.Appendix E (2.2´10
-7
) must not exceed 1.0.
f) Alternative HC limit for furnaces with organic matter in raw material. For industrial furnaces
that cannot meet the 20 ppmv HC limit because of organic matter in normal raw material, the
Agency shall establish an alternative HC limit on a case-by-case basis (under a Part B permit
proceeding) at a level that ensures that flue gas HC (and CO) concentrations when burning
hazardous waste are not greater than when not burning hazardous waste (the baseline HC level)
provided that the owner or operator complies with the following requirements. However,
cement kilns equipped with a by-pass duct meeting the requirements of subsection (g) below
are not eligible for an alternative HC limit.
1) The owner or operator shall demonstrate that the facility is designed and operated to
minimize HC emissions from fuels and raw materials, and that the facility is
producing normal products under normal operating conditions feeding normal
feedstocks and fuels when the baseline HC (and CO) level is determined. The
baseline HC level is defined as the average over all valid test runs of the highest
hourly rolling average value for each run when the facility does not burn hazardous
waste, adjusted as appropriate to consider the variability of hydrocarbon levels under
good combustion operating conditions. The baseline CO level is determined based on
the test runs used to establish the baseline HC level and is defined as the average over
all test runs of the highest hourly rolling average CO value for each run. More than
one baseline level must be determined if the facility operates under different modes
that generate significantly different HC (and CO) levels;
241
2) The owner or operator shall develop an approach to monitor over time changes in the
operation of the facility that could reduce the baseline HC level;
3) The owner or operator shall conduct emissions testing during the trial burn to:
A) Determine the baseline HC (and CO) level;
B) Demonstrate that, when hazardous waste is burned, HC (and CO) levels do
not exceed the baseline level; and
C) Identify the types and concentrations of organic compounds listed in 35 Ill.
Adm. Code 721.Appendix H, that are emitted and conduct dispersion
modeling to predict the maximum annual average ground level concentration
of each organic compound. On-site ground level concentrations must be
considered for this evaluation if a person resides on site.
i) Sampling and analysis of organic emissions must be conducted using
procedures prescribed by the Agency pursuant to 35 Ill. Adm. Code
703.208(a).
ii) Dispersion modeling must be conducted according to procedures
provided by subsection (e)(2) above; and
D) Demonstrate that maximum annual average ground level concentrations of the
organic compounds identified in subsection (f)(3)(C) above do not exceed the
following levels:
i) For the noncarcinogenic compounds listed in Section 726.Appendix
D, the levels established in that Section;
ii) For the carcinogenic compounds listed in Section 726.Appendix E,
the sum for all compounds of the ratios of the actual ground level
concentration to the level established in that Section cannot exceed
1.0. To estimate the health risk from chlorinated dibenzo-p-dioxins
and dibenzofuran congeners, use the procedures prescribed by
subsection (e)(3) above to estimate the 2,3,7,8-TCDD toxicity
equivalence of the congeners.
iii) For compounds not listed in Section 726.Appendix D or
726.Appendix E, 0.1 mg/m
3
(micrograms per cubic meter).
4) All HC levels specified under this subsection are to be monitored and reported as
specified in subsections (c)(1) and (c)(2) above.
gf)
Monitoring CO and HC in the by-pass duct of a cement kiln. Cement kilns may comply with
the CO and HC limits provided by subsections (b), (c) and (d) above by monitoring in the by-
pass duct provided that:
1)
Hazardous waste is fired only into the kiln and not at any location downstream from
the kiln exit relative to the direction of gas flow; and
242
2)
The by-pass duct diverts a minimum of 10% of kiln off-gas into the duct.
hg)
Use of emissions test data to demonstrate compliance and establish operating limits.
Compliance with the requirements of this Section must be demonstrated simultaneously by
emissions testing or during separate runs under identical operating conditions. Further, data to
demonstrate compliance with the CO and HC limits of this Section or to establish alternative
CO or HC limits under this Section must be obtained during the time that DRE testing, and
where applicable, CDD/CDF testing under subsection (e) above and comprehensive organic
emissions testing under subsection (f) above is conducted.
ih)
Enforcement. For the purposes of permit enforcement, compliance with the operating
requirements specified in the permit (under Section 726.202) will be regarded as compliance
with this Section. However, evidence that compliance with those permit conditions is
insufficient to ensure compliance with the requirements of this Section is "information"
justifying modification or revocation and re-issuance of a permit under 35 Ill. Adm. Code
703.270 et seq.
(Source: Amended at 20 Ill. Reg. ________, effective ______________________)
TITLE 35: ENVIRONMENTAL PROTECTION
SUBTITLE G: WASTE DISPOSAL
CHAPTER I: POLLUTION CONTROL BOARD
SUBCHAPTER c: HAZARDOUS WASTE OPERATING REQUIREMENTS
PART 728
LAND DISPOSAL RESTRICTIONS
SUBPART A: GENERAL
Section
728.101 Purpose, Scope and Applicability
728.102 Definitions
728.103 Dilution Prohibited as a Substitute for Treatment
728.104 Treatment Surface Impoundment Exemption
728.105 Procedures for case-by-case Extensions to an Effective Date
728.106 Petitions to Allow Land Disposal of a Waste Prohibited under Subpart C
728.107 Waste Analysis and Recordkeeping
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
728.111 Second Third
728.112 Third Third
728.113 Newly Listed Wastes
728.114 Surface Impoundment exemptions
SUBPART C: PROHIBITION ON LAND DISPOSAL
Section
243
728.130 Waste Specific Prohibitions -- Solvent Wastes
728.131 Waste Specific Prohibitions -- Dioxin-Containing Wastes
728.132 Waste Specific Prohibitions -- California List Wastes
728.133 Waste Specific Prohibitions: First Third Wastes
728.134 Waste Specific Prohibitions -- Second Third Wastes
728.135 Waste Specific Prohibitions -- Third Third Wastes
728.136 Waste Specific Prohibitions -- Newly Listed Wastes
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 Statutory Prohibitions
SUBPART D: TREATMENT STANDARDS
Section
728.140 Applicability of Treatment Standards
728.141 Treatment Standards Expressed as Concentrations in Waste Extract
728.142 Treatment Standards Expressed as Specified Technologies
728.143 Treatment Standards Expressed as Waste Concentrations
728.144 Adjustment of Treatment Standard
728.145 Treatment Standards for Hazardous Debris
728.146 Alternative Treatment Standards Based on HTMR
728.148 Universal Treatment Standards
SUBPART E: PROHIBITIONS ON STORAGE
Section
728.150 Prohibitions on Storage of Restricted Wastes
728.Appendix A Toxicity Characteristic Leaching Procedure (TCLP)
728.Appendix B
Treatment Standards (As concentrations in the Treatment Residual Extract)
728.Appendix C List of Halogenated Organic Compounds
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
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
728.Table H
Wastes Excluded from CCW Treatment Standards
728.Table T
Treatment Standards for Hazardous Wastes
728.Table U
Universal Treatment Standards (UTS)
244
AUTHORITY: Implementing Section 22.4 and authorized by Section 27 of the Environmental Protection Act
[415 ILCS 5/22.4 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; amendment withdrawn at 15 Ill. Reg. 14716, October 11,
1991; amended in R91-13 at 16 Ill. Reg. 9619, effective June 9, 1992; amended in R92-10 at 17 Ill. Reg. 5727,
effective March 26, 1993; amended in R93-4 at 17 Ill. Reg. 20692, effective November 22, 1993; amended in
R93-16 at 18 Ill. Reg. 6799, effective April 26, 1994; amended in R94-7 at 18 Ill. Reg. 12203, effective July
29, 1994; amended in R94-17 at 18 Ill. Reg. 17563, effective November 23, 1994; amended in R95-6 at 19 Ill.
Reg. 9660, effective June 27, 1995; amended in R95-20 at 20 Ill. Reg. ________, _______________________.
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)
Wastes that are hazardous only because they exhibit a hazardous characteristic and that
are otherwise prohibited from land disposal under this Part are not prohibited from
land disposal if the wastes:
A)
Are disposed into a nonhazardous or hazardous waste injection well, as
defined in 35 Ill. Adm. Code 704.106(a);
B)
Do not exhibit any prohibited characteristic of hazardous waste at the point of
injection; and
C)
If, at the point of generation, the injected wastes include D001 High TOC
subcategory wastes or D012-D017 pesticide wastes that are prohibited under
Section 728.117(c), those wastes have been treated to meet the treatment
standards of Section 728.140 prior to injection.
245
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. §§ 9601 et seq.).
e)
The following hazardous wastes are not subject to any provision of this Part:
1)
Wastes 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 pesticides that a farmer disposes of pursuant to 35 Ill. Adm. Code 722.170;
3)
Wastes identified or listed as hazardous after November 8, 1984, for which U.S. EPA
has not promulgated land disposal prohibitions or treatment standards.;
4)
De minimis losses to wastewater treatment systems of commercial chemical product or
chemical intermediates that are ignitable (D001) or corrosive (D002) or that are
organic constituents that exhibit the characteristic of toxicity (D012-D043) and that
contain underlying hazardous constituents, as defined in Section 728.102 of this Part,
are not considered to be prohibited wastes. "De minimis" is 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 purging;
relief device discharges; discharges from safety showers and rinsing and cleaning of
personal safety equipment; and rinsate from empty containers or from containers that
are rendered empty by that rinsing.;
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 headwork 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 268.150 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; and
3)
Thermostats, as described in 35 Ill. Adm. Code 733.104.
fg)
This Part is cumulative with the land disposal restrictions of 35 Ill. Adm. Code 729. The
Environmental Protection Agency (Agency) shall not issue a wastestream authorization
246
pursuant to 35 Ill. Adm. Code 709 or Sections 22.6 or 39(h) of the Environmental Protection
Act [415 ILCS 5/22.6 or 39.6(h)] unless the waste meets the requirements of this Part as well
as 35 Ill. Adm. Code 729.
(Source: Amended at 20 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 mg/l
3
;
or Technology
Code
4
Concentration in
mg/kg
3
unless noted
as "mg/l TCLP"; or
Technology Code
4
D001
Ignitable Characteristic Wastes, except for the Section 721.121(a)(1) High TOC Subcategory, that are managed
in non-CWA or non-CWA-equivalent or non-Class I SDWA systems.
NA
NA
DEACT and meet
Section 728.148
standards; or
RORGS; or CMBST
DEACT and meet
Section 728.148
standards; or
RORGS; or CMBST
D001
Ignitable Characteristic Wastes, except for the Section 721.121(a)(1) High TOC Subcategory, that are managed
in CWA or CWA-equivalent or Class I SDWA systems
NA
NA
DEACT
DEACT
D001
High TOC Ignitable Characteristic Liquids Subcategory based on 35 Ill. Adm. Code 721.121(a)(1) - Greater
than or equal to 10% total organic carbon.
(Note: This subcategory consists of nonwastewaters only.)
NA
NA
NA
RORGS; or CMBST
D002
Corrosive Characteristic Wastes that are managed in non-CWA or non-CWA equivalent or non-Class I SDWA
systems.
NA
NA
DEACT
and meet Section
728.148 standards
DEACT
and meet Section
728.148 standards
D002
Corrosive Characteristic Wastes that are managed in CWA, CWA equivalent, or Class I SDWA systems.
247
NA
NA
DEACT
DEACT
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
Reactive Sulfides Subcategory based on 35 Ill. Adm. Code 721.123(a)(5).
NA
NA
DEACT
DEACT
D003
Explosive subcategory based on 35 Ill. Adm. Code 721.123(a)(6), (a)(7), and (a)(8).
NA
NA
DEACT
DEACT
D003
Other Reactives Subcategory based on 35 Ill. Adm. Code 721.123(a)(1).
NA
NA
DEACT
DEACT
D003
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
D003
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
Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for arsenic based on the extraction
procedure (EP) in SW-846 Method 1310.
Arsenic
7440-38-2
5.0
5.0 mg/l EP
Arsenic; alternate
6
standard for
nonwastewaters only.
7440-38-2
NA
5.0 mg/l TCLP
D005
Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for barium based on the extraction
procedure (EP) in SW-846 Method 1310.
Barium
7440-39-3
100
100 mg/l TCLP
248
D006
Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for cadmium based on the extraction
procedure (EP) in SW-846 Method 1310.
Cadmium
7440-43-9
1.0
1.0 mg/l TCLP
D006
Cadmium Containing Batteries Subcategory
(Note: This subcategory consists of nonwastewaters only.)
Cadmium
7440-43-9
NA
RTHRM
D007
Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for chromium based on the
extraction procedure (EP) in SW-846 Metod 1310.
Chromium (Total)
7440-47-3
5.0
5.0 mg/l TCLP
D008
Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for lead based on the extraction
procedure (EP) in SW-846 Method 1310.
Lead
7439-92-1
5.0
5.0 mg/l EP
Lead; alternate
6
standard for
nonwastewaters only
7439-92-1
NA
5.0 mg/l TCLP
D008
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).).
(Note: This subcategory consists of nonwastewaters only.)
Lead
7439-92-1
NA
RLEAD
D008
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.)
(Note: This subcategory consists of nonwastewaters only.)
Lead
7439-92-1
NA
MACRO
D009
Nonwastewaters that exhibit, or are expected to exhibit, the characteristic of toxicity for mercury based on the
extraction procedure (EP) in SW-846 Method 1310; 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
D009
Nonwastewaters that exhibit, or are expected to exhibit, the characteristic of toxicity for mercury based on the
extraction procedure (EP) in SW-846 Method 1310; 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)
249
Mercury
7439-97-6
NA
RMERC
D009
Nonwastewaters that exhibit, or are expected to exhibit, the characteristic of toxicity for mercury based on the
extraction procedure (EP) in SW-846 Method 1310; and contain less than 260 mg/kg total mercury.
(Low Mercury Subcategory)
Mercury
7439-97-6
NA
0.20 mg/l TCLP
All D009 wastewaters.
Mercury
7439-97-6
0.20
NA
D009
Elemental mercury contaminated with radioactive materials.
(Note: This subcategory consists of nonwastewaters only.)
Mercury
7439-97-6
NA
AMLGM
D009
Hydraulic oil contaminated with Mercury Radioactive Materials Subcategory.
(Note: This subcategory consists of nonwastewaters only.)
Mercury
7439-97-6
NA
IMERC
D010
Wastes that exhibit, or are expected to exhibit, the characteristic or toxicity for selenium based on the extraction
procedure (EP) in SW-846 Method 1310.
Selenium
7782-49-2
1.0
5.7 mg/l TCLP
D011
Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for silver based on the extraction
procedure (EP) in SW-846 Method 1310.
Silver
7440-22-4
5.0
5.0 mg/l TCLP
D012
Wastes that are TC for Endrin based on the TCLP in SW-846 Method 1311.
Endrin
72-20-8
BIODG; or INCIN
0.13
and meet Section
728.148 standards
Endrin aldehyde
7421-93-4
BIODG; or INCIN
0.13
and meet Section
728.148 standards
D013
Wastes that are TC for Lindane based on the TCLP in SW-846 Method 1311.
250
alpha-BHC
319-84-6
CARBN; or INCIN
0.066
and meet Section
728.148 standards
beta-BHC
319-85-7
CARBN; or INCIN
0.066
and meet Section
728.148 standards
delta-BHC
319-86-8
CARBN; or INCIN
0.066
and meet Section
728.148 standards
gamma-BHC (Lindane)
58-89-9
CARBN; or INCIN
0.066
and meet Section
728.148 standards
D014
Wastes that are TC for Methoxychlor based on the TCLP in SW-846 Method 1311.
Methoxychlor
72-43-5
WETOX or INCIN
0.18
and meet Section
728.148 standards
D015
Wastes that are TC for Toxaphene based on the TCLP in SW-846 Method 1311.
Toxaphene
8001-35-2
BIODG or INCIN
2.6
and meet Section
728.148 standards
D016
Wastes that are TC for 2,4-D (2,4-Dichlorophenoxyacetic acid) based on the TCLP in SW-846 Method 1311.
2,4-D (2,4-Dichlorophenoxyacetic
acid)
94-75-7
CHOXD, BIODG,
or INCIN
10
and meet Section
728.148 standards
D017
Wastes that are TC for 2,4,5-TP (Silvex) based on the TCLP in SW-846 Method 1311.
2,4,5-TP (Silvex)
93-72-1
CHOXD or INCIN
7.9
and meet Section
728.148 standards
D018
Wastes that are TC for Benzene based on the TCLP in SW-846 Method 1311 and that are managed in non-CWA
or non-CWA equivalent or non-Class I SDWA systems only.
Benzene
71-43-2
0.14
and meet Section
728.148 standards
10
and meet Section
728.148 standards
D019
Wastes that are TC for Carbon tetrachloride based on the TCLP in SW-846 Method 1311 and that are managed
in non-CWA or non-CWA equivalent or non-Class I SDWA systems only.
Carbon tetrachloride
56-23-5
0.057
and meet Section
728.148 standards
6.0
and meet Section
728.148 standards
251
D020
Wastes that are TC for Chlordane based on the TCLP in SW-846 Method 1311 and that are managed in non-
CWA or non-CWA equivalent or non-Class I SDWA systems only.
Chlordane (alpha and gamma
isomers)
57-74-9
0.0033
and meet Section
728.148 standards
0.26
and meet Section
728.148 standards
D021
Wastes that are TC for Chlorobenzene based on the TCLP in SW-846 Method 1311 and that are managed in
non-CWA or non-CWA equivalent or non-Class I SDWA systems only.
Chlorobenzene
108-90-7
0.057
and meet Section
728.148 standards
6.0
and meet Section
728.148 standards
D022
Wastes that are TC for Chloroform based on the TCLP in SW-846 Method 1311 and that are managed in non-
CWA or non-CWA equivalent or non-Class I SDWA systems only.
Chloroform
67-66-3
0.046
and meet Section
728.148 standards
6.0
and meet Section
728.148 standards
D023
Wastes that are TC for o-Cresol based on the TCLP in SW-846 Method 1311 and that are managed in non-CWA
or non-CWA equivalent or non-Class I SDWA systems only.
o-Cresol`
95-48-7
0.11
and meet Section
728.148 standards
5.6
and meet Section
728.148 standards
D024
Wastes that are TC for m-Cresol based on the TCLP in SW-846 Method 1311 and that are managed in non-
CWA or non-CWA equivalent or non-Class I SDWA systems only.
m-Cresol
(difficult to distinguish from p-
cresol)
108-39-4
0.77
and meet Section
728.148 standards
5.6
and meet Section
728.148 standards
D025
Wastes that are TC for p-Cresol based on the TCLP in SW-846 Method 1311 and that are managed in non-CWA
or non-CWA equivalent or non-Class I SDWA systems only.
p-Cresol
(difficult to distinguish from m-
cresol)
106-44-5
0.77
and meet Section
728.148 standards
5.6
and meet Section
728.148 standards
D026
Wastes that are TC for Cresols (Total) based on the TCLP in SW-846 Method 1311 and that are managed in
non-CWA or non-CWA equivalent or non-Class I SDWA systems only.
Cresol-mixed isomers (Cresylic
acid)
(sum of o-, m-, and p-cresol con-
centrations)
1319-77-3
0.88
and meet Section
728.148 standards
11.2
and meet Section
728.148 standards
252
D027
Wastes that are TC for p-Dichlorobenzene based on the TCLP in SW-846 Method 1311 and that are managed in
non-CWA or non-CWA equivalent or non-Class I SDWA systems only.
p-Dichlorobenzene (1,4-Dichloro-
benzene)
106-46-7
0.090
and meet Section
728.148 standards
6.0
and meet Section
728.148 standards
D028
Wastes that are TC for 1,2-Dichloroethane based on the TCLP in SW-846 Method 1311 and that are managed in
non-CWA or non-CWA equivalent or non-Class I SDWA systems only.
1,2-Dichloroethane
107-06-2
0.21
and meet Section
728.148 standards
6.0
and meet Section
728.148 standards
D029
Wastes that are TC for 1,1-Dichloroethylene based on the TCLP in SW-846 Method 1311 and that are managed
in non-CWA or non-CWA equivalent or non-Class I SDWA systems only.
1,1-Dichloroethylene
75-35-4
0.025
and meet Section
728.148 standards
6.0
and meet Section
728.148 standards
D030
Wastes that are TC for 2,4-Dinitrotoluene based on the TCLP in SW-846 Method 1311 and that are managed in
non-CWA or non-CWA equivalent or non-Class I SDWA systems only.
2,4-Dinitrotoluene
121-14-2
0.32
and meet Section
728.148 standards
140
and meet Section
728.148 standards
D031
Wastes that are TC for Heptachlor based on the TCLP in SW-846 Method 1311 and that are managed in non-
CWA or non-CWA equivalent or non-Class I SDWA systems only.
Heptachlor
76-44-8
0.0012
0.066
and meet Section
728.148 standards
Heptachlor epoxide
1024-57-3
0.016
and meet Section
728.148 standards
0.066
and meet Section
728.148 standards
D032
Wastes that are TC for Hexachlorobenzene based on the TCLP in SW-846 Method 1311 and that are managed in
non-CWA or non-CWA equivalent or non-Class I SDWA systems only.
Hexachlorobenzene
118-74-1
0.055
and meet Section
728.148 standards
10
and meet Section
728.148 standards
D033
Wastes that are TC for Hexachlorobutadiene based on the TCLP in SW-846 Method 1311 and that are managed
in non-CWA or non-CWA equivalent or non-Class I SDWA systems only.
253
Hexachlorobutadiene
687-68-3
0.055
and meet Section
728.148 standards
5.6
and meet Section
728.148 standards
D034
Wastes that are TC for Hexachloroethane based on the TCLP in SW-846 Method 1311 and that are managed in
non-CWA or non-CWA equivalent or non-Class I SDWA systems only.
Hexachloroethane
67-72-1
0.055
and meet Section
728.148 standards
30
and meet Section
728.148 standards
D035
Wastes that are TC for Methyl ethyl ketone based on the TCLP in SW-846 Method 1311 and that are managed in
non-CWA or non-CWA equivalent or non-Class I SDWA systems only.
Methyl ethyl ketone
78-93-3
0.28
and meet Section
728.148 standards
36
and meet Section
728.148 standards
D036
Wastes that are TC for Nitrobenzene based on the TCLP in SW-846 Method 1311 and that are managed in non-
CWA or non-CWA equivalent or non-Class I SDWA systems only.
Nitrobenzene
98-95-3
0.068
and meet Section
728.148 standards
14
and meet Section
728.148 standards
D037
Wastes that are TC for Pentachlorophenol based on the TCLP in SW-846 Method 1311 and that are managed in
non-CWA or non-CWA equivalent or non-Class I SDWA systems only.
Pentachlorophenol
87-86-5
0.089
and meet Section
728.148 standards
7.4
and meet Section
728.148 standards
D038
Wastes that are TC for Pyridine based on the TCLP in SW-846 Method 1311 and that are managed in non-CWA
or non-CWA equivalent or non-Class I SDWA systems only.
Pyridine
110-86-1
0.014
and meet Section
728.148 standards
16
and meet Section
728.148 standards
D039
Wastes that are TC for Tetrachloroethylene based on the TCLP in SW-846 Method 1311 and that are managed in
non-CWA or non-CWA equivalent or non-Class I SDWA systems only.
Tetrachloroethylene
127-18-4
0.056
and meet Section
728.148 standards
6.0
and meet Section
728.148 standards
D040
Wastes that are TC for Trichloroethylene based on the TCLP in SW-846 Method 1311 and that are managed in
non-CWA or non-CWA equivalent or non-Class I SDWA systems only.
254
Trichloroethylene
79-01-6
0.054
and meet Section
728.148 standards
6.0
and meet Section
728.148 standards
D041
Wastes that are TC for 2,4,5-Trichlorophenol based on the TCLP in SW-846 Method 1311 and that are managed
in non-CWA or non-CWA equivalent or non-Class I SDWA systems only.
2,4,5-Trichlorophenol
95-95-4
0.18
and meet Section
728.148 standards
7.4
and meet Section
728.148 standards
D042
Wastes that are TC for 2,4,6-Trichlorophenol based on the TCLP in SW-846 Method 1311 and that are managed
in non-CWA or non-CWA equivalent or non-Class I SDWA systems only.
2,4,6-Trichlorophenol
88-06-2
0.035
and meet Section
728.148 standards
7.4
and meet Section
728.148 standards
D043
Wastes that are TC for Vinyl chloride based on the TCLP in SW-846 Method 1311 and that are managed in non-
CWA or non-CWA equivalent or non-Class I SDWA systems only.
Vinyl chloride
75-01-4
0.27
and meet Section
728.148 standards
6.0
and meet Section
728.148 standards
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 fluoro-
carbons, chlorobenzene, o-cresol, m-cresol, p-cresol, cyclohexanone, o-dichlorobenzene, 2-ethoxyethanol, ethyl
acetate, ethyl benzene, ethyl ether, isobutyl alcohol, methanol, methylene chloride, methyl ethyl ketone, methyl
isobutyl ketone, nitrobenzene, 2-nitropropane, pyridine, tetrachloroethylene, toluene, 1,1,1-trichloroethane,
1,1,2-trichloroethane, 1,1,2-trichloro- 1,2,2-trifluoroethane, trichloroethylene, trichloromonofluoromethane, or
xylenes (except as specifically noted in other subcategories). See further details of these listings in 35 Ill. Adm.
Code 721.131
255
Acetone
67-64-1
0.28
160
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 con-
centrations)
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 con-
centrations)
1330-20-7
0.32
30
F001, F002, F003, F004 & F005
F003 and F005 solvent wastes that contain any combination of one or more of the following three solvents as the
only listed F001 through F005 solvents: carbon disulfide, cyclohexanone, or methanol. (Formerly Section
728.141(c))
Carbon disulfide
75-15-0
3.8
4.8 mg/l TCLP
Cyclohexanone
108-94-1
0.36
0.75 mg/l TCLP
Methanol
67-56-1
5.6
0.75 mg/l TCLP
F001, F002, F003, F004 & F005
F005 solvent waste containing 2-Nitropropane as the only listed F001 through F005 solvent.
256
2-Nitropropane
79-46-9
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
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 INCIN
INCIN
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
0.19 mg/l TCLP
Chromium (Total)
7440-47-3
2.77
0.86 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
0.37 mg/l TCLP
Nickel
7440-02-0
3.98
5.0 mg/l TCLP
Silver
7440-22-4
NA
0.30 mg/l TCLP
F007
Spent cyanide plating bath solutions from electroplating operations.
Cadmium
7440-43-9
NA
0.19 mg/l TCLP
Chromium (Total)
7440-47-3
2.77
0.86 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
0.37 mg/l TCLP
Nickel
7440-02-0
3.98
5.0 mg/l TCLP
Silver
7440-22-4
NA
0.30 mg/l TCLP
F008
Plating bath residues from the bottom of plating baths from electroplating operations where cyanides are used in
the process.
Cadmium
7440-43-9
NA
0.19 mg/l TCLP
Chromium (Total)
7440-47-3
2.77
0.86 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
0.37 mg/l TCLP
Nickel
7440-02-0
3.98
5.0 mg/l TCLP
Silver
7440-22-4
NA
0.30 mg/l TCLP
F009
Spent stripping and cleaning bath solutions from electroplating operations where cyanides are used in the
process.
257
Cadmium
7440-43-9
NA
0.19 mg/l TCLP
Chromium (Total)
7440-47-3
2.77
0.86 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
0.37 mg/l TCLP
Nickel
7440-02-0
3.98
5.0 mg/l TCLP
Silver
7440-22-4
NA
0.30 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
0.88
NA
F011
Spent cyanide solutions from salt bath pot cleaning from metal heat treating operations.
Cadmium
7440-43-9
NA
0.19 mg/l TCLP
Chromium (Total)
7440-47-3
2.77
0.86 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
0.37 mg/l TCLP
Nickel
7440-02-0
3.98
5.0 mg/l TCLP
Silver
7440-22-4
NA
0.30 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
0.19 mg/l TCLP
Chromium (Total)
7440-47-3
2.77
0.86 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
0.37 mg/l TCLP
Nickel
7440-02-0
3.98
5.0 mg/l TCLP
Silver
7440-22-4
NA
0.30 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
0.86 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,
258
or of intermediates used to produce its derivatives (i.e., F021); (3) tetra-, penta-, or hexachlorobenzenes under
alkaline conditions (i.e., F022).
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);
(2) tetra-, penta-, or hexachlorobenzenes under alkaline conditions (i.e., F026).
HxCDDs (All Hexachlorodibenzo-
p-dioxins)
NA
0.000063
0.001
HxCDFs (All Hexachlorodibenzo-
furans)
NA
0.000063
0.001
PeCDDs (All Pentachlorodibenzo-
p-dioxins)
NA
0.000063
0.001
PeCDFs (All Pentachlorodibenzo-
furans)
NA
0.000035
0.001
TCDDs (All Tetrachlorodibenzo-
p-dioxins)
NA
0.000063
0.001
TCDFs (All Tetrachlorodibenzo-
furans)
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
Pentachlorophenol
87-86-5
0.089
7.4
F027
Discarded unused formulations contianing tri-, tetra-, or pentachlorophenol or discarded unused formulations
containing compounds derived from these chlorophenols. (This listing does not include formulations containing
hexachlorophene synthesized from prepurified 2,4,5-trichlorophenol as the sole component.)
HxCDDs (All Hexachlorodibenzo-
p-dioxins)
NA
0.000063
0.001
HxCDFs (All Hexachlorodibenzo-
furans)
NA
0.000063
0.001
PeCDDs (All Pentachlorodibenzo-
p-dioxins)
NA
0.000063
0.001
PeCDFs (All Pentachlorodibenzo-
furans)
NA
0.000035
0.001
TCDDs (All Tetrachlorodibenzo-
p-dioxins)
NA
0.000063
0.001
TCDFs (All Tetrachlorodibenzo-
furans)
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
Pentachlorophenol
87-86-5
0.089
7.4
F028
Residues resulting from the incineration or thermal treatment of soil contaminated with U.S. EPA hazardous
waste numbers F020, F021, F023, F026, and F027.
259
HxCDDs (All Hexachlorodibenzo-
p-dioxins)
NA
0.000063
0.001
HxCDFs (All Hexachlorodibenzo-
furans)
NA
0.000063
0.001
PeCDDs (All Pentachlorodibenzo-
p-dioxins)
NA
0.000063
0.001
PeCDFs (All Pentachlorodibenzo-
furans)
NA
0.000035
0.001
TCDDs (All Tetrachlorodibenzo-
p-dioxins)
NA
0.000063
0.001
TCDFs (All Tetrachlorodibenzo-
furans)
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
Pentachlorophenol
87-86-5
0.089
7.4
F024
Process wastes, including but not limited to, distillation residues, heavy ends, tars, and reactor clean-out wastes,
from the production of certain chlorinated aliphatic hydrocarbons by free radical catalyzed processes. These
chlorinated aliphatic hydrocarbons are those having carbon chain lengths ranging from one to and including five,
with varying amounts and positions of chlorine substitution. (This listing does not include wastewaters,
wastewater treatment sludges, spent catalysts, and wastes listed in 35 Ill. Adm. Code 721.131 or 721.132.)
All F024 wastes
NA
INCIN
INCIN
2-Chloro-1,3-butadiene
126-99-8
0.057
0.28
3-Chloropropylene
107-05-1
0.036
30
1,1-Dichloroethane
75-34-3
0.059
6.0
1,2-Dichloroethane
107-06-2
0.21
6.0
1,2-Dichloropropane
78-87-5
0.85
18
cis-1,3-Dichloropropylene
10061-01-5
0.036
18
trans-1,3-Dichloropropylene
10061-02-6
0.036
18
bis(2-Ethylhexyl) phthalate
117-81-7
0.28
28
Hexachloroethane
67-72-1
0.055
30
Chromium (Total)
7440-47-3
2.77
0.86 mg/l TCLP
Nickel
7440-02-0
3.98
5.0 mg/l TCLP
F025
Condensed light ends from the production of certain chlorinated aliphatic hydrocarbons, by free radical
catalyzed processes. These chlorinated aliphatic hydrocarbons are those having carbon chain lengths ranging
from one to and including five, with varying amounts and positions of chlorine substitution.
F025 - Light Ends Subcategory
Carbon tetrachloride
56-23-6
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
260
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 or Aids and Desiccants Subcategory
Carbon tetrachloride
56-23-5
0.067
6.0
Chloroform
67-66-3
0.046
6.0
Hexachlorobenzene
118-74-1
0.055
10
Hexachlorobutadiene
87-68-3
0.055
5.6
Hexachloroethane
67-72-1
0.055
30
Methylene chloride
75-9-2
0.089
30
1,1,2-Trichloroethane
79-00-5
0.054
6.0
Trichloroethylene
79-01-6
0.054
6.0
Vinyl chloride
75-01-4
0.27
6.0
F037
Petroleum refinery primary oil/water/solids separation sludge-Any sludge generated from the gravitational
separation of oil/water/solids during the storage or treatment of process wastewaters and oily cooling
wastewaters from petroleum refineries. Such sludges include, but are not limited to, those generated in:
oil/water/solids separators; tanks and impoundments; ditches and other conveyances; sumps; and stormwater
units receiving dry weather flow. Sludge generated in stormwater units that do not receive dry weather flow,
sludges generated from non-contact once-through cooling waters segregated for treatment from other process or
oily cooling waters, sludges generated in agressive 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
agressive 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 con-
centrations)
1330-20-7
0.032
30
Chromium (Total)
7440-47-3
2.77
0.86 mg/l TCLP
Cyanides (Total)
7
57-12-5
1.2
590
Lead
7439-92-1
0.69
NA
Nickel
7440-02-0
NA
5.0 mg/l TCLP
261
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 agressive
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 agressive biological units) and F037,
K048, and K051 are not included in this listing.
Benzene
71-43-2
0.14
10
Benzo(a)pyrene
50-32-8
0.061
3.4
bis(2-Ethylhexyl) phthalate
117-81-7
0.28
28
Chrysene
218-01-9
0.059
3.4
Di-n-butyl phthalate
84-74-2
0.057
28
Ethylbenzene
100-41-4
0.057
10
Fluorene
86-73-7
0.059
NA
Naphthalene
91-20-3
0.059
5.6
Phenanthrene
85-01-8
0.059
5.6
Phenol
108-95-2
0.039
6.2
Pyrene
129-00-0
0.067
8.2
Toluene
108-88-3
0.080
10
Xylenes-mixed isomers
(sum of o-, m-, and p-xylene con-
centrations)
1330-20-7
0.32
30
Chromium (Total)
7440-47-3
2.77
0.86 mg/l TCLP
Cyanides (Total)
7
57-12-5
1.2
590
Lead
7439-92-1
0.69
NA
Nickel
7440-02-0
NA
5.0 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 728.Subpart D. (Leachate resulting from the disposal of one
or more of the following U.S. EPA hazardous wastes and no other hazardous wastes retains its U.S. EPA
hazardous waste numbers: F020, F021, F022, F026, F027, or F028.).
262
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
alpha-BHC
319-84-6
0.00014
0.066
beta-BHC
319-85-7
0.00014
0.066
delta-BHC
319-86-8
0.023
0.066
gamma-BHC
58-89-9
0.0017
0.066
Benzene
71-43-2
0.14
10
Benz(a)anthracene
56-55-3
0.059
3.4
Benzo(b)fluoranthene (difficult to
distinguish from benzo(k)fluor-
anthene)
205-99-2
0.11
6.8
Benzo(k)fluoranthene (difficult to
distinguish from benzo(b)fluor-
anthene)
207-08-9
0.11
6.8
Benzo(g,h,i)perylene
191-24-2
0.0055
1.8
Benzo(a)pyrene
50-32-8
0.061
3.4
Bromodichloromethane
75-27-4
0.35
15
Methyl bromide (Bromomethane)
74-83-9
0.11
15
4-Bromophenyl phenyl ether
101-55-3
0.055
15
n-Butyl alcohol
71-36-3
5.6
2.6
Butyl benzyl phthalate
85-68-7
0.017
28
2-sec-Butyl-4,6-dinitrophenol
(Dinoseb)
88-85-7
0.066
2.5
Carbon disulfide
75-15-0
3.8
NA
Carbon tetrachloride
56-23-5
0.057
6.0
Chlordane (alpha and gamma
isomers)
57-74-9
0.0033
0.26
p-Chloroaniline
106-47-8
0.46
16
Chlorobenzene
108-90-7
0.057
6.0
Chlorobenzilate
510-15-6
0.10
NA
2-Chloro-1,3-butadiene
126-99-8
0.057
NA
Chlorodibromomethane
124-48-1
0.057
15
Chloroethane
75-00-3
0.27
6.0
bis(2-Chloroethoxy)methane
111-91-1
0.036
7.2
bis(2-Chloroethyl)ether
111-44-4
0.033
6.0
Chloroform
67-66-3
0.046
6.0
bis(2-Chloroisopropyl)ether
39638-32-9
108-60-1
0.055
7.2
p-Chloro-m-cresol
59-50-7
0.018
14
Chloromethane (Methyl chloride)
74-87-3
0.19
30
263
2-Chloronaphthalene
91-58-7
0.055
5.6
2-Chlorophenol
95-57-8
0.044
5.7
3-Chloropropylene
107-05-1
0.036
30
Chrysene
218-01-9
0.059
3.4
o-Cresol
95-48-7
0.11
5.6
m-Cresol
(difficult to distinguish from p-
cresol)
108-39-4
0.77
5.6
p-Cresol
(difficult to distinguish from m-
cresol)
106-44-5
0.77
5.6
Cyclohexanone
108-94-1
0.36
NA
1,2-Dibromo-3-chloropropane
96-12-8
0.11
15
Ethylene dibromide (1,2-
Dibromoethane)
106-93-4
0.028
15
Dibromomethane
74-95-3
0.11
15
2,4-D (2,4-Dichlorophenoxyacetic
acid)
94-75-7
0.72
10
o,p'-DDD
53-19-0
0.023
0.087
p,p'-DDD
72-54-8
0.023
0.087
o,p'-DDE
3424-82-6
0.031
0.087
p,p'-DDE
72-55-9
0.031
0.087
o,p'-DDT
789-02-6
0.0039
0.087
p,p'-DDT
50-29-3
0.0039
0.087
Dibenz(a,h)anthracene
53-70-3
0.055
8.2
Dibenz(a,e)pyrene
192-65-4
0.061
NA
m-Dichlorobenzene
541-73-1
0.036
6.0
o-Dichlorobenzene
95-50-1
0.088
6.0
p-Dichlorobenzene
106-46-7
0.090
6.0
Dichlorodifluoromethane
75-71-8
0.23
7.2
1,1-Dichloroethane
75-34-3
0.059
6.0
1,2-Dichloroethane
107-06-2
0.21
6.0
1,1-Dichloroethylene
75-35-4
0.025
6.0
trans-1,2-Dichloroethylene
156-60-5
0.054
30
2,4-Dichlorophenol
120-83-2
0.044
14
2,6-Dichlorophenol
87-65-0
0.044
14
1,2-Dichloropropane
78-87-5
0.85
18
cis-1,3-Dichloropropylene
10061-01-5
0.036
18
trans-1,3-Dichloropropylene
10061-02-6
0.036
18
Dieldrin
60-57-1
0.017
0.13
Diethyl phthalate
84-66-2
0.20
28
2-4-Dimethyl phenol
105-67-9
0.036
14
Dimethyl phthalate
131-11-3
0.047
28
Di-n-butyl phthalate
84-74-2
0.057
28
1,4-Dinitrobenzene
100-25-4
0.32
2.3
4,6-Dinitro-o-cresol
534-52-1
0.28
160
2,4-Dinitrophenol
51-28-5
0.12
160
2,4-Dinitrotoluene
121-14-2
0.32
140
2,6-Dinitrotoluene
606-20-2
0.55
28
Di-n-octyl phthalate
117-84-0
0.017
28
Di-n-propylnitrosamine
621-64-7
0.40
14
264
1,4-Dioxane
123-91-1
NA
170
Diphenylamine (difficult to
distinguish from diphenylnitros-
amine)
122-39-4
0.92
13
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
1-31-07-8
0.029
0.13
Endrin
72-20-8
0.0028
0.13
Endrin aldehyde
7421-93-4
0.025
0.13
Ethyl acetate
141-78-6
0.34
33
Ethyl cyanide (Propanenitrile)
107-12-0
0.24
360
Ethyl benzene
100-41-4
0.057
10
Ethyl ether
60-29-7
0.12
160
bis(2-Ethylhexyl) phthalate
117-81-7
0.28
28
Ethyl methacrylate
97-63-2
0.14
160
Ethylene oxide
75-21-8
0.12
NA
Famphur
52-85-7
0.017
15
Fluoranthene
206-44-0
0.068
3.4
Fluorene
86-73-7
0.059
3.4
Heptachlor
76-44-8
0.0012
0.066
Heptachlor epoxide
1024-57-3
0.016
0.066
Hexachlorobenzene
118-74-1
0.055
10
Hexachlorobutadiene
87-68-3
0.055
5.6
Hexachlorocyclopentadiene
77-47-4
0.057
2.4
HxCDDs (All Hexachlorodibenzo-
p-dioxins)
NA
0.000063
0.001
HxCDFs (All Hexachlorodibenzo-
furans)
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
265
Methyl methansulfonate
66-27-3
0.018
NA
Methyl parathion
298-00-0
0.014
4.6
Naphthalene
91-20-3
0.059
5.6
2-Naphthylamine
91-59-8
0.52
NA
p-Nitroaniline
100-01-6
0.028
28
Nitrobenzene
98-95-3
0.068
14
5-Nitro-o-toluidine
99-55-8
0.32
28
p-Nitrophenol
100-02-7
0.12
29
N-Nitrosodiethylamine
55-18-5
0.40
28
N-Nitrosodimethylamine
62-75-9
0.40
NA
N-Nitroso-di-n-butylamine
924-16-3
0.40
17
N-Nitrosomethylethylamine
10595-95-6
0.40
2.3
N-Nitrosomorpholine
59-89-2
0.40
2.3
N-Nitrosopiperidine
100-75-4
0.013
35
N-Nitrosopyrrolidine
930-55-2
0.013
35
Parathion
56-38-2
0.014
4.6
Total PCBs
(sum of all PCB isomers, or all
Aroclors)
1336-36-3
0.10
10
Pentachlorobenzene
608-93-5
0.055
10
PeCDDs (All Pentachlorodibenzo-
p-dioxins)
NA
0.000063
0.001
PcCDFs (All Pentachlorodibenzo-
furans)
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 Tetrachlorodibenzo-
p-dioxins)
NA
0.000063
0.001
TCDFs (All Tetrachlorodibenzo-
furans)
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
266
1,1,2-Trichloroethane
79-00-5
0.054
6.0
Trichloroethylene
79-01-6
0.054
6.0
Trichloromonofluoromethane
75-69-4
0.020
30
2,4,5-Trichlorophenol
95-95-4
0.18
7.4
2,4,6-Trichlorophenol
88-06-2
0.035
7.4
1,2,3-Trichloropropane
96-18-4
0.85
30
1,1,2-Trichloro-1,2,2-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 or o-, m-, and p-xylene con-
centrations)
1330-20-7
0.32
30
Antimony
7440-36-0
1.9
2.1 mg/l TCLP
Arsenic
7440-38-2
1.4
5.0 mg/l TCLP
Barium
7440-39-3
1.2
7.6 mg/l TCLP
Beryllium
7440-41-7
0.82
NA
Cadmium
7440-43-9
0.69
0.19 mg/l TCLP
Chromium (Total)
7440-47-3
2.77
0.86 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
0.37 mg/l TCLP
Mercury
7439-97-6
0.15
0.025 mg/l TCLP
Nickel
7440-02-0
3.98
5.0 mg/l TCLP
Selenium
7782-49-2
0.82
0.16 mg/l TCLP
Silver
7440-22-4
0.43
0.30 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 con-
centrations)
1330-20-7
0.32
30
Lead
7439-92-1
0.690.37 mg/l
TCLP
K002
Wastewater treatment sludge from the production of chrome yellow and orange pigments.
Chromium (Total)
7440-47-3
2.77
0.86 mg/l TCLP
Lead
7439-92-1
0.69
0.37 mg/l TCLP
267
K003
Wastewater treatment sludge from the production of molybdate orange pigments.
Chromium (Total)
7440-47-3
2.77
0.86 mg/l TCLP
Lead
7439-92-1
0.69
0.37 mg/l TCLP
K004
Wastewater treatment sludge from the production of zinc yellow pigments.
Chromium (Total)
7440-47-3
2.77
0.86 mg/l TCLP
Lead
7439-92-1
0.69
0.37 mg/l TCLP
K005
Wastewater treatment sludge from the production of chrome green pigments.
Chromium (Total)
7440-47-3
2.77
0.86 mg/l TCLP
Lead
7439-92-1
0.69
0.37 mg/l TCLP
Cyanides (Total)
7
57-12-5
1.25
90
K006
Wastewater treatment sludge from the production of chrome oxide green pigments (anhydrous).
Chromium (Total)
7440-47-3
2.77
0.86 mg/l TCLP
Lead
7439-92-1
0.69
0.37 mg/l TCLP
K006
Wastewater treatment sludge from the production of chrome oxide green pigments (hydrated).
Chromium (Total)
7440-47-3
2.77
0.86 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
0.86 mg/l TCLP
Lead
7439-92-1
0.69
0.37 mg/l TCLP
Cyanides (Total)
7
57-12-5
1.25
90
K008
Oven residue from the production of chrome oxide green pigments.
Chromium (Total)
7440-47-3
2.77
0.86 mg/l TCLP
Lead
7439-92-1
0.69
0.37 mg/l TCLP
K009
Distillation bottoms from the production of acetaldehyde from ethylene.
Chloroform
67-66-3
0.046
6.0
K010
Distillation side cuts from the production of acetaldehyde from ethylene.
Chloroform
67-66-3
0.046
6.0
K011
Bottom stream from the wastewater stripper in the production of acrylonitrile.
268
Acetonitrile
75-05-8
5.6
1.8
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
1.8
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
1.8
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)fluor-
anthene)
205-99-2
0.11
6.8
Benzo(k)fluoranthene (difficult to
distinguish from benzo(b)fluor-
anthene)
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
0.86 mg/l TCLP
Nickel
7440-02-0
3.9
85.0 mg/l TCLP
K016
Heavy ends or distillation residues from the production of carbon tetrachloride.
Hexachlorobenzene
118-74-1
0.055
10
Hexachlorobutadiene
87-68-3
0.055
5.6
Hexachlorocyclopentadiene
77-47-4
0.057
2.4
Hexachloroethane
67-72-1
0.055
30
Tetrachloroethylene
127-18-4
0.056
6.0
K017
Heavy ends (still bottoms) from the purification column in the production of epichlorohydrin.
bis(2-Chloroethyl)ether
111-44-4
0.033
6.0
1,2-Dichloropropane
78-87-5
0.85
18
1,2,3-Trichloropropane
96-18-4
0.85
30
269
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
111-44-14
0.033
6.0
Chlorobenzene
108-90-7
0.057
6.0
Chloroform
67-66-3
0.046
6.0
p-Dichlorobenzene
106-46-7
0.090
NA
1,2-Dichloroethane
107-06-2
0.21
6.0
Fluorene
86-73-7
0.059
NA
Hexachloroethane
67-72-1
0.055
30
Naphthalene
91-20-3
0.059
5.6
Phenanthrene
85-01-8
0.059
5.6
1,2,4,5-Tetrachlorobenzene
95-94-3
0.055
NA
Tetrachloroethylene
127-18-4
0.056
6.0
1,2,4-Trichlorobenzene
120-82-1
0.055
19
1,1,1-Trichloroethane
71-55-6
0.054
6.0
K020
Heavy ends from the distillation of vinyl chloride in vinyl chloride monomer production.
1,2-Dichloroethane
107-06-2
0.21
6.0
1,1,2,2-Tetrachloroethane
79-34-6
0.057
6.0
Tetrachloroethylene
127-18-4
0.056
6.0
K021
Aqueous spent antimony catalyst waste from fluoromethanes production.
Carbon tetrachloride
56-23-5
0.057
6.0
Chloroform
67-66-3
0.046
6.0
Antimony
7440-36-0
1.9
2.1 mg/l TCLP
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
2.1 mg/l TCLP
K022
Distillation bottom tars from the production of phenol or acetone from cumene.
270
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
0.86 mg/l TCLP
Nickel
7440-02-0
3.98
5.0 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
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
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
INCIN
INCIN
K026
Stripping still tails from the production of methyl ethyl pyridines.
NA
NA
INCIN
INCIN
K027
Centrifuge and distillation residues from the toluene diisocyanate production.
NA
NA
CARBN; or INCIN
CMBST
K028
Spent catalyst from the hydrochlorinator reactor in the production of 1,1,1-trichloroethane.
271
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
0.86 mg/l TCLP
Lead
7439-92-1
0.69
0.37 mg/l TCLP
Nickel
7440-02-0
3.98
5.0 mg/l TCLP
K029
Waste from the product steam stripper in the production of 1,1,1-trichloroethane.
Chloroform
67-66-3
0.046
6.0
1,2-Dichloroethane
107-06-2
0.21
6.0
1,1-Dichloroethylene
75-35-4
0.025
6.0
1,1,1-Trichloroethane
71-55-6
0.054
6.0
Vinyl chloride
75-01-4
0.27
6.0
K030
Column bodies or heavy ends from the combined production of trichloroethylene and perchloroethylene.
o-Dichlorobenzene
95-50-1
0.088
NA
p-Dichlorobenzene
106-46-7
0.090
NA
Hexachlorobutadiene
87-68-3
0.055
5.6
Hexachloroethane
67-72-1
0.055
30
Hexachloropropylene
1888-71-7
NA
30
Pentachlorobenzene
608-93-5
NA
10
Pentachloroethane
76-01-7
NA
6.0
1,2,4,5-Tetrachlorobenzene
95-94-3
0.055
14
Tetrachloroethylene
127-18-4
0.056
6.0
1,2,4-Trichlorobenzene
120-82-1
0.055
19
K031
By-product salts generated in the production of MSMA and cacodylic acid.
Arsenic
7440-38-2
1.4
5.0 mg/l TCLP
K032
Wastewater treatment sludge from the production of chlordane.
Hexachlorocyclopentadiene
77-47-4
0.057
2.4
Chlordane (alpha and gamma
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.
272
Hexachlorocyclopentadiene
77-47-4
0.057
2.4
K034
Filter solids from the filtration of hexachlorocyclopentadiene in the production of chlordane.
Hexachlorocyclopentadiene
77-47-4
0.057
2.4
K035
Wastewater treatment sludges generated in the production of creosote.
Acenaphthene
83-32-9
NA
3.4
Anthracene
120-12-7
NA
3.4
Benz(a)anthracene
56-55-3
0.059
3.4
Benzo(a)pyrene
50-32-8
0.061
3.4
Chrysene
218-01-9
0.059
3.4
o-Cresol
95-48-7
0.11
5.6
m-Cresol
(difficult to distinguish from p-
cresol)
108-39-4
0.77
5.6
p-Cresol
(difficult to distinguish from m-
cresol)
106-44-5
0.77
5.6
Dibenz(a,h)anthracene
53-70-3
NA
8.2
Fluoranthene
206-44-0
0.068
3.4
Fluorene
86-73-7
NA
3.4
Indeno(1,2,3-cd)pyrene
193-39-5
NA
3.4
Naphthalene
91-20-3
0.059
5.6
Phenanthrene
85-01-8
0.059
5.6
Phenol
108-95-2
0.039
6.2
Pyrene
129-00-0
0.067
8.2
K036
Still bottoms from toluene reclamation distillaiton in the production of disulfoton.
Disulfoton
298-04-4
0.017
6.2
K037
Wastewater treatment sludges from the production of disulfoton.
Disulfoton
298-04-4
0.017
6.2
Toluene
108-88-3
0.080
10
K038
Wastewater from the washing and stripping of phorate production.
Phorate
298-02-2
0.021
4.6
K039
Filter cake from the filtration of diethylphosphorodithioic acid in the production of phorate.
NA
NA
CARBN; or INCIN
CMBST
K040
Wastewater treatment sludge from the production of phorate.
Phorate
298-02-2
0.021
4.6
273
K041
Wastewater treatment sludge from the production of toxaphene.
Toxaphene
8001-35-2
0.0095
2.6
K042
Heavy ends or distillation residues from the distillation of tetrachlorobenzene in the production of 2,4,5-T.
o-Dichlorobenzene
95-50-1
0.088
6.0
p-Dichlorobenzene
106-46-7
0.090
6.0
Pentachlorobenzene
608-93-5
0.055
10
1,2,4,5-Tetrachlorobenzene
95-94-3
0.055
14
1,2,4-Trichlorobenzene
120-82-1
0.055
19
K043
2,6-Dichlorophenol waste from the production of 2,4-D.
2,4-Dichlorophenol
120-83-2
0.044
14
2,6-Dichlorophenol
187-65-0
0.044
14
2,4,5-Trichlorophenol
95-95-4
0.18
7.4
2,4,6-Trichlorophenol
88-06-2
0.035
7.4
2,3,4,6-Tetrachlorophenol
58-90-2
0.030
7.4
Pentachlorophenol
87-86-5
0.089
7.4
Tetrachloroethylene
127-18-4
0.056
6.0
HxCDDs (All Hexachlorodibenzo-
p-dioxins)
NA
0.000063
0.001
HxCDFs (All Hexachlorodibenzo-
furans)
NA
0.000063
0.001
PeCDDs (All Pentachlorodibenzo-
p-dioxins)
NA
0.000063
0.001
PeCDFs (All Pentachlorodibenzo-
furans)
NA
0.000035
0.001
TCDDs (All Tetrachlorodibenzo-
p-dioxins)
NA
0.000063
0.001
TCDFs (All Tetrachlorodibenzo-
furans)
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
0.37 mg/l TCLP
K047
Pink or red water from TNT operations.
NA
NA
DEACT
DEACT
274
K048
Dissolved air flotation (DAF) float from the petroleum refining industry.
Benzene
71-43-2
0.14
10
Benzo(a)pyrene
50-32-8
0.061
3.4
bis(2-Ethylhexyl) phthalate
117-81-7
0.28
28
Chrysene
218-01-9
0.059
3.4
Di-n-butyl phthalate
84-74-2
0.057
28
Ethylbenzene
100-41-4
0.057
10
Fluorene
86-73-7
0.059
NA
Naphthalene
91-20-3
0.059
5.6
Phenanthrene
85-01-8
0.059
5.6
Phenol
108-95-2
0.039
6.2
Pyrene
129-00-0
0.067
8.2
Toluene
108-88-33
0.080
10
Xylenes-mixed isomers
(sum of o-, m-, and p-xylene con-
centrations)
1330-20-7
0.32
30
Chromium (Total)
7440-47-3
2.77
0.86 mg/l TCLP
Cyanides (Total)
7
57-12-5
1.2
590
Lead
7439-92-1
0.69
NA
Nickel
7440-02-0
NA
5.0 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 con-
centrations)
1330-20-7
0.32
30
Cyanides (Total)
7
57-12-5
1.2
590
Chromium (Total)
7440-47-3
2.77
0.86 mg/l TCLP
Lead
7439-92-1
0.69
NA
Nickel
7440-02-0
NA
5.0 mg/l TCLP
K050
Heat exchanger bundle cleaning sludge from the petroleum refining industry.
275
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
0.86 mg/l TCLP
Lead
7439-92-1
0.69
NA
Nickel
7440-02-0
NA
5.0 mg/l TCLP
K051
API separator sludge from the petroleum refining industry.
Acenaphthene
83-32-9
0.059
NA
Anthracene
120-12-7
0.059
3.4
Benz(a)anthracene
56-55-3
0.059
3.4
Benzene
71-43-2
0.14
10
Benzo(a)pyrene
50-32-8
0.061
3.4
bis(2-Ethylhexyl) phthalate
117-81-7
0.28
28
Chrysene
2218-01-9
0.059
3.4
Di-n-butyl phthalate
105-67-9
0.057
28
Ethylbenzene
100-41-4
0.057
10
Fluorene
86-73-7
0.059
NA
Naphthalene
91-20-3
0.059
5.6
Phenanthrene
85-01-8
0.059
5.6
Phenol
108-95-2
0.039
6.2
Pyrene
129-00-0
0.067
8.2
Toluene
1068-88-3
0.08
10
Xylenes-mixed isomers
(sum of o-, m-, and p-xylene con-
centrations)
1330-20-7
0.32
30
Cyanides (Total)
7
57-12-5
1.2
590
Chromium (Total)
7440-47-3
2.77
0.86 mg/l TCLP
Lead
7439-92-1
0.69
NA
Nickel
7440-02-0
NA
5.0 mg/l TCLP
K052
Tank bottoms (leaded) from the petroleum refining industry.
276
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 con-
centrations)
1330-20-7
0.32
30
Chromium (Total)
7440-47-3
2.77
0.86 mg/l TCLP
Cyanides (Total)
7
57-12-5
1.2
590
Lead
7439-92-1
0.69
NA
Nickel
7440-02-0
NA
5.0 mg/l TCLP
K060
Ammonia still lime sludge from coking operations.
Benzene
71-43-2
0.14
10
Benzo(a)pyrene
50-32-8
0.061
3.4
Naphthalene
91-20-3
0.059
5.6
Phenol
108-95-2
0.039
6.2
Cyanides (Total)
7
57-12-5
1.2
590
K061
Emission control dust or sludge from the primary production of steel in electric furnaces.
Antimony
7440-36-0
NA
2.1 mg/l TCLP
Arsenic
7440-38-2
NA
5.0 mg/l TCLP
Barium
7440-39-3
NA
7.6 mg/l TCLP
Beryllium
7440-41-7
NA
0.014 mg/l TCLP
Cadmium
7440-43-9
0.69
0.19 mg/l TCLP
Chromium (Total)
7440-47-3
2.77
0.86 mg/l TCLP
Lead
7439-92-1
0.69
0.37 mg/l TCLP
Mercury
7439-97-6
NA
0.025 mg/l TCLP
Nickel
7440-02-0
3.98
5.0 mg/l TCLP
Selenium
7782-49-2
NA
0.16 mg/l TCLP
Silver
7440-22-4
NA
0.30 mg/l TCLP
Thallium
NA
NA
0.078 mg/l TCLP
Zinc
7440-66-6
NA
5.3 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).
277
Chromium (Total)
7440-47-3
2.77
0.86 mg/l TCLP
Lead
7439-92-1
0.69
0.37 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
0.19 mg/l TCLP
Lead
7439-92-1
0.69
0.37 mg/l TCLP
K069
Emission control dust or sludge from secondary lead smelting. - Non-Calcium sulfate (High Lead) Subcategory
NA
NA
NA
RLEAD
K071
K071 (Brine purification muds from the mercury cell process in chlorine production, where separately
prepurified brine is not used) nonwastewaters that are residues from RMERC.
Mercury
7439-97-6
NA
0.20 mg/l TCLP
K071
K071 (Brine purification muds from the mercury cell process in chlorine production, where separately
prepurified brine is not used) nonwastewaters that are not residues from RMERC.
Mercury
7439-97-6
NA
0.025 mg/l TCLP
K071
All K071 wastewaters.
Mercury
7439-97-6
0.15
NA
K073
Chlorinated hydrocarbon waste from the purification step of the diaphragm cell process using graphite anodes in
chlorine production.
Carbon tetrachloride
56-23-5
0.057
6.0
Chloroform
67-66-3
0.046
6.0
Hexachloroethane
67-72-1
0.055
30
Tetrachloroethylene
127-18-4
0.058
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
5.0 mg/l TCLP
278
K084
Wastewater treatment sludges generated during the production of veterinary pharmaceuticals from arsenic or
organo-arsenic compounds.
Arsenic
7440-38-2
1.4
5.0 mg/l TCLP
K085
Distillation or fractionation column bottoms from the production of chlorobenzenes.
Benzene
71-43-2
0.14
10
Chlorobenzene
108-90-7
0.057
6.0
m-Dichlorobenzene
541-73-1
0.036
6.0
o-Dichlorobenzene
95-50-1
0.088
6.0
p-Dichlorobenzene
106-46-7
0.090
6.0
Hexachlorobenzene
118-74-1
0.055
10
Total PCBs
(sum of all PCB isomers, or all
Aroclors)
1336-36-3
0.10
10
Pentachlorobenzene
608-93-5
0.055
10
1,2,4,5-Tetrachlorobenzene
95-94-3
0.055
14
1,2,4-Trichlorobenzene
120-82-1
0.055
19
K086
Solvent wastes and sludges, caustic washes and sludges, or water washes and sludges from cleaning tubs and
equipment used in the formulation of ink from pigments, driers, soaps, and stabilizers containing chromium and
lead.
279
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 con-
centrations)
1330-20-7
0.32
30
Chromium (Total)
7440-47-3
2.77
0.86 mg/l TCLP
Cyanides (Total)
7
57-12-5
1.2
590
Lead
7439-92-1
0.69
0.37 mg/l TCLP
K087
Decanter tank tar sludge from coking operations.
Acenaphthylene
208-96-8
0.059
3.4
Benzene
71-43-2
0.14
10
Chrysene
218-01-9
0.059
3.4
Fluoranthene
206-44-0
0.068
3.4
Indenol(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 con-
centrations)
1330-20-7
0.32
30
Lead
7439-92-1
0.69
0.37 mg/l TCLP
K093
Distillation light ends from the production of phthalic anhydride from ortho-xylene.
Phthalic anhydride (measured as
Phthalic acid or erephthalic acid)
100-21-0
0.055
28
Phthalic anhydride
85-44-9
0.055
28
280
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
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 (alpha and gamma
isomers)
57-74-9
0.0033
0.26
Heptachlor
76-44-8
0.0012
0.066
Heptachlor epoxide
1024-57-3
0.016
0.068
Hexachlorocyclopentadiene
77-47-4
0.057
2.4
K098
Untreated process wastewater from the production of toxaphene.
Toxaphene
8001-35-2
0.0095
2.6
K099
Untreated wastewater from the production of 2,4-D.
281
2,4-Dichlorophenoxyacetic acid
94-75-7
0.72
10
HxCDDs (All Hexachlorodibenzo-
p-dioxins)
NA
0.000063
0.001
HxCDFs (All Hexachlorodibenzo-
furans)
NA
0.000063
0.001
PeCDDs (All Pentachlorodibenzo-
p-dioxins)
NA
0.000063
0.001
PeCDFs (All Pentachlorodibenzo-
furans)
NA
0.000035
0.001
TCDDs (All Tetrachlorodibenzo-
p-dioxins)
NA
0.000063
0.001
TCDFs (All Tetrachlorodibenzo-
furans)
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
0.19 mg/l TCLP
Chromium (Total)
7440-47-3
2.77
0.86 mg/l TCLP
Lead
7439-92-1
0.69
0.37 mg/l TCLP
K101
Distillation tar residues from the distillation of aniline-based compounds in the production of veterinary
pharmaceuticals from arsenic or organo-arsenic compounds.
o-Nitroaniline
88-74-4
0.27
14
Arsenic
7440-38-2
1.4
5.0 mg/l TCLP
Cadmium
7440-43-9
0.69
NA
Lead
7439-92-1
0.69
NA
Mercury
7439-97-6
0.15
NA
K102
Residue from the use of activated carbon for decolorization in the production of veterinary pharmaceuticals from
arsenic or organo-arsenic compounds.
o-Nitrophenol
88-75-5
0.028
13
Arsenic
7440-38-2
1.4
5.0 mg/l TCLP
Cadmium
7440-43-9
0.69
NA
Lead
7439-92-1
0.69
NA
Mercury
7439-97-6
0.15
NA
K103
Process residues from aniline extraction from the production of aniline.
Aniline
62-53-3
0.81
14
Benzene
71-43-2
0.14
10
2,4-Dinitrophenol
51-28-5
0.12
160
Nitrobenzene
98-95-3
0.068
14
Phenol
108-95-2
0.039
6.2
K104
Combined wastewater streams generated from nitrobenzene or aniline production.
282
Aniline
62-53-3
0.81
14
Benzene
71-43-2
0.14
10
2,4-Dinitrophenol
51-28-5
0.12
160
Nitrobenzene
98-95-3
0.068
14
Phenol
108-95-2
0.039
6.2
Cyanides (Total)
7
57-12-5
1.2
590
K105
Separated aqueous stream from the reactor product washing step in the production of chlorobenzenes.
Benzene
71-43-2
0.14
10
Chlorobenzene
108-90-7
0.057
6.0
2-Chlorophenol
95-57-8
0.044
5.7
o-Dichlorobenzene
95-50-1
0.088
6.0
p-Dichlorobenzene
106-46-7
0.090
6.0
Phenol
108-95-2
0.039
6.2
2,4,5-Trichlorophenol
95-95-4
0.18
7.4
2,4,6-Trichlorophenol
88-06-2
0.035
7.4
K106
K106 (wastewater treatment sludge from the mercury cell process in chlorine production) nonwastewaters that
contain greater than or equal to 260 mg/kg total mercury.
Mercury
7439-97-6
NA
RMERC
K106
K106 (wastewater treatment sludge from the mercury cell process in chlorine production) nonwastewaters that
contain less than 260 mg/kg total mercury that are residues from RMERC.
Mercury
7439-97-6
NA
0.20 mg/l TCLP
K106
Other K106 nonwastewaters that contain less than 260 mg/kg total mercury and are not residues from RMERC.
Mercury
7439-97-6
NA
0.025 mg/l TCLP
K106
All K106 wastewaters.
Mercury
7439-97-6
0.15
NA
K107
Column bottoms from product separation from the production of 1,1-dimethylhydrazine (UDMH) from
carboxylic acid hydrazides.
NA
NA
INCIN; or CHOXD
fb CARBN; or
BIODG fb CARBN
INCIN
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
INCIN; or CHOXD
fb CARBN; or
BIODG fb CARBN
INCIN
283
K109
Spent filter cartridges from product purification from the production of 1,1-dimethylhydrazine (UDMH) from
carboxylic acid hydrazides.
NA
NA
INCIN; or CHOXD
fb CARBN; or
BIODG fb CARBN
INCIN
K110
Condensed column overheads from intermediate separation from the production of 1,1-dimethylhydrazine
(UDMH) from carboxylic acid hydrazides.
NA
NA
INCIN; or CHOXD
fb CARBN; or
BIODG fb CARBN
INCIN
K111
Product washwaters from the production of dinitrotoluene via nitration of toluene
2,4-Dinitrotoluene
121-1-1
0.32
140
2,6-Dinitrotoluene
606-20-2
0.55
28
K112
Reaction by-product water from the drying column in the production of toluenediamine via hydrogenation of
dinitrotoluene.
NA
NA
INCIN; or CHOXD
fb CARBN; or
BIODG fb CARBN
INCIN
K113
Condensed liquid light ends from the purification of toluenediamine in the production of toluenediamine via
hydrogenation of dinitrotoluene.
NA
NA
CARBN; or INCIN
CMBST
K114
Vicinals from the purification of toluenediamine in the production of toluenediamine via hydrogenation of
dinitrotoluene.
NA
NA
CARBN; or INCIN
CMBST
K115
Heavy ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of
dinitrotoluene.
Nickel
7440-02-0
3.98
5.0 mg/l TCLP
NA
NA
CARBN; or INCIN
CMBST
K116
Organic condensate from the solvent recovery column in the production of toluene diisocyanate via phosgenation
of toluenediamine.
NA
NA
CARBN; or INCIN
CMBST
K117
Wastewater from the reactor vent gas scrubber in the production of ethylene dibromide via bromination of
ethene.
284
Methyl bromide (Bromomethane)
74-83-9
0.11
15
Chloroform
67-66-3
0.046
6.0
Ethylene dibromide (1,2-
Dibromoethane)
106-93-4
0.028
15
K118
Spent absorbent solids from purification of ethylene dibromide in the production of ethylene dibromide via
bromination of ethene.
Methyl bromide (Bromomethane)
74-83-9
0.11
15
Chloroform
67-66-3
0.046
6.0
Ethylene dibromide (1,2-
Dibromoethane)
106-93-4
0.028
15
K123
Process wastewater (including supernates, filtrates, and washwaters) from the production of ethylenebisdithio-
carbamic acid and its salts.
NA
NA
INCIN; or CHOXD
fb (BIODG or
CARBN)
INCIN
K124
Reactor vent scrubber water from the production of ethylenebisdithiocarbamic acid and its salts.
NA
NA
INCIN; or CHOXD
fb (BIODG or
CARBN)
INCIN
K125
Filtration, evaporation, and centrifugation solids from the production of ethylenebisdithiocarbamic acid and its
salts.
NA
NA
INCIN; or CHOXD
fb (BIODG or
CARBN)
INCIN
K126
Baghouse dust and floor sweepings in milling and packaging operations from the production or formulation of
ethylenebisdithiocarbamic acid and its salts.
NA
NA
INCIN; or CHOXD
fb (BIODG or
CARBN)
INCIN
K131
Wastewater from the reactor and spent sulfuric acid from the acid dryer from the production of methyl bromide.
Methyl bromide (Bromomethane)
74-83-9
0.11
15
K132
Spent absorbent and wastewater separator solids from the production of methyl bromide.
Methyl bromide (Bromomethane)
74-83-9
0.11
15
K136
Still bottoms from the purification of ethylene dibromide in the production of ethylene dibromide via
bromination of ethene.
285
Methyl bromide (Bromomethane)
74-83-9
0.11
15
Chloroform
67-66-3
0.046
6.0
Ethylene dibromide (1,2-
Dibromoethane)
106-93-4
0.028
15
K141
Process residues from the recovery of coal tar, including, but not limited to, collecting sump residues from the
production of coke or the recovery of coke by-products produced from coal. This listing does not include K087
(decanter tank tar sludge from coking operations).
Benzene
71-43-2
0.14
10
Benz(a)anthracene
56-55-3
0.059
3.4
Benzo(a)pyrene
50-2-8
0.061
3.4
Benzo(b)fluoranthene (difficult to
distinguish from benzo(k)fluor-
anthene)
205-99-2
0.11
6.8
Benzo(k)fluoranthene (difficult to
distinguish from benzo(b)fluor-
anthene)
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)fluor-
anthene)
205-99-2
0.11
6.8
Benzo(k)fluoranthene (difficult to
distinguish from benzo(b)fluor-
anthene)
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
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.
286
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)fluor-
anthene)
205-99-2
0.11
6.8
Benzo(k)fluoranthene (difficult to
distinguish from benzo(b)fluor-
anthene)
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)fluor-
anthene)
205-99-2
0.11
6.8
Benzo(k)fluoranthene (difficult to
distinguish from benzo(b)fluor-
anthene)
207-08-9
0.11
6.8
Chrysene
218-01-9
0.059
3.4
Dibenz(a,h)anthracene
53-70-3
0.055
8.2
K145
Residues from naphthalene collection and recovery operations from the recovery of coke by-products produced
from coal.
Benzene
71-43-2
0.14
10
Benz(a)anthracene
56-55-3
0.059
3.4
Benzo(a)pyrene
50-32-8
0.061
3.4
Chrysene
218-01-9
0.059
3.4
Dibenz(a,h)anthracene
53-70-3
0.055
6.2
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)fluor-
anthene)
205-99-2
0.11
6.8
Benzo(k)fluoranthene (difficult to
distinguish from benzo(b)fluor-
anthene)
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
287
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)fluor-
anthene)
205-99-2
0.11
6.8
Benzo(k)fluoranthene (difficult to
distinguish from benzo(b)fluor-
anthene)
207-08-9
0.11
6.8
Chrysene
218-01-9
0.059
3.4
Dibenz(a,h)anthracene
53-70-3
0.055
8.2
Indeno(1,2,3-cd)pyrene
193-39-5
0.0055
3.4
K149
Distillation bottoms from the production of alpha- (or methyl-) chlorinated toluenes, ring-chlorinated toluenes,
benzoyl chlorides, and compounds with mixtures of these functional groups. (This waste does not include still
bottoms from the distillations of benzyl chloride.)
Chlorobenzene
108-90-7
0.057
6.0
Chloroform
67-66-3
0.046
6.0
Chloromethane
74-87-3
0.19
30
p-Dichlorobenzene
106-46-7
0.090
6.0
Hexachlorobenzene
118-74-1
0.055
10
Pentachlorobenzene
608-93-5
0.055
10
1,2,4,5-Tetrachlorobenzene
95-94-3
0.055
14
Toluene
108-88-3
0.080
10
K150
Organic residuals, excluding spent carbon adsorbent, from the spent chlorine gas and hydrochloric acid recovery
processes associated with the production of alpha- (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 alpha- (or methyl-) chlorinated toluenes, ring-chlorinated toluenes, benzoyl
chlorides, and compounds with mixtures of these functional groups.
288
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
P001
Warfarin, & salts, when present at concentrations greater than 0.3%
Warfarin
81-81-2
(WETOX or
CHOXD) fb
CARBN; or INCIN
CMBST
P002
1-Acetyl-2-thiourea
1-Acetyl-2-thiourea
591-08-2
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
P003
Acrolein
Acrolein
107-02-6
0.29
CMBST
P004
Aldrin
Aldrin
309-00-2
0.021
0.068
P005
Allyl alcohol
Allyl alcohol
107-18-6
(WETOX or
CHOXD) fb
CARBN; or INCIN
CMBST
P006
Aluminum phosphide
Aluminum phosphide
20859-73-6
CHOXD; CHRED;
or INCIN
CHOXD; CHRED;
or INCIN
P007
5-Aminomethyl-3-isoxazolol
5-Aminomethyl-3-isoxazolol
2763-96-4
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
P008
4-Aminopyridine
289
4-Aminopyridine
504-24-5
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
P009
Ammonium picrate
Ammonium picrate
131-74-8
CHOXD; CHRED;
CARBN; BIODG;
or INCIN
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
7.6 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 INCIN
INCIN
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 INCIN
INCIN
P017
Bromoacetone
Bromoacetone
598-31-2
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
290
P018
Brucine
Brucine
357-57-3
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
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
INCIN
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 INCIN
INCIN
P024
p-Chloroaniline
p-Chloroaniline
106-47-8
.046
16
P026
1-(o-Chlorophenyl)thiourea
1-(o-Chlorophenyl)thiourea
5344-82-1
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
P027
3-Chloropropionitrile
3-Chloropropionitrile
542-76-7
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
P028
Benzyl chloride
Benzyl chloride
100-44-7
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
291
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 INCIN
CHOXD; WETOX;
or INCIN
P033
Cyanogen chloride
Cyanogen chloride
506-77-4
CHOXD; WETOX;
or INCIN
CHOXD; WETOX;
or INCIN
P034
2-Cyclohexyl-4,6-dinitrophenol
2-Cyclohexyl-4,6-dinitrophenol
131-89-5
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
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 INCIN
CMBST
P041
Diethyl-p-nitrophenyl phosphate
Diethyl-p-nitrophenyl phosphate
311-45-5
CARBN; or INCIN
CMBST
292
P042
Epinephrine
Epinephrine
51-43-4
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
P043
Diisopropylfluorophosphate (DFP)
Diisopropylfluorophosphate (DFP)
55-91-4
CARBN; or INCIN
CMBST
P044
Dimethoate
Dimethoate
60-51-5
CARBN; or INCIN
CMBST
P045
Thiofanox
Thiofanox
39196-18-4
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
P046
alpha,alpha-Dimethylphenethylamine
alpha,alpha-Dimethylphenethyl-
amine
122-09-8
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
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 INCIN
INCIN
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 INCIN
INCIN
P050
Endosulfan
293
Endosulfan I
939-98-8
0.023
0.066
Endosulfan II
33213-6-5
0.029
0.13
Endosulfan sulfate
1031-07-8
0.029
0.13
P051
Endrin
Endrin
72-20-8
0.0028
0.13
Endrin aldehyde
7421-93-4
0.025
0.13
P054
Aziridine
Aziridine
151-56-4
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
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 INCIN
INCIN
P058
Fluoroacetic acid, sodium salt
Fluoroacetic acid, sodium salt
62-74-8
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
P059
Heptachlor
Heptachlor
76-44-8
0.0012
0.066
Heptachlor epoxide
1024-57-3
0.016
0.066
P060
Isodrin
Isodrin
465-73-6
0.021
0.066
P062
Hexaethyl tetraphosphate
Hexaethyl tetraphosphate
757-58-4
CARBN; or INCIN
CMBST
P063
Hydrogen cyanide
Cyanides (Total)
7
57-12-5
1.2
590
Cyanides (Amenable)
7
57-12-5
0.86
30
294
P064
Isocyanic acid, ethyl ester
Isocyanic acid, ethyl ester
624-83-9
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
P065
P065 (mercury fulminate) nonwastewaters, regardless of their total mercury contant, that are not incinerator
residues or are not residues from RMERC.
Mercury
7439-97-6
NA
IMERC
P065
P065 (mercury fulminate) nonwastewaters that are either incinerator residues or are residues from RMERC; and
contain greater than or equal to 260 mg/kg total mercury.
Mercury
7339-97-6
NA
RMERC
P065
P065 (mercury fulminate) nonwastewaters that are residues from RMERC and contain less than 260 mg/kg total
mercury.
Mercury
7439-97-6
NA
0.20 mg/l TCLP
P065
P065 (mercury fulminate) nonwastewaters that are incinerator residues and contain less than 260 mg/kg total
mercury.
Mercury
7439-97-6
NA
0.025 mg/l TCLP
P065
All P065 (mercury fulminate) wastewaters.
Mercury
7439-97-6
0.15
NA
P066
Methomyl
Methomyl
16752-77-5
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
P067
2-Methyl-aziridine
2-Methyl-aziridine
75-55-8
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
P068
Methyl hydrazine
Methyl hydrazine
60-34-4
CHOXD; CHRED;
CARBN; BIODG;
or INCIN
CHOXD; CHRED,
or CMBST
P069
2-Methyllactonitrile
295
2-Methyllactonitrile
75-86-5
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
P070
Aldicarb
Aldicarb
116-06-3
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
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 INCIN
INCIN
P073
Nickel carbonyl
Nickel
7440-02-0
3.98
5.0 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
5.0 mg/l TCLP
P075
Nicotine and salts
Nicotine and salts
54-11-5
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
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
296
Nitroglycerin
55-63-0
CHOXD; CHRED;
CARBN; BIODG or
INCIN
CHOXD; CHRED;
or CMBST
P082
N-Nitrosodimethylamine
N-Nitrosodimethylamine
62-75-9
0.40
2.3
P084
N-Nitrosomethylvinylamine
N-Nitrosomethylvinylamine
4549-40-0
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
P085
Octamethylpyrophosphoramide
Octamethylpyrophosphoramide
152-16-9
CARBN; or INCIN
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 INCIN
CMBST
P089
Parathion
Parathion
56-38-2
0.014
4.6
P092
P092 (phenyl mercuric acetate) nonwastewaters, regardless of their total mercury content, that are not
incinerator residues or are not residues from RMERC.
Mercury
7439-97-6
NA
IMERC; or RMERC
P092
P092 (phenyl mercuric acetate) nonwastewaters that are either incinerator residues or are residues from
RMERC; and still contain greater than or equal to 260 mg/kg total mercury.
Mercury
7439-97-6
NA
RMERC
P092
P092 (phenyl mercuric acetate) nonwastewaters that are residues from RMERC and contain less than 260 mg/kg
total mercury.
Mercury
7439-97-6
NA
0.20 mg/l TCLP
P092
P092 (phenyl mercuric acetate) nonwastewaters that are incinerator residues and contain less than 260 mg/kg
total mercury.
297
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 INCIN
INCIN
P094
Phorate
Phorate
298-02-2
0.021
4.6
P095
Phosgene
Phosgene
75-44-5
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
P096
Phosphine
Phosphine
7803-51-2
CHOXD; CHRED;
or INCIN
CHOXD; CHRED;
or INCIN
P097
Famphur
Famphur
52-85-7
0.017
15
P098
Potassium cyanide.
Cyanides (Total)
7
57-12-5
1.2
590
Cyanides (Amenable)
7
57-12-5
0.86
30
P099
Potassium silver cyanide
Cyanides (Total)
7
57-12-5
1.2
590
Cyanides (Amenable)
7
57-12-5
0.86
30
Silver
7440-22-4
0.43
0.30 mg/l TCLP
P101
Ethyl cyanide (Propanenitrile)
Ethyl cyanide (Propanenitrile)
107-12-0
0.24
360
P102
Propargyl alcohol
298
Propargyl alcohol
107-19-7
(WETOX or
CHOXD) fb
CARBN; or INCIN
CMBST
P103
Selenourea
Selenium
7782-49-2
0.82
0.16 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
0.30 mg/l TCLP
P105
Sodium azide
Sodium azide
26628-22-8
CHOXD; CHRED;
CARBN; BIODG;
or INCIN
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 INCIN
INCIN
P109
Tetraethyldithiopyrophosphate
Tetraethyldithiopyrophosphate
3689-24-5
CARBN; or INCIN
CMBST
P110
Tetraethyl lead
lead
7439-92-1
0.69
0.37 mg/l TCLP
P111
Tetraethylpyrophosphate
Tetraethylpyrophosphate
107-49-3
CARBN; or INCIN
CMBST
P112
Tetranitromethane
Tetranitromethane
509-14-8
CHOXD; CHRED;
CARBN; BIODG;
or INCIN
CHOXD; CHRED;
or CMBST
P113
Thallic oxide
299
Thallium (measured in
wastewaters only)
7440-28-0
1.4
RTHRM; or STABL
P114
Thallium selenite
Selenium
7782-49-2
0.82
0.16 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 INCIN
INCIN
P118
Trichloromethanethiol
Trichloromethanethiol
75-70-7
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
P119
Ammonium vanadate
Vanadium (measured in
wastewaters only)
7440-62-2
4.3
STABL
P120
Vanadium pentoxide
Vanadium (measured in
wastewaters only)
7440-62-2
4.3
STABL
P121
Zinc cyanide
Cyanides (Total)
7
57-12-5
1.2
590
Cyanides (Amenable)
7
57-12-5
0.86
30
P122
Zinc phosphide Zn
3
P
2
, when present at concentrations greater than 10%
Zinc Phosphide
1314-84-7
CHOXD; CHRED;
or INCIN
CHOXD; CHRED;
or INCIN
P123
Toxaphene
Toxaphene
8001-35-2
0.0095
2.6
U001
Acetaldehyde
300
Acetaldehyde
75-07-0
(WETOX or
CHOXD) fb
CARBN; or INCIN
CMBST
U002
Acetone
Acetone
67-64-1
0.28
160
U003
Acetonitrile
Acetonitrile
75-05-8
5.6
INCIN
Acetonitrile; alternate
6
standard
for nonwastewaters only
75-05-8
NA
1.8
U004
Acetophenone
Acetophenone
98-86-2
0.010
9.7
U005
2-Acetylaminofluorene
2-Acetylaminofluorene
53-96-3
0.059
140
U006
Acetyl chloride
Acetyl chloride
75-36-5
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U007
Acrylamide
Acrylamide
79-06-1
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U008
Acrylic acid
Acrylic acid
79-10-7
(WETOX or
CHOXD) fb
CARBN; or INCIN
CMBST
U009
Acrylonitrile
Acrylonitrile
107-13-1
0.24
84
U010
Mitomycin C
Mitomycin C
50-07-7
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
301
U011
Amitrole
Amitrole
61-82-5
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U012
Aniline
Aniline
62-53-3
0.81
14
U014
Auramine
Auramine
492-80-8
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U015
Azaserine
Azaserine
115-02-6
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U016
Benz(c)acridine
Benz(c)acridine
225-51-4
(WETOX or
CHOXD) fb
CARBN; or INCIN
CMBST
U017
Benzal chloride
Benzal chloride
98-87-3
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
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 INCIN
INCIN
U021
Benzidine
302
Benzidine
92-87-5
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
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 INCIN
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 INCIN
INCIN
U027
bis(2-Chloroisopropyl)ether
bis(2-Chloroisopropyl)ether
39638-32-9
108-60-1
0.055
7.2
U028
bis(2-Ethylhexyl)phthalate
bis(2-Ethylhexyl)phthalate
117-81-7
0.28
28
U029
Methyl bromide (Bromomethane)
Methyl bromide (Bromomethane)
74-83-9
0.11
15
U030
4-Bromophenyl phenyl ether
4-Bromophenyl phenyl ether
101-55-3
0.055
15
U031
n-Butyl alcohol
n-Butyl alcohol
71-36-3
5.6
2.6
U032
Calcium chromate
303
Chromium (Total)
7440-47-3
2.77
0.86 mg/l TCLP
U033
Carbon oxyfluoride
Carbon oxyfluoride
353-50-4
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U034
Trichloroacetaldehyde (Chloral)
Trichloroacetaldehyde (Chloral)
75-87-6
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U035
Chlorambucil
Chlorambucil
305-03-3
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U036
Chlordane
Chlordane (alpha and gamma
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
INCIN
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 INCIN
INCIN
U042
2-Chloroethyl vinyl ether
2-Chloroethyl vinyl ether
110-75-8
0.062
INCIN
U043
Vinyl chloride
Vinyl chloride
75-01-4
0.27
6.0
304
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 INCIN
INCIN
U047
2-Chloronaphthalene
2-Chloronaphthalene
91-58-7
0.055
5.6
U048
2-Chlorophenol
2-Chlorophenol
95-57-8
0.044
5.7
U049
4-Chloro-o-toluidine hydrochloride
4-Chloro-o-toluidine hydro-
chloride
3165-93-3
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
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 con-
centrations)
1330-20-7
0.32
30
Lead
7439-92-1
0.69
0.37 mg/l TCLP
U052
Cresols (Cresylic acid)
305
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 con-
centrations)
1319-77-3
0.88
11.2
U053
Crotonaldehyde
Crotonaldehyde
4170-30-3
(WETOX or
CHOXD) fb
CARBN; or INCIN
CMBST
U055
Cumene
Cumene
98-82-8
(WETOX or
CHOXD) fb
CARBN; or INCIN
CMBST
U056
Cyclohexane
Cyclohexane
110-82-7
(WETOX or
CHOXD) fb
CARBN; or INCIN
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 INCIN
CMBST
U059
Daunomycin
Daunomycin
20830-81-3
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U060
DDD
o,p'-DDD
53-19-0
0.023
0.087
p,p'-DDD
72-54-8
0.023
0.087
U061
DDT
306
o,p'-DDT
789-02-6
0.0039
0.087
p,p'-DDT
50-29-3
0.0039
0.087
o,p'-DDD
53-19-0
0.023
0.087
p,p'-DDD
72-54-8
0.023
0.087
o,p'-DDE
3424-82-6
0.031
0.087
p,p'-DDE
72-55-9
0.031
0.087
U062
Diallate
Diallate
2303-16-4
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
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 INCIN
CMBST
U066
1,2-Dibromo-3-chloropropane
1,2-Dibromo-3-chloropropane
96-12-8
0.11
15
U067
Ethylene dibromide (1,2-Dibromoethane)
Ethylene dibromide (1,2-
Dibromoethane)
106-93-4
0.028
15
U068
Dibromomethane
Dibromomethane
74-95-3
0.11
15
U069
Di-n-butyl phthalate
Di-n-butyl phthalate
84-74-2
0.057
28
U070
o-Dichlorobenzene
o-Dichlorobenzene
95-50-1
0.088
6.0
U071
m-Dichlorobenzene
m-Dichlorobenzene
541-73-1
0.036
6.0
U072
p-Dichlorobenzene
307
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 INCIN
INCIN
U074
1,4-Dichloro-2-butene
cis-1,4-Dichloro-2-butene
1476-11-5
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
trans-1,4-Dichloro-2-butene
764-41-0
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U075
Dichlorodifluoromethane
Dichlorodifluoromethane
75-71-8
0.23
7.2
U076
1,1-Dichloroethane
1,1-Dichloroethane
75-34-3
0.059
6.0
U077
1,2-Dichloroethane
1,2-Dichloroethane
107-06-2
0.21
6.0
U078
1,1-Dichloroethylene
1,1-Dichloroethylene
75-35-4
0.025
6.0
U079
1,2-Dichloroethylene
trans-1,2-Dichloroethylene
156-60-5
0.054
30
U080
Methylene chloride
Methylene chloride
75-09-2
0.089
30
U081
2,4-Dichlorophenol
2,4-Dichlorophenol
120-83-2
0.044
14
U082
2,6-Dichlorophenol
2,6-Dichlorophenol
87-65-0
0.044
14
U083
1,2-Dichloropropane
308
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 INCIN
CMBST
U086
N,N'-Diethylhydrazine
N,N'-Diethylhydrazine
1615-80-1
CHOXD; CHRED;
CARBN; BIODG;
or INCIN
CHOXD; CHRED;
or CMBST
U087
O,O-Diethyl S-methyldithiophosphate
O,O-Diethyl S-methyldithio-
phosphate
3288-58-2
CARBN; or INCIN
CMBST
U088
Diethyl phthalate
Diethyl phthalate
84-66-2
0.20
28
U089
Diethyl stilbestrol
Diethyl stilbestrol
56-53-1
(WETOX or
CHOXD) fb
CARBN; or INCIN
CMBST
U090
Dihydrosafrole
Dihydrosafrole
94-58-6
(WETOX or
CHOXD) fb
CARBN; or INCIN
CMBST
U091
3,3'-Dimethoxybenzidine
3,3'-Dimethoxybenzidine
119-90-4
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U092
Dimethylamine
309
Dimethylamine
124-40-3
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U093
p-Dimethylaminoazobenzene
p-Dimethylaminoazobenzene
60-11-7
0.13
INCIN
U094
7,12-Dimethylbenz(a)anthracene
7,12-Dimethylbenz(a)anthracene
57-97-6
(WETOX or
CHOXD) fb
CARBN; or INCIN
CMBST
U095
3,3'-Dimethylbenzidine
3,3'-Dimethylbenzidine
119-93-7
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U096
alpha, alpha-Dimethyl benzyl hydroperoxide
alpha, alpha-Dimethyl benzyl
hydroperoxide
80-15-9
CHOXD; CHRED;
CARBN; BIODG;
or INCIN
CHOXD; CHRED;
or CMBST
U097
Dimethylcarbamoyl chloride
Dimethylcarbamoyl chloride
79-44-7
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U098
1,1-Dimethylhydrazine
1,1-Dimethylhydrazine
57-14-7
CHOXD; CHRED;
CARBN; BIODG;
or INCIN
CHOXD; CHRED;
or CMBST
U099
1,2-Dimethylhydrazine
1,2-Dimethylhydrazine
540-73-8
CHOXD; CHRED;
CARBN; BIODG;
or INCIN
CHOXD; CHRED;
or CMBST
U101
2,4-Dimethylphenol
2,4-Dimethylphenol
105-67-9
0.036
14
U102
Dimethyl phthalate
310
Dimethyl phthalate
131-11-3
0.047
28
U103
Dimethyl sulfate
Dimethyl sulfate
77-78-1
CHOXD; CHRED;
CARBN; BIODG;
or INCIN
CHOXD; CHRED;
or CMBST
U105
2,4-Dinitrotoluene
2,4-Dinitrotoluene
121-14-2
0.32
140
U106
2,6-Dinitrotoluene
2,6-Dinitrotoluene
606-20-2
0.55
28
U107
Di-n-octyl phthalate
Di-n-octyl phthalate
117-84-0
0.017
28
U108
1,4-Dioxane
1,4-Dioxane
123-91-1
(WETOX or
CHOXD) fb
CARBN; or INCIN
CMBST
1,4-Dioxane; alternate
6
standard
for nonwastewaters only
123-91-1
NA
170
U109
1,2-Diphenylhydrazine
1,2-Diphenylhydrazine
122-66-7
CHOXD; CHRED;
CARBN; BIODG;
or INCIN
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 INCIN
INCIN
U111
Di-n-propylnitrosamine
Di-n-propylnitrosamine
621-64-7
0.40
14
U112
Ethyl acetate
Ethyl acetate
141-78-8
0.34
33
311
U113
Ethyl acrylate
Ethyl acrylate
140-88-5
(WETOX or
CHOXD) fb
CARBN; or INCIN
CMBST
U114
Ethylenebisdithiocarbamic acid salts and esters
Ethylenebisdithiocarbamic acid
111-54-6
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U115
Ethylene oxide
Ethylene oxide
75-21-8
(WETOX or
CHOXD) fb
CARBN; or INCIN
CHOXD; or INCIN
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 INCIN
INCIN
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 INCIN
INCIN
U120
Fluoranthene
Fluoranthene
206-44-0
0.068
3.4
U121
Trichloromonofluoromethane
Trichloromonofluoromethane
75-69-4
0.020
30
U122
Formaldehyde
312
Formaldehyde
50-00-0
(WETOX or
CHOXD) fb
CARBN; or INCIN
CMBST
U123
Formic acid
Formic acid
64-18-6
(WETOX or
CHOXD) fb
CARBN; or INCIN
CMBST
U124
Furan
Furan
110-00-9
(WETOX or
CHOXD) fb
CARBN; or INCIN
CMBST
U125
Furfural
Furfural
98-01-1
(WETOX or
CHOXD) fb
CARBN; or INCIN
CMBST
U126
Glycidylaldehyde
Glycidylaldehyde
765-34-4
(WETOX or
CHOXD) fb
CARBN; or INCIN
CMBST
U127
Hexachlorobenzene
Hexachlorobenzene
118-74-1
0.055
10
U128
Hexachlorobutadiene
Hexachlorobutadiene
87-68-3
0.055
5.6
U129
Lindane
alpha-BHC
319-84-6
0.00014
0.066
beta-BHC
319-85-7
0.00014
0.066
delta-BHC
319-86-8
0.023
0.066
gamma-BHC (Lindane)
58-89-9
0.0017
0.066
U130
Hexachlorocyclopentadiene
Hexachlorocyclopentadiene
77-47-4
0.057
2.4
U131
Hexachloroethane
Hexachloroethane
67-72-1
0.055
30
313
U132
Hexachlorophene
Hexachlorophene
70-30-4
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U133
Hydrazine
Hydrazine
302-01-2
CHOXD; CHRED;
CARBN; BIODG;
or INCIN
CHOXD; CHRED;
or CMBST
U134
Hydrogen fluoride
Fluoride (measured in wastewaters
only)
16964-48-8
35
ADGAS fb NEUTR;
or NEUTR
U135
Hydrogen sulfide
Hydrogen sulfide
7783-06-4
CHOXD; CHRED;
or INCIN
CHOXD; CHRED;
or INCIN
U136
Cacodylic acid
Arsenic
7440-38-2
1.4
5.0 mg/l TCLP
U137
Indeno(1,2,3-cd)pyrene
Indeno(1,2,3-cd)pyrene
193-39-5
0.0055
3.4
U138
Iodomethane
Iodomethane
74-88-4
0.19
65
U140
Isobutyl alcohol
Isobutyl alcohol
78-83-1
5.6
170
U141
Isosafrole
Isosafrole
120-58-1
0.081
2.6
U142
Kepone
Kepone
143-50-8
0.0011
0.13
U143
Lasiocarpine
314
Lasiocarpine
303-34-4
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U144
Lead acetate
Lead
7439-92-1
0.69
0.37 mg/l TCLP
U145
Lead phosphate
Lead
7439-92-1
0.69
0.37 mg/l TCLP
U146
Lead subacetate
Lead
7439-92-1
0.69
0.37 mg/l TCLP
U147
Maleic anhydride
Maleic anhydride
108-31-6
(WETOX or
CHOXD) fb
CARBN; or INCIN
CMBST
U148
Maleic hydrazide
Maleic hydrazide
123-33-1
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U149
Malononitrile
Malononitrile
109-77-3
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U150
Melphalan
Melphalan
148-82-3
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
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.
315
Mercury
7439-97-6
NA
0.025 mg/l TCLP
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 INCIN
INCIN
U154
Methanol
Methanol
67-56-1
(WETOX or
CHOXD) fb
CARBN; or INCIN
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 INCIN
INCIN
U157
3-Methylcholanthrene
3-Methylcholanthrene
56-49-5
0.0055
15
U158
4,4'-Methylene bis(2-chloroaniline)
4,4'-Methylene bis(2-chloro-
aniline)
101-14-4
0.50
30
U159
Methyl ethyl ketone
316
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 INCIN
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 INCIN
INCIN
U164
Methylthiouracil
Methylthiouracil
56-04-2
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U165
Naphthalene
Naphthalene
91-20-3
0.059
5.6
U166
1,4-Naphthoquinone
1,4-Naphthoquinone
130-15-4
(WETOX or
CHOXD) fb
CARBN; or INCIN
CMBST
U167
1-Naphthylamine
1-Naphthylamine
134-32-7
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U168
2-Naphthylamine
2-Naphthylamine
91-59-8
0.52
INCIN
U169
Nitrobenzene
317
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 INCIN
INCIN
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 INCIN
INCIN
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 INCIN
INCIN
U177
N-Nitroso-N-methylurea
N-Nitroso-N-methylurea
684-93-5
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U178
N-Nitroso-N-methylurethane
N-Nitroso-N-methylurethane
615-53-2
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U179
N-Nitrosopiperidine
N-Nitrosopiperidine
100-75-4
0.013
35
U180
N-Nitrosopyrrolidine
N-Nitrosopyrrolidine
930-55-2
0.013
35
318
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 INCIN
CMBST
U183
Pentachlorobenzene
Pentachlorobenzene
608-93-5
0.055
10
U184
Pentachloroethane
Pentachloroethane
76-01-7
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
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 INCIN
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 INCIN
CHOXD; CHRED;
or INCIN
U190
Phthalic anhydride
319
Phthalic anhydride (measured as
Phthalic acid or Terephthalic acid)
100-21-0
0.055
28
Phthalic anhydride
85-44-9
0.055
28
U191
2-Picoline
2-Picoline
109-06-8
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
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 INCIN
INCIN
U194
n-Propylamine
n-Propylamine
107-10-8
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U196
Pyridine
Pyridine
110-86-1
0.014
16
U197
p-Benzoquinone
p-Benzoquinone
106-51-4
(WETOX or
CHOXD) fb
CARBN; or INCIN
CMBST
U200
Reserpine
Reserpine
50-55-5
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U201
Resorcinol
Resorcinol
108-46-3
(WETOX or
CHOXD) fb
CARBN; or INCIN
CMBST
U202
Saccharin and salts
320
Saccharin
81-07-2
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U203
Safrole
Safrole
94-59-7
0.081
22
U204
Selenium dioxide
Selenium
7782-49-2
0.82
0.16 mg/l TCLP
U205
Selenium sulfide
Selenium
7782-49-2
0.82
0.16 mg/l TCLP
U206
Streptozotocin
Streptozotocin
18883-66-4
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U207
1,2,4,5-Tetrachlorobenzene
1,2,4,5-Tetrachlorobenzene
95-94-3
0.055
14
U208
1,1,1,2-Tetrachloroethane
1,1,1,2-Tetrachloroethane
630-20-6
0.057
6.0
U209
1,1,2,2-Tetrachloroethane
1,1,2,2-Tetrachloroethane
79-34-5
0.057
6.0
U210
Tetrachloroethylene
Tetrachloroethylene
127-18-4
0.056
6.0
U211
Carbon tetrachloride
Carbon tetrachloride
56-23-5
0.057
6.0
U213
Tetrahydrofuran
Tetrahydrofuran
109-99-9
(WETOX or
CHOXD) fb
CARBN; or INCIN
CMBST
U214
Thallium (I) acetate
321
Thallium (measured in
wastewaters only)
7440-28-0
1.4
RTHRM; or STABL
U215
Thallium (I) carbonate
Thallium (measured in
wastewaters only)
7440-28-0
1.4
RTHRM; or STABL
U216
Thallium (I) chloride
Thallium (measured in
wastewaters only)
7440-28-0
1.4
RTHRM; or STABL
U217
Thallium (I) nitrate
Thallium (measured in
wastewaters only)
7440-28-0
1.4
RTHRM; or STABL
U218
Thioacetamide
Thioacetamide
62-55-5
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U219
Thiourea
Thiourea
62-56-6
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U220
Toluene
Toluene
108-88-3
0.080
10
U221
Toluenediamine
Toluenediamine
25376-45-8
CARBN; or INCIN
CMBST
U222
o-Toluidine hydrochloride
o-Toluidine hydrochloride
636-21-5
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U223
Toluene diisocyanate
Toluene diisocyanate
26471-62-5
CARBN; or INCIN
CMBST
U225
Bromoform (Tribromomethane)
Bromoform (Tribromomethane)
75-25-2
0.63
15
322
U226
1,1,1-Trichloroethane
1,1,1-Trichloroethane
71-55-6
0.054
6.0
U227
1,1,2-Tricloroethane
1,1,2-Tricloroethane
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 INCIN
INCIN
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 INCIN
INCIN
U237
Uracil mustard
Uracil mustard
66-75-1
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U238
Urethane (Ethyl carbamate)
Urethane (Ethyl carbamate)
51-79-6
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U239
Xylenes
Xylenes-mixed isomers
(sum of o-, m-, and p-xylene con-
centrations)
1330-20-7
0.32
30
U240
2,4-D (2,4-Dichlorophenoxyacetic acid)
323
2,4-D (2,4-Dichlorophenoxyacetic
acid)
94-75-7
0.72
10
2,4-D (2,4-Dichlorophenoxyacetic
acid) salts and esters
NA
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U243
Hexachloropropylene
Hexachloropropylene
1888-71-7
0.035
30
U244
Thiram
Thiram
137-26-8
(WETOX or
CHOXD) fb
CARBN; or INCIN
INCIN
U246
Cyanogen bromide
Cyanogen bromide
506-68-3
CHOXD; WETOX;
or INCIN
CHOXD; WETOX;
or INCIN
U247
Methoxychlor
Methoxychlor
72-43-5
0.25
0.18
U248
Warfarin, & salts, when present at concentrations of 0.3% or less
Warfarin
81-81-2
(WETOX or
CHOXD) fb
CARBN; or INCIN
CMBST
U249
Zinc phosphide, Zn
3
P
2
, when present at concentrations of 10% or less
Zinc Phosphide
1314-84-7
CHOXD; CHRED;
or INCIN
CHOXD; CHRED;
or INCIN
U328
o-Toluidine
o-Toluidine
95-53-4
INCIN; or CHOXD
fb (BIODG or
CARBN); or
BIODG fb CARBN
INCIN; or Thermal
Destruction
U353
p-Toluidine
p-Toluidine
106-49-0
INCIN; or CHOXD
fb (BIODG or
CARBN); or
BIODG fb CARBN
INCIN; or Thermal
Destruction
324
U359
2-Ethoxyethanol
2-Ethoxyethanol
110-80-5
INCIN; or CHOXD
fb (BIODG or
CARBN); or
BIODG fb CARBN
CMBST
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 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 35 Ill. Adm. Code 728.Table C, "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 treatement
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 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 combustion in fuel substitution units operating in accordance
with applicable technical requirements. A facility may comply with these treatment standards according
to provisions in 35 Ill. Adm. Code 728.140(d). All concentration standards for nonwastewaters are
based on analysis of grab samples.
6
Where an alternate treatment standard or set of alternate standards has been indicated, a facility may
comply with this alternate standard, but only for the Treatment or Regulatory Subcategory or physical
form (i.e., wastewater or nonwastewater) specified for that alternate standard.
7
Both Cyanides (Total) and Cyanides (Amenable) for nonwastewaters are to be analyzed using Method
9010 or 9012, found in "Test Methods for Evaluating Solid Waste, Physical or Chemical Methods",
U.S. EPA Publication SW-846, as 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.
NA
means not applicable.
(Source: Amended at 20 Ill. Reg. ________, effective ______________________)
Section 728.Table U
Universal Treatment Standards (UTS)
Nonwastewater
Standard
325
Regulated Constituent-Common
Name
CAS
1
No.
Wastewater Standard
Concentration (in
mg/l
2
)
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
1.8
Acetophenone
96-86-2
0.010
9.7
2-Acetylaminofluorene
53-96-3
0.059
140
Acrolein
107-02-8
0.29
NA
Acrylamide
79-06-1
19
23
Acrylonitrile
107-13-1
0.24
84
Aldrin
309-00-2
0.021
0.066
4-Aminobiphenyl
92-67-1
0.13
NA
Aniline
62-53-3
0.81
14
Anthracene
120-12-7
0.059
3.4
Aramite
140-57-8
0.36
NA
alpha-BHC
319-84-6
0.00014
0.066
beta-BHC
319-85-7
0.00014
0.066
delta-BHC
319-86-8
0.023
0.066
gamma-BHC
58-89-9
0.0017
0.066
Benzene
71-43-2
0.14
10
Benz(a)anthracene
56-55-3
0.059
3.4
Benzal chloride
98-87-3
0.055
6.0
326
Benzo(b)fluoranthene (difficult to
distinguish from
benzo(k)fluoranthene)
205-99-2
0.11
6.8
Benzo(k)fluoranthene (difficult to
distinguish from
benzo(b)fluoranthene)
207-08-9
0.11
6.8
Benzo(g,h,i)perylene
191-24-2
0.0055
1.8
Benzo(a)pyrene
50-32-8
0.061
3.4
Bromodichloromethane
75-27-4
0.35
15
Methyl bromide (Bromomethane)
74-83-9
0.11
15
4-Bromophenyl phenyl ether
101-55-3
0.055
15
n-Butyl alcohol
71-36-3
5.6
2.6
Butyl benzyl phthalate
85-68-7
0.017
28
2-sec-Butyl-4,6-dinitrophenol
(Dinoseb)
88-85-7
0.066
2.5
Carbon disulfide
75-15-0
3.8
4.8 mg/l TCLP
Carbon tetrachloride
56-23-5
0.057
6.0
Chlordane (alpha and gamma
isomers)
57-74-9
0.0033
0.26
p-Chloroaniline
106-47-8
0.46
16
Chlorobenzene
108-90-7
0.057
6.0
Chlorobenzilate
510-15-6
0.10
NA
2-Chloro-1,3-butadiene
126-99-8
0.057
0.28
Chlorodibromomethane
124-48-1
0.057
15
Chloroethane
75-00-3
0.27
6.0
bis(2-Chloroethoxy)methane
111-91-1
0.036
7.2
bis(2-Chloroethyl)ether
111-44-4
0.033
6.0
Chloroform
67-66-3
0.046
6.0
327
bis(2-Chloroisopropyl)ether
108-60-1
0.055
7.2
p-Chloro-m-cresol
59-50-7
0.018
14
2-Chloroethyl vinyl ether
110-75-8
0.062
NA
Chloromethane (Methyl chloride)
74-87-3
0.19
30
2-Chloronaphthalene
91-58-7
0.055
5.6
2-Chlorophenol
95-57-8
0.044
5.7
3-Chloropropylene
107-05-1
0.036
30
Chrysene
218-01-9
0.059
3.4
o-Cresol
95-48-7
0.11
5.6
m-Cresol (difficult to distinguish
from p-cresol)
108-39-4
0.77
5.6
p-Cresol (difficult to distinguish
from m-cresol)
106-44-5
0.77
5.6
Cyclohexanone
108-94-1
0.36
0.75 mg/l TCLP
1,2-Dibromo-3-chloropropane
96-12-8
0.11
15
Ethylene dibromide (1,2-
Dibromoethane)
106-93-4
0.028
15
Dibromomethane
74-95-3
0.11
15
2,4-D (2,4-Dichlorophenoxyacetic
acid)
94-75-7
0.72
10
o,p'-DDD
53-19-0
0.023
0.087
p,p'-DDD
72-54-8
0.023
0.087
o,p'-DDE
3424-82-6
0.031
0.087
p,p'-DDE
72-55-9
0.031
0.087
o,p'-DDT
789-02-6
0.0039
0.087
p,p'-DDT
50-29-3
0.0039
0.087
Dibenz(a,h)anthracene
53-70-3
0.055
8.2
328
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
329
p-Dimethylaminoazobenzene
60-11-7
0.13
NA
Di-n-propylnitrosamine
621-64-7
0.40
14
1,4-Dioxane
123-91-1
NA
170
Diphenylamine (difficult to
distinguish from
diphenylnitrosamine)
122-39-4
0.92
13
Diphenylnitrosamine (difficult to
distinguish from diphenylamine)
86-30-6
0.92
13
1,2-Diphenylhydrazine
122-66-7
0.087
NA
Disulfoton
298-04-4
0.017
6.2
Endosulfan I
939-98-8
0.023
0.066
Endosulfan II
33213-6-5
0.029
0.13
Endosulfan sulfate
1-31-07-8
0.029
0.13
Endrin
72-20-8
0.0028
0.13
Endrin aldehyde
7421-93-4
0.025
0.13
Ethyl acetate
141-78-6
0.34
33
Ethyl cyanide (Propanenitrile)
107-12-0
0.24
360
Ethyl benzene
100-41-4
0.057
10
Ethyl ether
60-29-7
0.12
160
bis(2-Ethylhexyl) phthalate
117-81-7
0.28
28
Ethyl methacrylate
97-63-2
0.14
160
Ethylene oxide
75-21-8
0.12
NA
Famphur
52-85-7
0.017
15
Fluoranthene
206-44-0
0.068
3.4
Fluorene
86-73-7
0.059
3.4
Heptachlor
76-44-8
0.0012
0.066
Heptachlor epoxide
1024-57-3
0.016
0.066
330
Hexachlorobenzene
118-74-1
0.055
10
Hexachlorobutadiene
87-68-3
0.055
5.6
Hexachlorocyclopentadiene
77-47-4
0.057
2.4
HxCDDs (All Hexachlorodibenzo-
p-dioxins)
NA
0.000063
0.001
HxCDFs (All 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
0.75 mg/l TCLP
Methapyrilene
91-80-5
0.081
1.5
Methoxychlor
72-43-5
0.25
0.18
3-Methylcholanthrene
56-49-5
0.0055
15
4,4-Methylene bis(2-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
331
Methyl parathion
298-00-0
0.014
4.6
Naphthalene
91-20-3
0.059
5.6
2-Naphthylamine
91-59-8
0.52
NA
o-Nitroaniline
88-74-4
0.27
14
p-Nitroaniline
100-01-6
0.028
28
Nitrobenzene
98-95-3
0.068
14
5-Nitro-o-toluidine
99-55-8
0.32
28
o-Nitrophenol
88-75-5
0.028
13
p-Nitrophenol
100-02-7
0.12
29
N-Nitrosodiethylamine
55-18-5
0.40
28
N-Nitrosodimethylamine
62-75-9
0.40
2.3
N-Nitroso-di-n-butylamine
924-16-3
0.40
17
N-Nitrosomethylethylamine
10595-95-6
0.40
2.3
N-Nitrosomorpholine
59-89-2
0.40
2.3
N-Nitrosopiperidine
100-75-4
0.013
35
N-Nitrosopyrrolidine
930-55-2
0.013
35
Parathion
56-38-2
0.014
4.6
Total PCBs (sum of all PCB
isomers, or all Aroclors)
1336-36-3
0.10
10
Pentachlorobenzene
608-93-5
0.055
10
PeCDDs (All Pentachlorodibenzo-
p-dioxins)
NA
0.000063
0.001
PeCDFs (All 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
332
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
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 (2,4,5-Trichloro-
phenoxyacetic acid)
93-76-5
0.72
7.9
1,2,4,5-Tetrachlorobenzene
95-94-3
0.055
14
TCDDs (All Tetrachlorodibenzo-
p-dioxins)
NA
0.000063
0.001
TCDFs (All 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
333
1,1,1-Trichloroethane
71-55-6
0.054
6.0
1,1,2-Trichloroethane
79-00-5
0.054
6.0
Trichloroethylene
79-01-6
0.054
6.0
Trichloromonofluoromethane
75-69-4
0.020
30
2,4,5-Trichlorophenol
95-95-4
0.18
7.4
2,4,6-Trichlorophenol
88-06-2
0.035
7.4
1,2,3-Trichloropropane
96-18-4
0.85
30
1,1,2-Trichloro-1,2,2-trifluoro-
ethane
76-13-1
0.057
30
tris-(2,3-Dibromopropyl)
phosphate
126-72-7
0.11
0.10
Vinyl chloride
75-01-4
0.27
6.0
Xylenes-mixed isomers (sum of o-
, m-, and p-xylene concentrations)
1330-20-7
0.32
30
Antimony
7440-36-0
1.9
2.1 mg/l TCLP
Arsenic
7440-38-2
1.4
5.0 mg/l TCLP
Barium
7440-39-3
1.2
7.6 mg/l TCLP
Beryllium
7440-41-7
0.82
0.014 mg/l TCLP
Cadmium
7440-43-9
0.69
0.19 mg/l TCLP
Chromium (Total)
7440-47-3
2.77
0.86 mg/l TCLP
Cyanides (Total)
4
57-12-5
1.2
590
Cyanides (Amenable)
4
57-12-5
0.86
30
Fluoride
16964-48-8
35
NA
Lead
7439-92-1
0.69
0.37 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
5.0 mg/l TCLP
334
Selenium
7782-49-2
0.82
0.16 mg/l TCLP
Silver
7440-22-4
0.43
0.30 mg/l TCLP
Sulfide
8496-25-8
14
NA
Thallium
7440-28-0
1.4
0.078 mg/l TCLP
Vanadium
5
7440-62-2
4.3
0.23 mg/l TCLP
Zinc
5
7440-66-6
2.61
5.3 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 40 CFR 268.40(d). All concentration standards for nonwastewaters are based on analysis of grab
samples.
4
Both Cyanides (Total) and Cyanides (Amenable) for nonwastewaters are to be analyzed using Method
9010 or 9012, found in "Test Methods for Evaluating Solid Waste, Physical/Chemical Methods", U.S.
EPA 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
Vanadium and zinc are not "underlying hazardous constituents" in characteristic wastes, according to
the definition at Section 728.102(i).
Note: NA means not applicable.
(Source: Amended at 20 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
335
733.102
Applicability--Batteries
733.103
Applicability--Pesticides
733.104
Applicability--Mercury Thermostats
733.105
Applicability--Household and Conditionally Exempt Small Quantity Generator Waste
733.106
Definitions
SUBPART B: STANDARDS FOR SMALL QUANTITY HANDLERS
Section
733.110
Applicability
733.111
Prohibitions
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
336
Section
733.170
Imports
SUBPART G: PETITIONS TO INCLUDE OTHER WASTES
Section
733.180
General
733.181
Factors for Petitions to Include Other Wastes
AUTHORITY: Implementing Section 22.4 and authorized by Section 27 of the Environmental Protection Act
[415 ILCS 5/22.4 and 27].
SOURCE: Adopted in R95-20 at 20 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; and
3)
Thermostats, as described in Section 733.104.
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.
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, except those listed in subsection (b) below.
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, 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.
3)
Batteries, as described in Section 733.106, 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.
337
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.
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, that meet the following conditions, except those
listed in subsection (b) below:
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. § 136q), including, but not limited to
those owned by the registrant responsible for conducting the recall; or
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, and unused pesticide products
described in subsection (a)(2) above, 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 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 or those that are not
wastes as described in subsection (d) below; and
4)
Pesticides that are not hazardous waste. A pesticide is a hazardous waste if it is a
waste (subsection (b)(3) above) 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.
338
1)
A recalled pesticide described in subsection (a)(1) above 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).
2)
An unused pesticide product described in subsection (a)(2) above 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, 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, 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.
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, except those listed in subsection (b) below.
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 describes when thermostats become wastes.
2)
Thermostats that are not hazardous waste. A thermostat is a hazardous waste if it is a
waste (subsection (b)(1) above) and it exhibits one or more of the characteristics
identified in 35 Ill. Adm. Code 721.Subpart C.
339
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.
Section 733.105 Applicability--Household and Conditionally Exempt Small Quantity Generator Waste
a)
Persons managing the wastes listed below may, at their option, manage them under the
requirements of this Part:
1)
Household wastes that are exempt under 35 Ill. Adm. Code 721.104(b)(1) and are also
of the same type as the universal wastes defined at Section 733.106; 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 universal wastes defined at
Section 733.106.
b)
Persons that commingle the wastes described in subsections (a)(1) and (a)(2) above together
with universal waste regulated under this Part shall manage the commingled waste under the
requirements of this Part.
Section 733.106 Definitions
"Battery" means a device consisting of one or more electrically connected electrochemical cells
which is designed to receive, store, and deliver electric energy. An electrochemical cell is a
system consisting of an anode, cathode, and an electrolyte, plus such connections (electrical
and mechanical) as may be needed to allow the cell to deliver or receive electrical energy. The
term battery also includes an intact, unbroken battery from which the electrolyte has been
removed.
"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.
"FIFRA" means the Federal Insecticide, Fungicide, and Rodenticide Act (7 U.S.C. §§ 136-
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.
"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, or thermostats, 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.
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"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 U.S.C. § 321(v)), incorporated by reference in Section 720.111,
It is an animal drug that has been determined by regulation of the federal Secretary of
Health and Human Services pursuant to FFDCA Section 360b(j), 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 U.S.C. § 321(w)), incorporated
by reference in Section 720.111 that bears or contains any substances described in
either of the two preceding paragraphs of this definition.
BOARD NOTE: The second exception of corresponding 40 CFR 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 U.S.C. § 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 definateness
required under Illinois law.
"Small quantity handler of universal waste" means a universal waste handler (as defined in this
Section) that does not accumulate more than 5,000 kilograms total of universal waste (batteries,
pesticides, or thermostats, calculated collectively) at any time.
"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).
"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; and
Thermostats, as described in Section 733.104.
"Universal waste handler" means either of the following:
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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 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.
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).
Section 733.111 Prohibitions
A small quantity handler of universal waste is prohibited from the following acts:
a)
Disposing of universal waste; and
b)
Diluting or treating universal waste, except by responding to releases as provided in Section
733.117 or by managing specific wastes as provided in Section 733.113.
Section 733.112 Notification
A small quantity handler of universal waste is not required to notify the Agency of its universal waste handling
activities.
Section 733.113 Waste Management
a)
Universal waste batteries. A small quantity handler of universal waste shall manage universal
waste batteries 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 battery
that shows evidence of leakage, spillage, or damage that could cause leakage under
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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, 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 landfills 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:
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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, 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 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;
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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;
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).
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 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, 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 landfills apply to the waste. Consult the ordinances of
relevant units of local government to determine whether local requirements
apply.
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 phrases: "Universal Waste-
Battery(ies)", "Waste Battery(ies)", or "Used Battery(ies)";
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:
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1)
The label that was on or accompanied the product as sold or distributed; and
2)
The words "Universal Waste-Pesticide(s)" or "Waste-Pesticide(s)";
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 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 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)" or "Waste-Pesticide(s)"; and
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)", or "Waste Mercury Thermostat(s)", or "Used Mercury
Thermostat(s)".
Section 733.115 Accumulation Time Limits
a)
A small quantity handler of universal waste may accumulate universal waste for no longer than
one year from the date the universal waste is generated or received from another handler,
unless the requirements of subsection (b) below are met.
b)
A small quantity handler of universal waste may accumulate universal waste for longer than
one year from the date the universal waste is generated or received from another handler if
such activity is solely for the purpose of accumulation of such quantities of universal waste as
are necessary to facilitate proper recovery, treatment, or disposal. However, the handler bears
the burden of proving that such activity is solely for the purpose of accumulation of such
quantities of universal waste as are necessary to facilitate proper recovery, treatment, or
disposal.
c)
A small quantity handler of universal waste that accumulates universal waste shall be able to
demonstrate the length of time that the universal waste has been accumulated from the date it
becomes a waste or is received. The handler may make this demonstration in any of the
following ways:
1)
Placing the universal waste in a container and marking or labeling the container with
the earliest date that any universal waste in the container became a waste or was
received;
2)
Marking or labeling each individual item of universal waste (e.g., each battery or
thermostat) with the date it became a waste or was received;
346
3)
Maintaining an on-site inventory system that identifies the date each universal waste
became a waste or was received;
4)
Maintaining an on-site inventory system that identifies the earliest date that any
universal waste in a group of universal waste items or a group of containers of
universal waste became a waste or was received;
5)
Placing the universal waste in a specific accumulation area and identifying the earliest
date that any universal waste in the area became a waste or was received; or
6)
Any other method that clearly demonstrates the length of time that the universal waste
has been accumulated from the date it became a waste or was received.
Section 733.116 Employee Training
A small quantity handler of universal waste shall inform all employees who handle or have responsibility for
managing universal waste. The information must describe proper handling and emergency procedures
appropriate to the type(s) of universal waste handled at the facility.
Section 733.117 Response to Releases
a)
A small quantity handler of universal waste shall immediately contain all releases of universal
waste and other residues from universal waste.
b)
A small quantity handler of universal waste shall determine whether any material resulting
from the release is hazardous waste, and if so, shall manage the hazardous waste 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 material resulting from the release and
shall manage it in compliance with 35 Ill. Adm. Code 722.
Section 733.118 Off-Site Shipments
a)
A small quantity handler of universal waste is prohibited from sending or taking universal
waste to a place other than another universal waste handler, a destination facility, or a foreign
destination.
b)
If a small quantity handler of universal waste self-transports universal waste off-site, the
handler becomes a universal waste transporter for those self-transportation activities and shall
comply with the transporter requirements of 733.Subpart D while transporting the universal
waste.
c)
If a universal waste being offered for off-site transportation meets the definition of hazardous
materials under 49 CFR 171 through 180, a small quantity handler of universal waste shall
package, label, mark, and placard the shipment and prepare the proper shipping papers in
accordance with the applicable USDOT regulations under 49 CFR 172 through 180.
d)
Prior to sending a shipment of universal waste to another universal waste handler, the
originating handler shall ensure that the receiving handler agrees to receive the shipment.
347
e)
If a small quantity handler of universal waste sends a shipment of universal waste to another
handler or to a destination facility and the shipment is rejected by the receiving handler or
destination facility, the originating handler shall either:
1)
Receive the waste back when notified that the shipment has been rejected, or
2)
Agree with the receiving handler on a destination facility to which the shipment will
be sent.
f)
A small quantity handler of universal waste may reject a shipment containing universal waste
or a portion of a shipment containing universal waste that it has received from another handler.
If a handler rejects a shipment or a portion of a shipment, it shall contact the originating
handler to notify the originating handler of the rejection and to discuss reshipment of the load.
The handler shall perform either of the following actions:
1)
Send the shipment back to the originating handler, or
2)
If agreed to by both the originating and receiving handler, send the shipment to a
destination facility.
g)
If a small quantity handler of universal waste receives a shipment containing hazardous waste
that is not a universal waste, the handler shall immediately notify the Agency (Bureau of Land,
Illinois EPA, 1001 North Grand Avenue, P.O. Box 19276, Springfield, Illinois 62794-9276
(telephone: 217-782-6761)) of the illegal shipment, and provide the name, address, and phone
number of the originating shipper. The Agency will provide instructions for managing the
hazardous waste.
h)
If a small quantity handler of universal waste receives a shipment of non-hazardous, non-
universal waste, the handler may manage the waste in any way that is in compliance with
applicable federal, 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 landfills apply to the
waste. Consult the ordinances of relevant units of local government to determine whether local
requirements apply.
Section 733.119 Tracking Universal Waste Shipments
A small quantity handler of universal waste is not required to keep records of shipments of universal waste.
Section 733.120 Exports
A small quantity handler of universal waste that sends universal waste to a foreign destination shall:
a)
Comply with the requirements applicable to a primary exporter in 35 Ill. Adm. Code 722.153;
722.156(a)(1) through (a)(4), (a)(6), and (b); and 722.157;
b)
Export such universal waste only upon consent of the receiving country and in conformance
with the USEPA Acknowledgement of Consent, as defined in 35 Ill. Adm. Code 722.Subpart
E; and
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c)
Provide a copy of the USEPA Acknowledgment of Consent for the shipment to the transporter
transporting the shipment for export.
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).
Section 733.131 Prohibitions
A large quantity handler of universal waste is prohibited from the following:
a) Disposing of universal waste; and
b) Diluting or treating universal waste, except by responding to releases, as provided in Section
733.137, or by managing specific wastes, as provided in Section 733.133.
Section 733.132 Notification
a)
Written notification of universal waste management.
1)
Except as provided in subsections (a)(2) and (a)(3) below, 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;
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);
349
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) the handler is accumulating above this quantity.
BOARD NOTE: At 60 Fed. Reg. 25520-21 (May 11, 1995), USEPA explained that
that 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.
Section 733.133 Waste Management
a)
Universal waste batteries. A large quantity handler of universal waste shall manage universal
waste batteries in a way 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;
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
350
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 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 landfills 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 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, 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 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;
351
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;
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 or local solid (nonhazardous) waste regulations.
352
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 landfills apply to the waste. Consult the ordinances of
relevant units of local government to determine whether local requirements
apply.
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)"; or "Waste Battery(ies)"; or "Used Battery(ies)";
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)" or "Waste-Pesticide(s)";
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 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 is
not feasible, another label prescribed or designated by the pesticide collection
program; and
2)
The words "Universal Waste-Pesticide(s)" or "Waste-Pesticide(s)"; and
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)", or "Waste Mercury Thermostat(s)", or
"Used Mercury Thermostat(s)".
Section 733.135 Accumulation Time Limits
a)
A large quantity handler of universal waste may accumulate universal waste for no longer than
one year from the date the universal waste is generated or received from another handler,
unless the requirements of subsection (b) below are met.
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b)
A large quantity handler of universal waste may accumulate universal waste for longer than one
year from the date the universal waste is generated or received from another handler if such
activity is solely for the purpose of accumulation of such quantities of universal waste as
necessary to facilitate proper recovery, treatment, or disposal. However, the handler bears the
burden of proving that such activity was solely for the purpose of accumulation of such
quantities of universal waste as necessary to facilitate proper recovery, treatment, or disposal.
c)
A large quantity handler of universal waste shall be able to demonstrate the length of time that
the universal waste has been accumulated from the date it becomes a waste or is received. The
handler may make this demonstration in any of the following ways:
1)
Placing the universal waste in a container and marking or labeling the container with
the earliest date that any universal waste in the container became a waste or was
received;
2)
Marking or labeling the individual item of universal waste (e.g., each battery or
thermostat) with the date it became a waste or was received;
3)
Maintaining an on-site inventory system that identifies the date the universal waste
being accumulated became a waste or was received;
4)
Maintaining an on-site inventory system that identifies the earliest date that any
universal waste in a group of universal waste items or a group of containers of
universal waste became a waste or was received;
5)
Placing the universal waste in a specific accumulation area and identifying the earliest
date that any universal waste in the area became a waste or was received; or
6)
Any other method that clearly demonstrates the length of time that the universal waste
has been accumulated from the date it became a waste or was received.
Section 733.136 Employee Training
A large quantity handler of universal waste shall ensure that all employees are thoroughly familiar with proper
waste handling and emergency procedures, relative to their responsibilities during normal facility operations and
emergencies.
Section 733.137 Response to Releases
a)
A large quantity handler of universal waste shall immediately contain all releases of universal
waste and other residues from universal waste.
b)
A large quantity handler of universal waste shall determine whether any material resulting from
the release is hazardous waste, and if so, shall manage the hazardous waste 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 material resulting from the release, and is
subject to 35 Ill. Adm. Code 722.
Section 733.138 Off-Site Shipments
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a)
A large quantity handler of universal waste is prohibited from sending or taking universal waste
to a place other than another universal waste handler, a destination facility, or a foreign
destination.
b)
If a large quantity handler of universal waste self-transports universal waste off-site, the
handler becomes a universal waste transporter for those self-transportation activities and shall
comply with the transporter requirements of 733.Subpart D while transporting the universal
waste.
c)
If a universal waste being offered for off-site transportation meets the definition of hazardous
materials under 49 CFR 171 through 180, a large quantity handler of universal waste shall
package, label, mark and placard the shipment, and prepare the proper shipping papers in
accordance with the applicable USDOT regulations under 49 CFR 172 through 180;
d)
Prior to sending a shipment of universal waste to another universal waste handler, the
originating handler shall ensure that the receiving handler agrees to receive the shipment.
e)
If a large quantity handler of universal waste sends a shipment of universal waste to another
handler or to a destination facility and the shipment is rejected by the receiving handler or
destination facility, the originating handler shall either:
1)
Receive the waste back when notified that the shipment has been rejected, or
2)
Agree with the receiving handler on a destination facility to which the shipment will
be sent.
f)
A large quantity handler of universal waste may reject a shipment containing universal waste,
or a portion of a shipment containing universal waste that it has received from another handler.
If a handler rejects a shipment or a portion of a shipment, it shall contact the originating
handler to notify the originating handler of the rejection and to discuss reshipment of the load.
The handler shall perform either of the following actions:
1)
Send the shipment back to the originating handler, or
2)
If agreed to by both the originating and receiving handler, send the shipment to a
destination facility.
g)
If a large quantity handler of universal waste receives a shipment containing hazardous waste
that is not a universal waste, the handler shall immediately notify the Agency (Bureau of Land,
Illinois EPA, 1001 North Grand Avenue, P.O. Box 19276, Springfield, Illinois 62794-9276
(telephone: 217-782-6761) of the illegal shipment, and provide the name, address, and phone
number of the originating shipper. The Agency will provide instructions for managing the
hazardous waste.
h)
If a large quantity handler of universal waste receives a shipment of non-hazardous, non-
universal waste, the handler may manage the waste in any way that is in compliance with
applicable federal, 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 landfills apply to the
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waste. Consult the ordinances of relevant units of local government to determine whether local
requirements apply.
Section 733.139 Tracking Universal Waste Shipments
a)
Receipt of shipments. A large quantity handler of universal waste shall keep a record of each
shipment of universal waste received at the facility. The record may take the form of a log,
invoice, manifest, bill of lading, or other shipping document. The record for each shipment of
universal waste received must include the following information:
1)
The name and address of the originating universal waste handler or foreign shipper
from whom the universal waste was sent;
2)
The quantity of each type of universal waste received (e.g., batteries, pesticides,
thermostats);
3)
The date of receipt of the shipment of universal waste.
b)
Shipments off-site. A large quantity handler of universal waste shall keep a record of each
shipment of universal waste sent from the handler to other facilities. The record may take the
form of a log, invoice, manifest, bill of lading or other shipping document. The record for
each shipment of universal waste sent must include the following information:
1)
The name and address of the universal waste handler, destination facility, or foreign
destination to whom the universal waste was sent;
2)
The quantity of each type of universal waste sent (e.g., batteries, pesticides,
thermostats);
3)
The date the shipment of universal waste left the facility.
c)
Record retention.
1)
A large quantity handler of universal waste shall retain the records described in
subsection (a) above for at least three years from the date of receipt of a shipment of
universal waste.
2)
A large quantity handler of universal waste shall retain the records described in
subsection (b) above for at least three years from the date a shipment of universal
waste left the facility.
Section 733.140 Exports
A large quantity handler of universal waste that sends universal waste to a foreign destination shall:
a)
Comply with the requirements applicable to a primary exporter in 35 Ill. Adm. Code 722.153;
722.156(a)(1) through (a)(4), (a)(6), and (b); and 722.157;
b)
Export such universal waste only upon consent of the receiving country and in conformance
with the USEPA Acknowledgement of Consent as defined in 35 Ill. Adm. Code 722.Subpart E;
and
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c)
Provide a copy of the USEPA Acknowledgement of Consent for the shipment to the transporter
transporting the shipment for export.
SUBPART D: STANDARDS FOR UNIVERSAL WASTE TRANSPORTERS
Section 733.150 Applicability
This Subpart applies to universal waste transporters (as defined in Section 733.106).
Section 733.151 Prohibitions
A universal waste transporter is prohibited from the following:
a) Disposing of universal waste; and
b) Diluting or treating universal waste, except by responding to releases as provided in Section
733.154.
Section 733.152 Waste Management
a)
A universal waste transporter shall comply with all applicable USDOT regulations in 49 CFR
171 through 180 for transport of any universal waste that meets the definition of hazardous
material in 49 CFR 171.8, incorporated by reference in Section 720.111. For purposes of the
USDOT regulations, a material is considered a hazardous waste if it is subject to the Hazardous
Waste Manifest Requirements of 35 Ill. Adm. Code 722. Because universal waste does not
require a hazardous waste manifest, it is not considered hazardous waste under the USDOT
regulations.
b)
Some universal waste materials are regulated by the USDOT as hazardous materials because
they meet the criteria for one or more hazard classes specified in 49 CFR 173.2, incorporated
by reference in Section 720.111. As universal waste shipments do not require a manifest under
35 Ill. Adm. Code 722, they may not be described by the USDOT proper shipping name
"hazardous waste, (l) or (s), n.o.s.", nor may the hazardous material's proper shipping name be
modified by adding the word "waste".
Section 733.153 Accumulation Time Limits
a)
A universal waste transporter may only store the universal waste at a universal waste transfer
facility for ten days or less.
b)
If a universal waste transporter stores universal waste for more than ten days, the transporter
becomes a universal waste handler and shall comply with the applicable requirements of
733.Subpart B or C while storing the universal waste.
Section 733.154 Response to Releases
a)
A universal waste transporter shall immediately contain all releases of universal waste and
other residues from universal wastes.
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b)
A universal waste transporter shall determine whether any material resulting from the release is
hazardous waste, and if so, it is subject to all applicable requirements of 35 Ill. Adm. Code 702
through 705, 720 through 726, and 728. If the waste is determined to be a hazardous waste,
the transporter is subject to 35 Ill. Adm. Code 722.
Section 733.155 Off-site Shipments
a)
A universal waste transporter is prohibited from transporting the universal waste to a place
other than a universal waste handler, a destination facility, or a foreign destination.
b)
If the universal waste being shipped off-site meets USDOT's definition of hazardous materials
under 49 CFR 171.8, incorporated by reference in Section 720.111, the shipment must be
properly described on a shipping paper in accordance with the applicable USDOT regulations
under 49 CFR part 172.
Section 733.156 Exports
A universal waste transporter transporting a shipment of universal waste to a foreign destination may not accept
a shipment if the transporter knows the shipment does not conform to the USEPA Acknowledgment of Consent.
In addition the transporter shall ensure the following:
a)
A copy of the USEPA Acknowledgment of Consent accompanies the shipment; and
b)
The shipment is delivered to the facility designated by the person initiating the shipment.
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) is subject to all
applicable requirements of 35 Ill. Adm. Code 702 through 705, 720 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).
Section 733.161 Off-Site Shipments
a)
The owner or operator of a destination facility is prohibited from sending or taking universal
waste to a place other than a universal waste handler, another destination facility, or a foreign
destination.
b)
The owner or operator of a destination facility may reject a shipment containing universal
waste, or a portion of a shipment containing universal waste. If the owner or operator of the
destination facility rejects a shipment or a portion of a shipment, it shall contact the shipper to
notify the shipper of the rejection and to discuss reshipment of the load. The owner or operator
of the destination facility shall perform either of the following actions:
1)
Send the shipment back to the original shipper, or
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2)
If agreed to by both the shipper and the owner or operator of the destination facility,
send the shipment to another destination facility.
c)
If the owner or operator of a destination facility receives a shipment containing hazardous
waste that is not a universal waste, the owner or operator of the destination facility shall
immediately notify the Agency (Bureau of Land, Illinois EPA, 1001 North Grand Avenue,
P.O. Box 19276, Springfield, Illinois 62794-9276 (telephone: 217-782-6761) of the illegal
shipment, and provide the name, address, and phone number of the shipper. The Agency will
provide instructions for managing the hazardous waste.
d)
If the owner or operator of a destination facility receives a shipment of non-hazardous, non-
universal waste, the owner or operator may manage the waste in any way that is in compliance
with applicable federal or state 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 landfills apply to the
waste. Consult the ordinances of relevant units of local government to determine whether local
requirements apply.
Section 733.162 Tracking Universal Waste Shipments
a)
The owner or operator of a destination facility shall keep a record of each shipment of
universal waste received at the facility. The record may take the form of a log, invoice,
manifest, bill of lading, or other shipping document. The record for each shipment of
universal waste received must include the following information:
1)
The name and address of the universal waste handler, destination facility, or foreign
shipper from whom the universal waste was sent;
2)
The quantity of each type of universal waste received (e.g., batteries, pesticides,
thermostats);
3)
The date of receipt of the shipment of universal waste.
b)
The owner or operator of a destination facility shall retain the records described in subsection
(a) above for at least three years from the date of receipt of a shipment of universal waste.
SUBPART F: IMPORT REQUIREMENTS
Section 733.170 Imports
Persons managing universal waste that is imported from a foreign country into the United States are subject to
the applicable requirements of this Part immediately after the waste enters the United States, as follows:
a)
A universal waste transporter is subject to the universal waste transporter requirements of
733.Subpart D.
b)
A universal waste handler is subject to the small or large quantity handler of universal waste
requirements of 733.Subpart B or C, as applicable.
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c)
An owner or operator of a destination facility is subject to the destination facility requirements
of 733.Subpart E.
SUBPART G: PETITIONS TO INCLUDE OTHER WASTES
Section 733.180 General
a)
Any person seeking to add a hazardous waste or a category of hazardous waste to this Part may
petition for a regulatory amendment as follows:
1)
If USEPA has already added the waste or category of waste to 40 CFR 273: by
identical-in-substance rulemaking, under Section 22.4(a) of the Act, 35 Ill. Adm.
Code 101 and 102, 35 Ill. Adm. Code 720.120; or
2)
If USEPA has not added the waste or catogory of waste to 40 CFR 273: by general
rulemaking, under Sections 22.4(b) and 27 of the Act, 35 Ill. Adm. Code 101 and
102, this Subpart, and 35 Ill. Adm. Code 720.120 and 720.123.
BOARD NOTE: The Board cannot add a hazardous waste or category of hazardous
waste to this Part by general rulemaking until USEPA either authorizes the Illinois
universal waste regulations or otherwise authorizes the Board to add new categories of
universal waste. The Board may, however, add a waste or category of waste by
identical-in-substance rulemaking.
b)
Petitions for identical-in-substance rulemaking.
1)
Any petition for identical-in-substance rulemaking under subsection (a)(1) above must
include a copy of the the Federal Register notice(s) of adopted amendments in which
USEPA promulgated the addition(s) to 40 CFR 273. The Board will evaluate any
petition for identical-in-substance rulemaking based on the Federal Register notice(s).
2)
If the petitioner desires expedited Board consideration of the proposed amendents to
this Part (i.e., adoption within one year of the date of the Federal Register notice), it
must explicitly request expedited consideration and set forth the arguments in favor of
such consideration.
c)
Petitions for general rulemaking.
1)
To be successful using the general rulemaking procedure under subsection (a)(2)
above, the petitioner must demonstrate to the satisfaction of the Board that each of the
following would be true of regulation under the universal waste regulations of this
Part:
A)
It would be appropriate for the waste or category of waste;
B)
It would improve management practices for the waste or category of waste;
and
C)
It would improve implementation of the hazardous waste program.
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2)
The petition must include the information required by 35 Ill. Adm. Code 720.120(b).
The petition should also address as many of the factors listed in Section 733.181 as are
appropriate for the waste or waste category addressed in the petition.
3)
The Board will evaluate petitions for general rulemaking and grant or deny the
requested relief using the factors listed in Section 733.181. The decision will be based
on the weight of evidence showing that regulation under this Part would fulfill the
requirements of subsection (c)(1) above.
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 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,
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 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;
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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.