ILLINOIS POLLUTION CONTROL BOARD
December 2, 1999
IN THE MATTER OF:
)
)
RCRA SUBTITLE C UPDATE, USEPA
)
R00-5
AMENDMENTS (January 1, 1999, through
)
(Identical-in-Substance
June 30, 1999)
)
Rulemaking - Land)
Adopted Rule. Final Order.
OPINION OF THE BOARD (by E.Z. Kezelis):
Under Sections 7.2 and 22.4(a) of the Environmental Protection Act (Act) (415 ILCS 5/7.2
and 22.4(a) (1998)), the Board today adopts amendments to the Illinois regulations that are “identical in
substance” to hazardous waste regulations that the United States Environmental Protection Agency
(USEPA) adopted to implement Subtitle C of the federal Resource Conservation and Recovery Act of
1976 (RCRA Subtitle C) (42 U.S.C. §§ 6921
et seq
. (1998)). The nominal timeframe of this docket
includes federal RCRA Subtitle C amendments that USEPA adopted in the period January 1, 1999,
through June 30, 1999.
Sections 7.2 and 22.4(a) provide for quick adoption of regulations that are identical in
substance to federal regulations that USEPA adopts to implement Sections 3001 through 3005 of
RCRA (42 U.S.C. §§ 6921-6925 (1998)). Section 22.4(a) also provides that Title VII of the Act and
Section 5 of the Administrative Procedure Act (APA) (5 ILCS 100/5-35 and 5-40 (1998)) do not
apply to the Board’s adoption of identical-in-substance regulations. The federal RCRA Subtitle C
regulations are found at 40 C.F.R. 260 through 266, 268, 270, 271, 273, and 279.
This opinion supports the order that the Board also adopts today. The Board will wait 30 days
for USEPA to review the amendments, as provided in the agreement between USEPA and the State of
Illinois relating to federal authorization of the State program, in order to allow USEPA an additional
opportunity to review the amendments before they become effective. We will then file the amendments
with the Secretary of State and submit Notices of Adopted Amendments for publication in the
Illinois
Register
.
FEDERAL ACTIONS CONSIDERED IN THIS RULEMAKING
The following briefly summarizes the federal actions considered in this rulemaking.
2
Docket R00-5: January 1, 1999, through June 30, 1999, RCRA Subtitle C
Amendments
USEPA amended the federal RCRA Subtitle C regulations on three occasions during the period
January 1, 1999, through June 30, 1999. Each is summarized below:
64 Fed. Reg. 3382 (January 21, 1999)
USEPA adopted clarifying and corrective amendments to the 40 C.F.R. 264, Subpart CC and
265, Subpart CC organic material emission rules (Subpart CC rules) applicable to hazardous
waste tanks, containers, and surface impoundments.
64 Fed. Reg. 6806 (February 11, 1999)
USEPA adopted a temporary exemption of certain petroleum refining wastes from the definition
of hazardous waste.
64 Fed. Reg. 25408 (May 11, 1999)
USEPA adopted corrections and clarifications to several of its Phase IV rulemaking actions: its
May 12, 1997 (62 Fed. Reg. 25998) and May 26, 1998 (63 Fed. Reg. 28556) Phase IV
rules; its August 31, 1998 (63 Fed. Reg. 46332) administrative stay of aspects of its May 26,
1998 rule; its September 4, 1998 (63 Fed. Reg. 47409) emergency amendment of the
carbamate rule; and the September 24, 1998 (63 Fed. Reg. 51254) amendments relating to
spent potliners.
The Board has already acted with regard to two of the federal actions that occurred in the current
update period. See RCRA Update, USEPA Regulations (July 1, 1998, through December 31, 1998)
(June 17, 1999), R99-15. No further action is necessary as to one federal action, and only partial
action is required to complete the Board’s actions as to the other. The listing of the two federal actions
on which the Board has already acted follows, together with a brief explanation as to why no action or
only partial action is necessary:
64 Fed Reg. 6806 (February 11, 1999)
The Board fully incorporated the temporary exemption of certain petroleum refining wastes into
update docket R99-15, so no further action will be necessary.
64 Fed. Reg. 25408 (May 11, 1999)
The Board included most, but not all, of the USEPA corrections and clarifications to its Phase
IV rulemaking actions. The Board adopted all of the federal amendments except those to 40
C.F.R. 262, since corresponding 35 Ill. Adm. Code 722 was not included in the proposal for
public comment in RCRA Update, USEPA Regulations (July 1, 1998, through December 31,
1998) (April 23, 1999), R99-15. The Board must complete the amendments in this docket,
R00-5.
3
Later RCRA Subtitle C (Hazardous Waste) Amendments of Interest
The Board engages in ongoing monitoring of federal actions. As of the date of this opinion and
accompanying order, we have not identified any USEPA actions since June 30, 1999, that further
amend the RCRA Subtitle C hazardous waste rules involved in this proceeding. When the Board
observes an action outside the nominal timeframe of a docket that would require expedited
consideration in the pending docket, the Board will expedite consideration of those amendments.
Federal actions that could warrant expedited consideration include those that directly affect the
amendments involved in this docket, those for which compelling reasons would warrant consideration as
soon as possible, and those for which the Board has received a request for expedited consideration. If
the Board identifies any federal actions that fulfill these criteria prior to final action on the present
amendments, it may include those amendments in the present update docket R00-5. In this instance, no
later amendments affect the subject matter involved in this proceeding.
Unrelated Federal Actions Having an Ancillary Impact on the Illinois RCRA Subtitle C
Regulations
In addition to the amendments to the federal RCRA Subtitle C regulations, other, unrelated
federal amendments might have an effect on the corresponding Illinois rules. Most notably, 35 Ill. Adm.
Code 720.111 includes several incorporations of federal regulations by reference, and USEPA has
amended 40 C.F.R. 136, which is included among the incorporated references. The federal
amendments to 40 C.F.R. 136 are as follows, along with a description of the Board action each
requires, if any:
64 Fed. Reg. 4975 (February 2, 1999)
USEPA amended the 40 C.F.R. 136 methods for whole effluent toxicity testing for the
purposes of compliance with the Clean Water Act.
64 Fed. Reg. 26315 (May 14, 1999)
USEPA approved the use of a new method for analyzing oil and grease for the purposes of
compliance with the Clean Water Act and RCRA regulations.
64 Fed. Reg. 30417 (June 8, 1999)
USEPA amended its guidance on the analysis of mercury in water for the purposes of
compliance with the water quality requirements of the Clean Water Act.
Summary Listing of the Federal Actions Forming the Basis of the Board’s Actions in
this Docket
Based on the foregoing, the federal actions that form the basis for Board action in this update
docket are as follows, in chronological order:
4
64 Fed. Reg. 3381 (January 21, 1999)
Clarifying and corrective amendments to the Subpart
CC organic material emission rules applicable to
hazardous waste tanks, containers, and surface
impoundments.
64 Fed. Reg. 4975 (February 2, 1999)
40 C.F.R. 136 amendment.
64 Fed. Reg. 25408 (May 11, 1999)
Corrections and clarifications to the Phase IV
rulemaking actions. (Completion of action taken in
prior update docket R99-15.)
64 Fed. Reg. 26315 (May 14, 1999)
40 C.F.R. 136 amendment.
64 Fed. Reg. 30417 (June 8, 1999)
40 C.F.R. 136 amendment.
PUBLIC COMMENTS
The Board adopted a proposal for public comment in this matter by order dated September 23,
1999. “Notices of Proposed Amendments” appeared in the October 8, 1999 issue of the
Illinois
Register
, at 23 Ill. Reg. 12087 (Part 720), 12185 (Part 722), 12195 (Part 724), and 12100 (Part
725). The Board accepted public comments on the proposal for a 45-day period following publication
in the
Illinois Register.
The comment period expired on November 22, 1999.
The Board received two public comments during the public comment period. Those comments
are as follows:
PC 1
USEPA Region V, dated November 23, 1999, letter from Richard T. Traub, Chief,
State Programs and Authorization Section (received November 24, 1999).
PC 2
Illinois Environmental Protection Agency (the IEPA), dated November 17, 1999,
Response to Public Comment Period from Susan J. Schroeder, Associate Counsel,
Division of Legal Counsel (received November 24, 1999).
In PC 1, USEPA stated that it has no comments on the “RCRA Cluster VIII” requirements that
appeared in the
Federal Register
during the period January 1, 1999, through June 30, 1999. In PC 2,
the IEPA voiced its concern over two narrow aspects of the proposed amendments. The IEPA
comments are discussed below (at pages seven through nine) in the appropriate segments of the
substantive discussion of the amendments.
In addition to the public comments, the Board also received a series of four documents from the
Joint Committee on Administrative Rules (JCAR) (one for each Part involved in this proceeding) entitled
“Identical First Notice Line Numbered Version.” Each of these documents contain those changes that
JCAR made prior to the October 8, 1999 publication of these amendments in the
Illinois Register
.
The changes accepted by the Board are listed in the table entitled, “Revisions to the Text of the
Proposed Amendments in Final Adoption,” that begins at page 14 of this opinion. The changes not
accepted by the Board, together with a brief explanation, appear in the table entitled, “Requested
5
Revisions to the Text of the Proposed Amendments Not Made in Final Adoption,” beginning at page
14.
The Board adopts these amendments, having first made the changes necessitated by public
comment. The Board will delay filing these adopted rules with the Secretary of State for 30 days after
the date of this opinion and order, or until after January 1, 1999, in order to allow additional time for
USEPA to review the adopted amendments before they are filed and become effective. The complete
text of the adopted amendments appears in a separate order adopted this day.
DISCUSSION
The following discussion begins with a description of the types of deviations the Board makes
from the literal text of federal regulations in adopting identical-in-substance rules. It is followed by a
discussion of the amendments and actions undertaken in direct response to the federal actions involved
in this proceeding. This first series of discussions is organized by federal subject matter, generally
appearing in chronological order of the significant
Federal Register
notices involved. Finally, this
discussion closes with a description of the amendments and actions that are not directly derived from the
federal actions.
General Revisions and Deviations from the Federal Text
In incorporating the federal rules into the Illinois system, some minimal deviation from the federal
text is unavoidable. This deviation arises primarily through differences between the federal and state
regulatory structure and systems. Some deviation also arises through errors in and problems with the
federal text itself. The Board conforms the federal text to the Illinois rules and regulatory scheme and
corrects errors that we see in the text as we engage in these routine update rulemakings.
In addition to the amendments derived from federal amendments, the Board often finds it
necessary to alter the text of various passages of the existing rules as provisions are opened for update
in response to USEPA actions. This involves correcting deficiencies, clarifying provisions, and making
other changes that are necessary to establish a clear set of rules that closely parallel the corresponding
federal requirements within the codification scheme of the Illinois Administrative Code.
The Board updates the citations to the
Code of Federal Regulations
to the most recent version
available. As of the date of this opinion, the most recent version of the
Code of Federal Regulations
available to the Board is the July 1, 1998 version. Thus, we have updated all citations to the 1998
version, adding references to later amendments using their appropriate
Federal Register
citation, where
necessary.
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, spelling, and cross-reference format throughout the opened
text. We changed “who” to “that” and “he” or “she” to “it,” where the person to which the regulation
6
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.
In addition, 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 a duty 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.”
JCAR has requested that the Board refer to the USEPA in the same manner 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 has
decided to refer to the USEPA as “USEPA.” We will continue this conversion in future rulemakings as
additional sections otherwise become open to amendment. We will further convert “EPA” used in
federal text to “USEPA,” where USEPA is clearly intended.
The Board has assembled tables to aid location of those alterations and to briefly outline their
intended purpose. The tables set forth the miscellaneous deviations from the federal text and
corrections to the pre-amended base text of the rules in detail. The tables are set forth and explained
beginning at page 10. There is no further discussion of most of the deviations and revisions elsewhere in
this opinion.
One alteration of the base regulatory text and one to the verbatim text of the federal
amendments warrant specific discussions. The alteration of the base text was the addition of “USDOT”
as a defined term, in order to avoid the use of explanatory parentheticals at multiple locations in the text.
The new definition of “USDOT” appears at Section 724.981, with the rest of the definitions pertaining
to the “Subpart CC” rules. The Board has replaced “U.S. Department of Transportation (USDOT)”
with the abbreviation “USDOT” at Sections 724.986(c)(1)(A), (d)(1)(A), and (f) and
725.987(c)(1)(A), (d)(1)(A), and (f). The discussion of the alteration of the federal text is set forth in
the topical discussion of the “Subpart CC” rule amendments that immediately follows.
Discussion of Particular Federal Actions
Subpart CC Corrections—Section 722.134 and Subparts CC to Parts 724 and 725
USEPA adopted amendments, corrections, and clarifications to its Subpart CC rules on
January 21, 1999 (64 Fed. Reg. 3382). The rules at 40 C.F.R. 264, Subpart CC and 265, Subpart
CC set forth requirements for the control of organic material emissions for tanks, containers, and surface
impoundments that contain hazardous waste. USEPA initially adopted the Subpart CC rules on
December 6, 1994 (59 Fed. Reg. 62896). USEPA subsequently delayed the effective date four times
7
to further consider the Subpart CC rules and corrections and clarifications to them: on May 19, 1995
(60 Fed. Reg. 26828); November 13, 1995 (60 Fed. Reg. 56952); June 5, 1996 (61 Fed. Reg.
28508); and November 25, 1996 (61 Fed. Reg. 59931). Ultimate compliance with the Subpart CC
rules was delayed by these actions until December 6, 1996. During that time, USEPA published
corrections and amendments to the Subpart CC rules on February 9, 1996 (61 Fed. Reg. 4903);
November 25, 1996 (61 Fed. Reg. 59932); and December 8, 1997 (62 Fed. Reg. 64636). In these
Subpart CC actions, USEPA also corrected , Subparts AA and BB of 40 C.F.R. 264. Subparts AA
and BB regulate organic material emissions from process vents and equipment leaks. As in those earlier
actions, this January 21, 1999 action also involves corrections to rules other than the Subpart CC rules
of 40 C.F.R. 264 and 265; specifically, it involves amendments to 40 C.F.R. 262.34 and 264, Subpart
AA.
The Board has incorporated the federal amendments into Section 722.134 and the appropriate
segments of Subparts AA and CC of Part 724 and Subpart CC of Part 725. We have done so with
only minor deviations from the text of the federal amendments. Persons interested in the substance of
the underlying federal action should refer to the notice that appeared in the January 21, 1999 issue of
the
Federal Register
. The tables that begin on page 8 of this opinion outline the minor deviations that
the Board has made in adapting the text of the federal amendments.
Two deviations from the literal text of the federal amendments warrant specific discussion.
First, the Board has altered “either or” from 40 C.F.R. 264.1084(h)(3) and 265.1085(h)(3) to read
“either of” in corresponding Sections 724.984(h)(3) and 725.985(h)(3). Second, the Board has
deleted the “as specified in paragraph (h)(3)(i) or (h)(3)(ii) of this section” language from these same
two parallel federal provisions. As a substitution for this language, the Board has added the word “two”
in between the words “following” and “conditions.” The Board believes the revised language is more
straightforward.
Also worth noting is that the IEPA addressed the amendment of the Section 724.931 definition
of “open-ended valve or line” to replace the phrase “process fluid” with “hazardous waste.” The IEPA
expressed a concern that this alteration of the regulatory text makes it ambiguous whether the definition
would apply to valves handling reclaimed liquid from a recycling unit. The IEPA requested that the
Board not change the definition or, alternatively, that we clarify whether the definition should apply to
reclaimed product.
The Board cannot alter the language of the proposed amendments to the definition of “open-
ended valve or line.” The proposed language reflects the language dictated by USEPA. Examination of
USEPA’s preamble discussion of its amendments to the definition indicate that it altered the definition
because “the subpart BB rules only apply to equipment (
e.g.
, and open-ended valve or line) that
contains or contacts hazardous waste . . . .” Thus, USEPA intended that the Subpart BB rules and the
definition of “open-ended valve or line” apply only to equipment used to manage “hazardous waste.”
The Board cannot alter the federal language or clarify the rules in any way that would change the
meaning intended by USEPA.
8
Phase IV LDR Corrections and Clarifications—Section 722.134
On May 11, 1999 (64 Fed. Reg. 25408), USEPA adopted corrective and clarifying
amendments to five of its Phase IV LDR rulemaking actions, including those of May 12, 1997 (62 Fed.
Reg. 25998); May 26, 1998 (63 Fed. Reg. 28556); August 31, 1998 (63 Fed. Reg. 46332);
September 4, 1998 (63 Fed. Reg. 47409); and September 24, 1998 (63 Fed. Reg. 51254). The
Board adopted most, but not all, of the May 11, 1999 federal amendments in the prior RCRA Subtitle
C update docket RCRA Update, USEPA Regulations (July 1, 1998, through December 31, 1998)
(June 17, 1999), R99-15. The Board adopted all of the federal amendments except those to 40
C.F.R. 262. Corresponding 35 Ill. Adm. Code 722 was not included in the proposal for public
comment, so the Board could not amend that Part.
The Board completes the May 11, 1999 federal amendments in this docket, R00-5, by making
the necessary amendments to Section 722.134(d). The amendments are limited to the correction of
cross-references. The Board has incorporated the federal amendments without deviation from the
federal text. Persons interested in the details of the federal amendments should consult the May 11,
1999
Federal Register
notice. Those interested in the major segments of the federal amendments
incorporated into the Illinois hazardous waste rules in the prior update docket should refer to the opinion
and order in RCRA Update, USEPA Regulations (July 1, 1998, through December 31, 1998)
(June 17, 1999), R99-15.
The Board requested public comment on our completion of the May 11, 1999 federal
amendments to the Phase IV LDR rules. The IEPA commented on one narrow aspect of the federal
Phase IV LDR amendments in response to our request. Regrettably, the Board cannot alter the text of
the rules in response to the IEPA comment.
The IEPA did not question the text of Section 722.134. Instead it noted a couple of deviations
in the text of the definition of “soil” in Section 728.102 from the corresponding federal definition of 40
C.F.R. 268.2(c). The IEPA suggested that the Board change the definition to exactly reflect the federal
text.
The Board agrees with the IEPA that in the Section 728.102 definition of “soil” we should
change “debris” to “soil” and “hazardous debris” to “contaminated soil” in the final sentence, as
amended by USEPA on May 11, 1999, at 64 Fed. Reg. 25414. However, the Board did not propose
to amend Part 728 in our October 8, 1999 Notice of Proposed Amendments. Since Part 728 is not
open in this proceeding, we cannot proceed to make the changes in Section 728.102 at this time. We
will complete the IEPA-suggested revisions in the next routine update docket.
Incorporation of 40 C.F.R. 136 by Reference—Section 720.111
USEPA adopted multiple amendments to 40 C.F.R. 136, which are the Clean Water Act
analytical procedures, on February 2, 1999 (64 Fed. Reg. 4975); May 14, 1999 (64 Fed. Reg.
26315); and June 8, 1999 (64 Fed. Reg. 30417). The methods affected relate to whole effluent
9
toxicity testing, oil and grease testing, and the measurement of mercury in water. The Board has
incorporated 40 C.F.R. 136 by reference in Section 720.111 of the hazardous waste rules. Only one
set of the testing methods amendments purports to affect the hazardous waste system; that is the
May 14, 1999 oil and grease testing methods amendment. Persons interested in the details of the
federal amendments should refer to the appropriate
Federal Register
notice cited above.
The Board has incorporated the federal amendments without deviation. We have updated the
version of 40 C.F.R. 136 incorporated by reference by adding the three cited
Federal Register
notices
to the incorporation. The Board has included all three notices without regard to whether the individual
methods updated or added by USEPA are actually used to achieve or demonstrate compliance under
the RCRA Subtitle C regulatory scheme.
The Board requested public comment on the update to the version of 40 C.F.R. 136
incorporated by reference for the purposes of the Illinois RCRA Subtitle C hazardous waste regulatory
program. We received no comments on this aspect of the proposed amendments in response to our
request, and have adopted the amendments as proposed.
Discussion of Miscellaneous Other Amendments not Federally Driven
The tables beginning below list numerous corrections and amendments that are not based on
current federal amendments. The first table (beginning immediately below) includes deviations made in
the September 23, 1999 proposal for public comment from the verbatim text of the federal
amendments. The second table (beginning below on page 12 of this opinion) contains corrections and
clarifications that the Board made in the base text involved in this proposal. The amendments listed in
this second table are not directly derived from the current federal amendments. Some of the entries in
these tables are discussed further in appropriate segments of the general discussion beginning at page
five of this opinion.
The third table (beginning below on page 14 of this opinion) contains changes made, based on
public comments received, to the text of the September 23, 1999 proposal for public comment. The
third table indicates the affected provision of the rules, the source of the revision, and the nature of the
revision. The fourth table (beginning below on page 14 of this opinion) contains those suggested
changes that the Board has not made to the text. The fourth table indicates the affected provision, the
source and nature of the suggestion for change, and the reasons the Board chose not to make the
change.
Table 1:
Deviations from the Text of the Federal Amendments
Illinois Section
40 C.F.R. Section
Revision(s)
724.931 “sampling
connection”
264.1031
Used parentheses on defined term; changed
“used” to “that is used” (twice)
10
724.983(a)(1)(A)
264.1083(a)(1)(i)
Changed to active voice, using “an owner or
operator shall make . . .” (twice); broke run-on
sentence into two sentences; added a comma
after “thereafter”; changed ending punctuation to
a period; removed ending conjunction “and”
724.983(a)(1)(B)
264.1083(a)(1)(ii)
Completed sentence, adding “an owner or
operator shall”
724.983(b)(1)(A)
264.1083(b)(1)(i)
Changed to active voice, using “an owner or
operator shall make . . .” (twice); broke run-on
sentence into two sentences; added a comma
after “thereafter”; changed ending punctuation to
a period; removed ending conjunction “and”
724.983(b)(1)(B)
264.1083(b)(1)(ii)
Completed sentence, adding “an owner or
operator shall”; changed “a level such that” to
“such a level that”
724.984(h)(3)
264.1084(h)(3)
Changed “either or the following conditions as
specified . . . of this section” to “either of the
following two conditions”; changed ending
punctuation to a colon
724.984(h)(3)(A)
264.1084(h)(3)(i)
Completed sentence by adding “the tank does
not . . . system”; added the definite article “the”
before “opening”
724.984(h)(3)(B)
264.1084(h)(3)(ii)
Completed sentence by adding “the tank does
not . . . system”; added the definite article “the”
before “purging”
724.986(e)(6)
264.1086(e)(6)
Added the definite article “the” before
“transfer”; changed “in” to “into”; changed
“shall” to “must”; used “USEPA”; added “the
use of” (three times); added indefinite article “a”
before “submerged”
725.984(a)(1)(A)
265.1084(a)(1)(i)
Changed to active voice, using “an owner or
operator shall make . . .” (twice); broke run-on
sentence into two sentences; added a comma
after “thereafter”; changed ending punctuation to
a period; removed ending conjunction “and”
725.984(a)(1)(B)
265.1084(a)(1)(ii)
Completed sentence, adding “an owner or
operator shall”
725.984(a)(3)(B)(ii)
265.1084(a)(3)(ii)(B)
Changed “shall” to “must”
725.984(a)(3)(B)(iv)
265.1084(a)(3)(ii)(D)
Changed “shall” to “must”
725.984(a)(3)(C)
265.1084(a)(3)(iii)
Changed “which” to “that” for restrictive relative
clause; used “25° C” in place of “25 degrees
Centigrade”
11
725.984(b)(1)(A)
265.1084(b)(1)(i)
Changed to active voice, using “an owner or
operator shall make . . .” (twice); broke run-on
sentence into two sentences; added a comma
after “thereafter”; changed ending punctuation to
a period, removed ending conjunction “and”
725.984(b)(1)(B)
265.1084(b)(1)(ii)
Completed sentence, adding “an owner or
operator shall”; changed “a level such that” to
“such a level that”
725.984(b)(3)(B)(ii)
265.1084(b)(3)(ii)(B)
Changed “shall” to “must”
725.984(b)(3)(B)(iv)
265.1084(b)(3)(ii)(D)
Changed “shall” to “must”
725.984(b)(3)(C)
265.1084(b)(3)(iii)
Changed “which” to “that” for restrictive relative
clause; used “25° C” in place of “25 degrees
Centigrade”
725.985(h)(3)
265.1085(h)(3)
Changed “either or the following conditions as
specified . . . of this section” to “either of the
following two conditions”; changed ending
punctuation to a colon
725.985(h)(3)(A)
265.1085(h)(3)(i)
Completed sentence by adding “the tank does
not . . . system”; added the definite article “the”
before “opening”
725.985(h)(3)(B)
265.1085(h)(3)(ii)
Completed sentence by adding “the tank does
not . . . system”; added the definite article “the”
before “purging”
725.987(e)(6)
265.1087(e)(6)
Added the definite article “the” before
“transfer”; changed “in” to “into”; changed
“shall” to “must”; used “USEPA”; added “the
use of” (three times); added indefinite article “a”
before “submerged”
Table 2:
Board Amendments Not Federally-Derived
Section
Revision(s)
720. authority note
Added references to Sections 7.2 and 13 of the Act
720.111(a)
Deleted the reference to 35 Ill. Adm. Code 731, since that Part has its own
Section listing incorporations by reference
720.111(a) NTIS “Test
Methods . . .”
Deleted commas from reference version dates (five times)
720.111(a) U.S. DOD
“The Signature . . .”
Corrected spelling of “tally”
722. authority note
Added a reference to Section 7.2 of the Act
722.134(a)
Added “the following conditions are fulfilled”
12
722.134(a)(1)
Added “in or on one of the following”
722.134(a)(1)(A)
Added comma to offset a parenthetical; removed ending conjunction “or”
722.134(a)(1)(B)
Added comma to offset a parenthetical; removed ending conjunction “or”
722.134(a)(1)(C)
Added comma to offset a parenthetical
722.134(a)(1)(D)
Added comma to offset a parenthetical
722.134(c)(1)
Added “does the following”
722.134(c)(1)(A)
Added comma to offset the last element of a series; changed ending
punctuation to a semicolon
722.134(d)
Added “the following conditions are fulfilled”
722.134(f)
Added comma to offset a parenthetical
724. authority note
Added a reference to Section 7.2 of the Act
724.931
Changed “the Subpart” to “this Subpart”
724.931 “air stripping
operation”
Changed “is” to “means”
724.931 “equipment”
Removed unnecessary conjunction “or” from between intermediate members
of a series
724.931 “open-ended
valve or line”
Added indefinite article “a” before “pressure”; changed to singular “valve”;
changed “having” to “that has”
724.931 “USDOT”
Added defined term
724.931 “vented”
Added commas before “such as” to offset parentheticals (five times)
724.980(b)(5)
Added comma to offset the last element of a series
724.980(c)
Changed “shall” to “must”; changed “such” to “the”
724.983(a)(2)
Changed “shall” to “must”
724.983(b)(2)
Changed “shall” to “must”
724.984(b)(1)(C)
Changed to active voice, using “the owner or operator does not treat . . .”
724.984(c)(2)(B)
Changed “a manner such that” to “such a manner that”
724.984(c)(2)(C)(i)
Changed “such that” to “so that”
724.984(c)(3)(B)
Changed “which” to “that” for restrictive relative clause; changed “such that”
to “so that”
724.984(f)(1)(C)(viii)
Changed “which” to “that” for restrictive relative clause
724.984(g)(1)(B)
Changed “such that” to “so that”
724.984(h)(3)
Changed “closed system” to defined term “closed-vent system”; added
comma before “except” to offset a parenthetical
724.984(i)
Changed “must” to “shall”
724.986(c)(1)(A)
Changed “U.S. Department of Transportation (USDOT)” to “USDOT”
724.986(c)(1)(C)
Changed “such that” to “so that”
724.986(c)(3)(D)
Changed “which” to “that” for restrictive relative clause; changed “such that”
to “so that”
724.986(c)(5)
Deleted comma before “which” to clarify that what follows is a restrictive
relative clause
724.986(d)(1)(A)
Changed “U.S. Department of Transportation (USDOT)” to “USDOT”
13
724.986(d)(3)(D)
Changed “which” to “that” for restrictive relative clause; changed “such that”
to “so that”
724.986(f)
Changed “U.S. Department of Transportation (USDOT)” to “USDOT”
725. authority note
Added a reference to Section 7.2 of the Act
725.984(a)(3)(B)
Changed “a manner such that” to “such a manner that”
725.984(a)(3)(B)(iii)
Changed “such that” to “so that”
725.984(a)(4)(C)
Changed “which” to “that” for restrictive relative clause
725.984(b)(3)(B)
Changed “a manner such that” to “such a manner that”
725.984(b)(3)(B)(iii)
Changed “such that” to “so that”
725.984(b)(3)(C)
Changed “shall” to “must”
725.984(b)(3)(E)
Changed “shall” to “must”
725.984(c)(3)(A)
Changed “such that” to “so that”
725.985(c)(2)(B)
Changed “a manner such that” to “such a manner that”
725.985(c)(2)(C)(i)
Changed “such that” to “so that”
725.985(c)(3)(B)
Changed “which” to “that” for restrictive relative clause; changed “such that”
to “so that”
725.985(f)(1)(B)(i)
Added parenthetical English units “(24 inches)”
725.985(f)(1)(C)(viii)
Changed “which” to “that” for restrictive relative clause
725.985(g)(1)(B)
Changed “such that” to “so that”
725.985(h)(1)
Changed “shall” to “must”
725.985(h)(3)
Changed “closed system” to defined term “closed-vent system”; added
comma before “except” to offset a parenthetical
725.985(k)(1)
Changed “shall” to “must”
725.987(c)(1)(A)
Changed “U.S. Department of Transportation (USDOT)” to “USDOT”
725.987(c)(1)(C)
Changed “such that” to “so that”
725.987(c)(3)(D)
Changed “which” to “that” for restrictive relative clause; changed “such that”
to “so that”
725.987(d)(1)(A)
Changed “U.S. Department of Transportation (USDOT)” to “USDOT”
725.987(d)(3)
Added comma before “except” to offset a parenthetical
725.987(d)(3)(D)
Changed “which” to “that” for restrictive relative clause; changed “such that”
to “so that”
725.987(f)
Changed “U.S. Department of Transportation (USDOT)” to “USDOT”
725.987(h)
Added definite article “the”; added “is as follows”; changed ending
punctuation to a colon
14
Table 3:
Revisions to the Text of the Proposed Amendments in Final Adoption
Section Revised
Source(s) of
Revision(s)
Revision(s)
720.111 “NTIS, Method 164”
JCAR
Added closing quotation mark after “gravimetry”;
corrected spelling of “document”
720.111 “NTIS, Method 164”
JCAR
Deleted comma from “August 1993”
722.134(f)
Board
Added comma before “unless” to offset a
parenthetical
724 source note
Board
Added “effective” to correct the reference to R95-20
724.983(b)(1)(B)
Board
Corrected the cross-reference format to “Subsection
724.982(c)(2)” by removing a space
724.986(e)(6)
JCAR
Corrected cross-reference from “this subsection” to
“this subsection (e)(6)”
725.987(e)(6)
JCAR
Corrected cross-reference from “this subsection” to
“this subsection (e)(6)”
Table 4:
Requested Revisions to the Text of the Proposed Amendments Not Made in Final
Adoption
Section Affected
Source(s) of Request:
Requested Revision(s)
Explanation
720. authority note
JCAR: failed to add Sections
7.2 and 13 of the Act to the
note
The Board has decided to add references
to Sections 7.2 and 13 of the Act, since
the scope of our identical-in-substance
authority is in part defined by Section 7.2,
and many segments of Part 720 derived
from the federal underground injection
control regulations under Section 13
722. authority note
JCAR: failed to add Section
7.2 of the Act to the note
The Board has decided to add a
reference to Section 7.2 of the Act, since
the scope of our identical-in-substance
authority is in part defined by Section 7.2
725. authority note
JCAR: failed to add Section
7.2 of the Act to the note
The Board has decided to add a
reference to Section 7.2 of the Act, since
the scope of our identical-in-substance
authority is in part defined by Section 7.2
725.984(a)(3)(C)
JCAR: remove comma after
“adjustment factor (f
m25D
)”
Comma already overstruck for deletion in
the original proposal
15
HISTORY OF RCRA SUBTITLE C AND UIC ADOPTION
ILLINOIS ENVIRONMENTAL PROTECTION AGENCY OR BOARD ACTION
EDITORIAL CONVENTIONS
The Board appends the following three discussions to this opinion. The first is a summary
history of the Illinois RCRA Subtitle C and UIC programs. It lists all Board actions taken to adopt and
maintain these programs since their inception. 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 exemptions or exceptions. 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.
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. The dockets captioned Proposed Regulations for
“RCRA” (Chapter 7 and Chapter 9) (September 16, 1981, and February 4, 1982), R81-22, and
Amendments to Phase I, RCRA Rules (January 13, 1983), R82-18, dealt with the Phase I RCRA
Subtitle C regulations. The Board adopted RCRA Subtitle C Phase II regulations in Parts 703 and 724
in dockets Phase II, RCRA Rules (July 26, 1983), R82-19, and Technical Correction to Phase II
RCRA Rules (December 15, 1983), R83-24. USEPA reviewed and authorized the Illinois Phase I and
Phase II regulations. The entire listing of all RCRA Subtitle C identical-in-substance rulemakings
follows. A listing of federal authorizations of the Illinois program to date, as noticed in the
Federal
Register
, appears at the end of this historical summary of the Illinois hazardous waste program.
R81-22
Proposed Regulations for “RCRA” (Chapter 7 and Chapter 9) (September 16,
1981, and February 4, 1982), R81-22; published at 6 Ill. Reg. 4828 (April 23,
1982), effective May 17, 1982. (Federal rules and amendments adopted by
USEPA during the period May 18, 1980, through October 1, 1981.)
R82-18
Amendments to Phase I, RCRA Rules (January 13, 1983), R82-18; published
at 7 Ill. Reg. 2518 (March 4, 1983), effective May 17, 1982. (Federal rules
and amendments adopted by USEPA during the period November 11, 1981,
through June 24, 1982.)
R82-19
Phase II, RCRA Rules (July 26, 1983), R82-19; published at 7 Ill. Reg. 13999
(October 28, 1983), effective October 2, 1983. (Federal rules and
amendments adopted by USEPA during the period November 23, 1981,
through October 29, 1982.)
16
R83-24
1
Technical Correction to Phase II RCRA Rules (December 15, 1983), R83-24;
published at 8 Ill. Reg. 200 (January 6, 1984), effective December 27, 1983.
(Corrections to the docket R82-19 rules.)
R84-9
RCRA and UIC Update (June 13 and 27, 1985), R84-9; published at 9 Ill.
Reg. 11964 (August 2, 1985), effective July 8 and 24, 1985. (Federal rules
and amendments adopted by USEPA during the period January 19, 1983,
through April 24, 1984.)
R85-22
RCRA Update (April 24, 1984, through June 30, 1985) (December 20, 1985
and January 9, 1986), R85-22; published at 10 Ill. Reg. 968 (January 17,
1986), effective January 2, 1986.
R86-1
RCRA Update, USEPA Regulations (July 1, 1985, through December 31,
1985) (July 11, 1986), R86-1; published at 10 Ill. Reg. 13998 (August 22,
1986), effective August 12, 1986.
R86-19
RCRA Update (February 1, 1986, through March 31, 1986) (October 23,
1986), R86-19; published at 10 Ill. Reg. 20630 (December 12, 1986),
effective December 2, 1986.
R86-28
RCRA Update (April 1, 1986, through June 30, 1986) (February 5, 1987;
amended March 5, 1987; corrected April 16, 1987), R86-28; published at 11
Ill. Reg. 6017 (April 3, 1987), effective March 23, 1987; correction published
at 11 Ill. Reg. 8684 (May 1, 1987), effective April 21, 1987.
R86-46
RCRA Update (July 1, 1986, through September 30, 1986) (July 16, 1987),
R86-46; published at 11 Ill. Reg. 13435 (August 14, 1987), effective August 4,
1987.
R87-5
RCRA Update (October 1, 1986, through December 31, 1986) (October 15,
1987), R87-5; published at 11 Ill. Reg. 19280 (November 30, 1987), effective
November 10 and 12, 1987.
R87-26
RCRA Update (January 1, 1987, through June 30, 1987) (December 3, 1987),
R87-26; published at 12 Ill. Reg. 2450 (January 29, 1988), effective
January 15, 1988.
1
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).
17
R87-32
Correction to R86-1 (September 4, 1987), R87-32; published at 11 Ill. Reg.
16698 (October 16, 1987), effective September 30, 1987.
R87-39
RCRA Update, USEPA Regulations (July 1, 1987, through December 31,
1987) (June 16, 1988), R87-39; published at 12 Ill. Reg. 12999 (August 12,
1988), effective July 29, 1988.
R88-16
RCRA Update, USEPA Regulations (January 1, 1988, through July 31, 1988)
(November 17, 1988), R88-16; published at 13 Ill. Reg. 447 (January 13,
1989), effective December 28, 1988.
R89-1
RCRA Update, USEPA Regulations (August 1, 1988, through December 31,
1988) (September 13, 1989), R89-1; published at 13 Ill. Reg. 18278
(November 27, 1989), effective November 13, 1989.
R89-9
RCRA Update, USEPA Regulations (January 1, 1989, through June 30, 1989)
(March 8, 1990), R89-9; published at 14 Ill. Reg. 6225 (April 27, 1990),
effective April 16, 1990.
R90-2
RCRA Update, USEPA Regulations (July 1, 1989, through December 31,
1989) (July 3, 1990), R90-2; published at 14 Ill. Reg. 14401 (September 7,
1990), effective August 22, 1990.
R90-11
RCRA Update, USEPA Regulations (April 1, 1990, through June 30, 1990)
(April 11, 1991; corrected May 23, 1991; corrected August 8, 1991;
uncorrected August 22, 1991), R90-11; published at 15 Ill. Reg. 9323
(June 28, 1991), effective June 17, 1991.
R90-17
RCRA Delistings (See below.)
R91-1
RCRA Update, USEPA Regulations (July 1, 1990, through December 31,
1990) (August 8, 1991), R91-1; published at 15 Ill. Reg. 14446 (October 11,
1991), effective September 30, 1991. (Wood Preserving Rules.)
R91-13
RCRA Update, USEPA Regulations (January 1, 1991, through June 30, 1991)
(April 9, 1992), R91-13; published at 16 Ill. Reg. 9489 (June 19, 1992),
effective June 9, 1992. (Boilers and Industrial Furnace (BIF) Rules.)
R91-26
RCRA Wood Preserving compliance Dates (Identical in Substance Rules)
(January 9, 1992), R91-26; published at 16 Ill. Reg. 2600 (February 14,
1992), effective February 3, 1992. (Wood Preserving Rules Compliance
Dates.)
18
R92-1
RCRA Update, USEPA Regulations (July 1, 1991, through December 31,
1991) (September 17, 1992), R92-1; published at 16 Ill. Reg. 17636
(November 20, 1992), effective November 6, 1992.
R92-10
RCRA Update, USEPA Regulations (January 1, 1992, through June 30, 1992)
(January 21, 1993), R92-10; published at 17 Ill. Reg. 5625 (April 9, 1993),
effective March 26, 1993. (Leak Detection System (LDS) Rules.)
R93-4
RCRA Update, USEPA Regulations (July 1, 1992, through December 31,
1992) (September 23, 1993), R93-4; published at 17 Ill. Reg. 20545
(December 3, 1993), effective November 22, 1993. (Used Oil Rules.)
R93-16
RCRA Update, USEPA Regulations (January 1, 1993, through June 30, 1993)
(March 17, 1994, supplemental opinion and order on April 21, 1994), R93-16;
published at 18 Ill. Reg. 6720 (May 6, 1994), effective April 26, 1994.
R94-7
RCRA Subtitle C Update, USEPA Regulations (July 1, 1993, through
December 31, 1993) (June 23, 1994), R94-7; published at 18 Ill. Reg. 12160
(August 12, 1994), effective July 29, 1994.
R94-17
RCRA Subtitle C Update, USEPA Regulations (January 1, 1994, through
June 30, 1994) (October 20, 1994), R94-17; published at 18 Ill. Reg. 17480
(December 9, 1994), effective November 23, 1994.
R95-6
RCRA Subtitle C Update, USEPA Regulations (July 1, 1994, through
December 31, 1994, January 3, 1995 and May 19, 1995) (Consolidated with
R95-4) (June 1 and 15, 1995), R95-6; published at 19 Ill. Reg. 9501 (July 14,
1995), effective June 27, 1995.
R95-20
RCRA Subtitle C Update, USEPA Regulations (January 1, 1995, through
June 30, 1995; July 7, 1995; September 29, 1995; November 13, 1995;
June 6, 1996) (June 20, 1996), R95-20; published at 20 Ill. Reg. 10929
(August 16, 1996), effective August 1, 1996.
R96-10
RCRA Subtitle C Update, USEPA Regulations (July 1, 1995, through
December 31, 1995) (Consolidated with R97-3 and R97-5) (November 6,
1997), R96-10; published at 22 Ill. Reg. 256 (January 2, 1998), effective
December 16, 1997.
R97-5
RCRA Subtitle C Update, USEPA Regulations (January 1, 1996, through
June 30, 1996) (Consolidated with R96-10 and R97-3) (November 6, 1997),
R97-5; published at 22 Ill. Reg. 256 (January 2, 1998), effective December 16,
1997.
19
R97-21
RCRA Subtitle C (HW) Update, USEPA Regulations (July 1, 1996, through
December 31, 1996) (Consolidated with R98-3 and R98-5) (August 20,
1998), R97-21; published at 22 Ill. Reg. 17930 (October 9, 1998), effective
September 28, 1998.
R98-5
RCRA Subtitle C Update, USEPA Regulations (January 1, 1997, through
June 30, 1997) (Consolidated with R97-21 and R98-3) (August 20, 1998),
R98-5; published at 22 Ill. Reg. 17930 (October 9, 1998), effective
September 28, 1998.
R98-21
RCRA Subtitle C Update, USEPA Regulations (July 1, 1997, through
December 31, 1997) (Consolidated with R99-2 and R99-7) (December 17,
1998), R98-21; published at 23 Ill. Reg. 1695 (February 5, 1999), effective
January 19, 1999.
R99-2
RCRA Subtitle C Update, USEPA Regulations (January 1, 1998, through
June 30, 1998) (Consolidated with R98-21 and R99-7) (December 17, 1998),
R99-2; published at 23 Ill. Reg. 1695 (February 5, 1999), effective January 19,
1999.
R99-15
RCRA Subtitle C Update, USEPA Regulations (July 1, 1998, through
December 31, 1998) (June 17, 1999), R99-15; published at 23 Ill. Reg. 9094
(August 13, 1999), effective July 26, 1999.
R00-5
RCRA Subtitle C Update, USEPA Regulations (January 1, 1999, through
June 30, 1999) (this Docket.)
The Board added to the federal listings of hazardous waste by listing dioxins pursuant to Section
22.4(d) of the Act:
R84-34
Hazardous Waste Listings and Test Methods for Identification of
Tetrachlorodibenzo-p-Dioxins (November 21, 1984), R84-34; published at 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 Oil Company, Envirite
Corporation, USX Corporation, and Conversion Systems, Inc. (CSI):
20
R85-2
Petition of Amoco Oil Company Amendment to 35 Ill. Adm. Code Part 721,
Appendix I (April 24, 1986), R85-2; published at 10 Ill. Reg. 8112 (May 16,
1986), effective May 2, 1986.
R87-30
Petition for Rulemaking to Adopt Regulations Identical in Substance to federal
RCRA Requirements filed by the Envirite Corporation (June 30, 1988), R87-
30; published at 12 Ill. Reg. 12070 (July 22, 1988), effective July 12, 1988.
R91-12
Delisting Petition for USX Corporation (Identical in Substance Rule)
(December 19, 1991), R91-12; published at 16 Ill. Reg. 2155 (February 7,
1992), effective January 27, 1992.
R95-20
RCRA Subtitle C, USEPA Regulations (January 1, 1995, through June 30,
1995, July 7, 1995, September 29, 1995, November 13, 1995, and June 6,
1996) (June 20, 1996), R95-20; published at 20 Ill. Reg. 10929 (August 16,
1996), effective August 1, 1996.
On April 30, 1990, USEPA authorized Illinois to grant waste delistings. Upon this
authorization, USEPA transferred pending delisting petitions to the Board. The Board docketed these
as site-specific rulemaking proceedings:
R90-18
USX Corporation, Southworks Delisting (Site-Specific) (June 6, 1991), R90-
18. (Dismissed.)
R90-19
Woodward Governor Company Delisting (Site-Specific) (November 8, 1990),
R90-19. (Dismissed.)
R90-23
General Motors Corporation Site-Specific Exception to 35 Ill. Adm. Code
216.381 for Ferrous Foundries in Vermilion County (July 11, 1991), R90-23.
(Dismissed.)
The Board has modified the delisting procedures to allow the use of adjusted standards in lieu of
site-specific rulemakings:
R90-17
RCRA Delistings (February 28, 1991), R90-17; published at 15 Ill. Reg. 7934
(May 24, 1991), 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:
AS 89-4
In re
Safety-Kleen Corporation, Petition for an Adjusted Standard
(November 15, 1989), AS 89-4. (Dismissed.)
21
AS 89-5
In re
Safety-Kleen Corporation, Petition for an Adjusted Standard (July 3,
1990), AS 89-5. (Dismissed.)
AS 90-7
In re
Petition of Quantum Chemical Company, USI Division, for an Adjusted
Standard (July 11, 1991), AS 90-7. (Dismissed.)
AS 96-11
In re
Petition of Chemetco, Inc. for an Adjusted Standard (August 1, 1996),
AS 96-11. (Dismissed.)
AS 97-2
In re
Petition of Chemetco, Inc. for an Adjusted Standard (March 19, 1998),
AS 97-2. (Denied.)
AS 97-9
In re
Petition of Recycle Technologies, Inc. for an Adjusted Standard
(September 3, 1998), AS 97-9. (Granted.)
AS 99-3
In re
Petition of Big River Zinc Corporation for an Adjusted Standard
(April 15, 1999), AS 99-3. (Granted.)
AS 00-1
In re
Petition of Horsehead Resource Development Company, Inc. for an
Adjusted Standard (August 5, 1999), AS 00-1. (Dismissed.)
AS 00-2
In re
Petition of Horsehead Resource Development Company, Inc. for an
Adjusted Standard, AS 00-2. (Presently pending.)
Waste generators have filed Part 106 adjusted standard petitions for hazardous waste delistings
with the Board pursuant to Section 720.122:
AS 91-1
In re
Petition of Keystone Steel & Wire Co. for Hazardous Waste
Delisting
(February 6, 1992), AS 91-1. (Granted.)
AS 91-3
In re
Petition of Peoria Disposal Company for an Adjusted Standard
(February 4, 1993), AS 91-3. (Granted.)
AS 93-7
In re
Petition of Keystone Steel & Wire Company for an Adjusted Standard
(February 17, 1994), AS 93-7. (Granted.)
AS 94-10
In re
Petition of Envirite Corporation for an Adjusted Standard (December 14,
1994), AS 94-10. (Granted.)
The Board has procedures to be followed in cases before it involving the RCRA Subtitle C
regulations:
22
R84-10
RCRA and UIC Procedural Rules (December 20, 1984, and January 10,
1985), R84-10; published at 9 Ill. Reg. 1383 (February 1, 1985), 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 RCRA Update (April 24, 1984,
through June 30, 1985) (December 20, 1985, and January 9, 1986), R85-22 and amended them in
RCRA Update (July 1, 1986, through September 30, 1986) (July 16, 1987), R86-46, listed above.
One Part 106 adjusted standard proceeding filed pursuant to 728.106 sought relief from a
prohibition against land disposal:
AS 90-6
In re
Petition of Marathon Petroleum Company for an Adjusted Standard to
Allow Land Disposal of a Waste Prohibited (September 17, 1992), AS 90-6.
(Dismissed.)
Other adjusted standard proceedings sought relief from aspects of the land disposal unit closure
and post-closure care requirements:
AS 90-8
In re
Petition of Olin Corporation for an Adjusted Standard (Related to
Closure and Post Closure of RCRA Regulated Surface Impoundments)
(February 27, 1992), AS 90-8. (Granted.)
AS 91-4
In re
Petition of Amoco Oil Company for an Adjusted Standard (March 11,
1992), AS 91-4. (Granted.)
One adjusted standard proceeding sought relief from a RCRA Subtitle C land disposal
restriction:
AS 90-6
In re
Petition of Marathon Petroleum Company for an Adjusted Standard to
Allow Land Disposal of a Waste Prohibited (September 17, 1992), AS 90-6.
(Dismissed.)
Still another adjusted standard proceeding relates to substantive treatment, storage, and
disposal facility requirements of the RCRA Subtitle C regulations:
AS 91-10
In re
Petition of Cabot Corporation for an Adjusted Standard (May 19, 1994),
AS 91-10. (Dismissed; secondary containment for tanks.)
One adjusted standard proceeding related to the requirements applicable to the contents of the
application for a facility permit under the RCRA Subtitle C regulations:
23
AS 97-11
In re
Petition of Ensign-Bickford Company for an Adjusted Standard (June 19,
1997), AS 97-11. (Denied; topographic facility map requirement.)
A final adjusted standard filed under 35 Ill. Adm. Code 725.213(e) allowed the continued
operation of a lagoon that had formerly received hazardous waste but which did not comply with the
liner and leachate collection system requirements of 35 Ill. Adm. Code 725.321:
AS 97-3
In re
Shell Wood River Refining Company for an Adjusted Standard (May 15,
1997), AS 97-3. (Granted.)
AS 98-6
In re
Wood River Refining Co., a Division of Equilon Enterprises LLC, f/k/a
Shell Wood River Refining Co., for an Adjusted Standard (March 18, 1999),
AS 98-6. (Granted.)
In another regulatory proceeding, the Board has considered granting temporary relief from the
termination of a hazardous waste listing in the form of an emergency rule:
R91-11
Certain Hazardous Wastes from Primary Zinc Smelting and Refining, 35 Ill.
Adm. Code 721.104(b)(7)(U) (August 8, 1991), R91-11. (Filed by 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
Proposal for Adoption of Sanitary landfill Regulation, Rule 310: Special
Wastes; Prohibition of Landfilling of Halogenated Solvents filed by Citizens for
a Better Environment (October 25, 1984), R81-25; published at 8 Ill. Reg.
24124 (December 14, 1984), effective December 4, 1984.
R83-28
Definition of Liquid Hazardous Waste (February 26, 1986), R83-28; published
at 10 Ill. Reg. 4875 (March 21, 1986), effective March 7, 1986.
R86-9
Hazardous Waste Prohibitions (Emergency Rule) (October 23, 1986), R86-9;
published at 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).
Public Act 90-502, effective August 19, 1997, amended Section 22.23a of the Act to require
the Board to designate high intensity discharge lamps and fluorescent lamps as a category of universal
24
waste based on a proposal to be filed by the Illinois Environmental Protection Agency (IEPA). The
Board adopted such amendments to the Illinois hazardous waste rules on April 2, 1998, effective
April 15, 1998. Amendments of 35 Ill. Adm. Code 703, 720, 721, 724, 725, 728, and 733
(Standards For Universal Waste Management) (April 2, 1998), R98-12.
USEPA periodically reviews the Illinois hazardous waste program. As a result of these reviews,
USEPA has granted Illinois a number of authorizations. The
Federal Register
citations for the
authorizations are listed as follows:
47 Fed. Reg. 21043 (May 17, 1982) (Phase I authorization)
51 Fed. Reg. 3778 (January 30, 1986) (Phase II authorization), effective January 31, 1986
53 Fed. Reg. 126 (January 5, 1988) (partial HSWA authorization), effective March 5, 1988
54 Fed. Reg. 37649 (September 12, 1989) (approvals codified as 40 C.F.R. 272.700 and
272.701), effective November 13, 1989
55 Fed. Reg. 7320 (March 1, 1990), effective April 30, 1990
56 Fed. Reg. 13595 (April 3, 1991), effective June 3, 1991
57 Fed. Reg. 3731 (January 31, 1992), effective March 31, 1992
59 Fed. Reg. 30525 (June 14, 1994), effective August 14, 1994
61 Fed. Reg. 10684 (March 15, 1996), effective May 14, 1996
61 Fed, Reg. 40520 (August 5, 1996), effective October 4, 1996
History of UIC Rules Adoption
The Board has adopted and amended Underground Injection Control (UIC) regulations in
several dockets to correspond with the federal regulations. One such docket, Amendments to Phase I,
RCRA Rules (January 13, 1983), R82-18, was a RCRA Subtitle C docket. The entire listing of all
UIC rulemakings follows:
R81-32
Underground Injection Control Regulations, Waste Disposal (May 13, 1982),
R81-32; published at 6 Ill. Reg. 12479 (October 15, 1982), effective
February 1, 1984.
R82-18
Amendments to Phase I, RCRA Rules (January 13, 1983), R82-18; published
at 7 Ill. Reg. 2518 (March 4, 1983), effective May 17, 1982.
25
R83-39
Amendment of 35 Ill. Adm. Code 704.122, Underground Injection Control
(December 15, 1983), R83-39; published at 7 Ill. Reg. 17338 (December 20,
1983), effective December 19, 1983. (Amendments adopted by USEPA on
April 1, 1983.)
R85-23
UIC Update, USEPA Regulations (through June 30, 1985) (June 20 and
July 11, 1986), R85-23; published at 10 Ill. Reg. 13274 (August 8, 1986),
effective July 28 and 29, 1986.
R86-27
UIC Update (July 1, 1986, through December 31, 1986) (April 16, 1987),
R86-27. (Dismissed; no USEPA amendments in the update period.)
R87-29
UIC Update, USEPA Regulations (January 1, 1987, through June 30, 1987)
(January 21, 1988), R87-29; published at 12 Ill. Reg. 6673 (April 8, 1988),
effective March 28, 1988.
R88-2
UIC Update, USEPA Regulations (July 1, 1987, through December 31, 1987)
(June 30, 1988), R88-2; published at 12 Ill. Reg. 13700 (August 26, 1988),
effective August 16, 1988.
R88-17
UIC Update, USEPA Regulations (January 1, 1988, through June 30, 1988)
(December 15, 1988), R88-17; published at 13 Ill. Reg. 478 (January 13,
1989), effective December 30, 1988.
R89-2
UIC Update, USEPA Regulations (July 1, 1988, through December 31, 1988,
(January 25, 1990), R89-2; published at 14 Ill. Reg. 3059 (March 2, 1990),
effective February 20, 1990.
R89-11
UIC Update, USEPA Regulations (January 1, 1989, through June 30, 1989)
(May 24, 1990), R89-11; published at 14 Ill. Reg. 11948 (July 20, 1990),
effective July 9, 1990.
R90-5
UIC Update, USEPA Regulations (July 1, 1989, through December 31, 1989)
(March 22, 1990), R90-5. (Dismissed; no USEPA amendments in the update
period.)
R90-14
UIC Update, USEPA Regulations (January 1, 1990, through June 30, 1990)
(May 23, 1991), R90-14; published at 15 Ill. Reg. 11425 (August 9, 1991),
effective July 24, 1991.
26
R91-4
UIC Update, USEPA Regulations (July 1, 1990, through December 31, 1990)
(February 28, 1991), R91-4. (Dismissed; no USEPA amendments in the
update period.)
R91-16
UIC Update, USEPA Regulations (January 1, 1991, through June 30, 1991)
(December 6, 1991), R91-16. (Dismissed; no USEPA amendments in the
update period.)
R92-4
UIC Update, USEPA Regulations (July 1, 1990, through December 31, 1990)
(April 9, 1992), R92-4. (Dismissed; no USEPA amendments in the update
period.)
R92-13
UIC Update, USEPA Regulations (January 1, 1992, through June 30, 1992)
(February 4, 1993), R92-13; published at 17 Ill. Reg. 6190 (April 16, 199),
effective April 5, 1993.
R93-6
UIC Update, USEPA Regulations (July 1, 1992, through December 31, 1992)
(August 5, 1993), R93-6; published at 17 Ill. Reg. 15641 (September 24,
1993), effective September 14, 1993.
R93-17
UIC Update, USEPA Regulations (January 1, 1993, through June 30, 1993)
(September 23, 1993), R93-17. (Dismissed; no USEPA amendments in the
update period.)
R94-5
UIC Update, USEPA Regulations (July 1, 1993, through December 31, 1993)
(November 3, 1994), R94-5; published at 18 Ill. Reg. 18244 (December 23,
1994), effective December 20, 1994.
R94-24
UIC Update, USEPA Regulations (January 1, 1994, through June 30, 1994)
(October 6, 1994), R94-24. (Dismissed; the Board included the USEPA
amendments that occurred in the update period in RCRA Subtitle C Update,
USEPA Regulations (January 1, 1994, through June 30, 1994) (October 20,
1994), R94-17.
R95-4
UIC Update, USEPA Regulations (July 1, 1994, through December 31, 1994)
(Consolidated with R95-6) (June 1 and 15, 1995), R95-4; published at 19 Ill.
Reg. 9501 (July 14, 1995), effective June 27, 1995.
R95-18
UIC Update, USEPA Regulations (January 1, 1995, through June 30, 1995)
(October 5, 1995), R95-18. (Dismissed; no USEPA amendments in the
update period.)
27
R96-8
UIC Update, USEPA Regulations (July 1, 1995, through December 31, 1995)
(February 15, 1996, R96-8). (Dismissed; no USEPA amendments in the
update period.)
R97-3
UIC Update, USEPA Regulations (January 1, 1996, through June 30, 1996)
(Consolidated with R96-10 and R97-5) (November 6, 1997), R97-3;
published at 22 Ill. Reg. 256 (January 2, 1998), effective December 16, 1997.
R97-19
UIC Update, USEPA Regulations (July 1, 1996, through December 31, 1996)
(May 1, 1997), R97-19. (Dismissed; no USEPA amendments in the update
period.)
R98-3
UIC Update, USEPA Regulations (January 1, 1997, through June 30, 1997)
(Consolidated R97-21 and R98-5) (August 20, 1998), R98-3; published at 22
Ill. Reg. 17930 (October 9, 1998), effective September 18, 1998.
R98-19
UIC Update, USEPA Regulations (July 1, 1997, through December 31, 1997)
(February 19, 1998), R98-19. (Dismissed; no USEPA amendments in the
update period.)
R99-7
UIC Update, USEPA Regulations (January 1, 1998, through June 3, 1998)
(Consolidated with R98-21 and R99-2) (December 17, 1998), R99-7;
published at 23 Ill. Reg. 1695 (February 5, 1999), effective January 19, 1999.
R99-13
UIC Update, USEPA Regulations (July 1, 1998, through December 31, 1998)
(February 18, 1999), R99-13. (Dismissed; no USEPA amendments in the
update period.)
R00-3
UIC Update, USEPA Regulations (January 1, 1999, through June 3, 1999)
(August 19, 1999), R00-3. (Dismissed; no USEPA amendments in the update
period.)
The Board has twice considered an adjusted standard from a UIC land disposal restriction,
pursuant to the procedures outlined above with respect to the RCRA Subtitle C program:
AS 92-8
In re
Petition of Cabot Corporation for Adjusted Standard (February 17,
1994), AS 92-8. (Granted; no migration exception.)
AS 96-3
In re
Petition of Cabot Corporation for Adjusted Standard (March 7, 1996),
AS 92-8. (Granted modification of
In re
Petition of Cabot Corporation for
Adjusted Standard (February 17, 1994), AS 92-8. (No migration exception.))
28
USEPA authorized the Illinois UIC program on March 3, 1984, at 49 Fed. Reg. 3991
(February 1, 1984); codified that approval as 40 C.F.R. 147, Subpart O, at 49 Fed. Reg. 20197
(May 11, 1984); and amended the authorization at 53 Fed. Reg. 43087 (October 25, 1988) and 56
Fed. Reg. 9414 (March 6, 1991).
Illinois Environmental Protection IEPA or Board Action
Section 7.2(a)(5) of the Act requires the Board to specify for which portions of the program
USEPA will retain decision making authority. Based on the general division of functions within the Act
and other Illinois statutes, the Board is also to specify which State agency is to make decisions.
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 some identical-in-substance rules, certain decisions pertaining to a permit application are not
appropriate for the IEPA to consider. In determining the general division of authority between the IEPA
and the Board, the following factors should be considered:
1.
Whether the person making the decision is 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.
Whether there is a clear standard for action such that the Board can give meaningful
review to an IEPA decision.
3.
Whether the action would result in exemption from the permit requirement itself. If so,
Board action is generally required.
4.
Whether the decision amounts 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 decisions: 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). There often are differences in the nomenclature for these decisions between the USEPA
and Board regulations.
29
IT IS SO ORDERED.
I, Dorothy M. Gunn, Clerk of the Illinois Pollution Control Board, do hereby certify that the
above opinion was adopted on the 2nd day of December 1999 by a vote of 6-0.
Dorothy M. Gunn, Clerk
Illinois Pollution Control Board
ILLINOIS POLLUTION CONTROL BOARD
December 2, 1999
IN THE MATTER OF:
)
)
RCRA SUBTITLE C UPDATE, USEPA
)
R00-5
AMENDMENTS (January 1, 1999, through
)
(Identical-in-Substance
June 30, 1999)
)
Rulemaking - Land)
Adopted Rule. Final Order.
ORDER OF THE BOARD (by E.Z. Kezelis):
Under Sections 7.2 and 22.4(a) of the Environmental Protection Act (Act) (415 ILCS 5/7.2
and 22.4(a) (1998)), the Board today adopts amendments to the Illinois regulations that are “identical in
substance” to hazardous waste regulations that the United States Environmental Protection Agency
(USEPA) adopted to implement Subtitle C of the federal Resource Conservation and Recovery Act of
1976 (RCRA Subtitle C) (42 U.S.C. §§ 6921
et seq
. (1998)). The nominal timeframe of this docket
includes federal RCRA Subtitle C amendments that USEPA adopted in the period January 1, 1999,
through June 30, 1999.
30
Sections 7.2 and 22.4(a) provide for quick adoption of regulations that are identical in
substance to federal regulations that USEPA adopts to implement Sections 3001 through 3005 of
RCRA (42 U.S.C. §§ 6921-6925 (1998)). Section 22.4(a) also provides that Title VII of the Act and
Section 5 of the Administrative Procedure Act (APA) (5 ILCS 100/5-35 and 5-40 (1998)) do not
apply to the Board’s adoption of identical-in-substance regulations. The federal RCRA Subtitle C
regulations are found at 40 C.F.R. 260 through 266, 268, 270, 271, 273, and 279.
This order is supported by an opinion that the Board also adopts today. The Board will wait 30
days for USEPA to review the amendments, as provided in the agreement between USEPA and the
State of Illinois relating to federal authorization of the State program, in order to allow USEPA an
additional opportunity to review the amendments before they become effective. We will then file the
amendments with the Secretary of State and submit Notices of Adopted Amendments for publication in
the
Illinois Register
. The complete text of the adopted amendments follows.
IT IS SO ORDERED.
I, Dorothy M. Gunn, Clerk of the Illinois Pollution Control Board, do hereby certify that the
above order was adopted on the 2nd day of December 1999 by a vote of 6-0.
Dorothy M. Gunn, Clerk
Illinois Pollution Control Board
31
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 Sections 7.2, 13, and 22.4 and authorized by Section 27 of the
Environmental Protection Act [415 ILCS 5/7.2, 13, 22.4, and 27].
SOURCE: Adopted in R81-22, 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,
32
effective December 2, 1986; amended in R86-28 at 11 Ill. Reg. 6017, effective March 24, 1987;
amended in R86-46 at 11 Ill. Reg. 13435, effective August 4, 1987; amended in R87-5 at 11 Ill. Reg.
19280, effective November 12, 1987; amended in R87-26 at 12 Ill. Reg. 2450, effective January 15,
1988; amended in R87-39 at 12 Ill. Reg. 12999, effective July 29, 1988; amended in R88-16 at 13 Ill.
Reg. 362, effective December 27, 1988; amended in R89-1 at 13 Ill. Reg. 18278, effective November
13, 1989; amended in R89-2 at 14 Ill. Reg. 3075, effective February 20, 1990; amended in R89-9 at
14 Ill. Reg. 6225, effective April 16, 1990; amended in R90-10 at 14 Ill. Reg. 16450, effective
September 25, 1990; amended in R90-17 at 15 Ill. Reg. 7934, effective May 9, 1991; amended in
R90-11 at 15 Ill. Reg. 9323, effective June 17, 1991; amended in R91-1 at 15 Ill. Reg. 14446,
effective September 30, 1991; amended in R91-13 at 16 Ill. Reg. 9489, effective June 9, 1992;
amended in R92-1 at 16 Ill. Reg. 17636, effective November 6, 1992; amended in R92-10 at 17 Ill.
Reg. 5625, effective March 26, 1993; amended in R93-4 at 17 Ill. Reg. 20545, effective November
22, 1993; amended in R93-16 at 18 Ill. Reg. 6720, effective April 26, 1994; amended in R94-7 at 18
Ill. Reg. 12160, effective July 29, 1994; amended in R94-17 at 18 Ill. Reg. 17480, effective November
23, 1994; amended in R95-6 at 19 Ill. Reg. 9508, effective June 27, 1995; amended in R95-20 at 20
Ill. Reg. 10929, August 1, 1996; amended in R96-10/R97-3/R97-5 at 22 Ill. Reg. 256, effective
December 16, 1997; amended in R98-12 at 22 Ill. Reg. 7590, effective April 15, 1998; amended in
R97-21/R98-3/R98-5 at 22 Ill. Reg. 17496, effective September 28, 1998; amended in R98-21/R99-
2/R99-7 at 23 Ill. Reg. 1704, effective January 19, 1999; amended in R99-15 at 23 Ill. Reg. 9094,
effective July 26, 1999; amended in R00-5 at 24 Ill. Reg. ________, effective
______________________.
SUBPART B: DEFINITIONS
Section 720.111
References
a)
The following publications are incorporated by reference for the purposes of this Part
and 35 Ill. Adm. Code 703 through 705, 721 through 726, 728, 730, 731, 733, 738,
and 739:
ACI. Available from the American Concrete Institute, Box 19150, Redford
Station, Detroit, Michigan 48219:
ACI 318-83: “Building Code Requirements for Reinforced Concrete”,
adopted September, 1983.
ANSI. Available from the American National Standards Institute, 1430
Broadway, New York, New York 10018, 212-354-3300:
ANSI B31.3 and B31.4. See ASME/ANSI B31.3 and B31.4.
API. Available from the American Petroleum Institute, 1220 L Street, N.W.,
33
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.
APTI. Available from the Air and Waste Management Association, Box 2861,
Pittsburgh, PA 15230, 412-232-3444:
APTI Course 415: Control of Gaseous Emissions, USEPA Publication
EPA-450/2-81-005, December, 1981.
ASME. Available from the American Society of Mechanical Engineers, 345
East 47th Street, New York, NY 10017, 212-705-7722:
“Chemical Plant and Petroleum Refinery Piping”, ASME/ANSI B31.3-
1987, as supplemented by B31.3a-1988 and B31.3b-1988. Also
available from ANSI.
“Liquid Transportation Systems for Hydrocarbons, Liquid Petroleum
Gas, Anhydrous Ammonia, and Alcohols”, ASME/ANSI B31.4-1986,
as supplemented by B31.4a-1987. Also available from ANSI.
ASTM. Available from American Society for Testing and Materials, 1916
Race Street, Philadelphia, PA 19103, 215-299-5400:
ASTM C 94-90, Standard Specification for Ready-Mixed Concrete,
approved March 30, 1990.
ASTM D 88-87, Standard Test Method for Saybolt Viscosity, April
24, 1981, reapproved January, 1987.
ASTM D 93-85, Standard Test Methods for Flash Point by Pensky-
34
Martens Closed Tester, approved October 25, 1985.
ASTM D 1946-90, Standard Practice for Analysis of Reformed Gas
by Gas Chromatography, approved March 30, 1990.
ASTM D 2161-87, Standard Practice for Conversion of Kinematic
Viscosity to Saybolt Universal or to Saybolt Furol Viscosity, March 27,
1987.
ASTM D 2267-88, Standard Test Method for Aromatics in Light
Naphthas and Aviation Gasolines by Gas Chromatography, approved
November 17, 1988.
ASTM D 2382-88, Standard Test Method for Heat of Combustion of
Hydrocarbon Fuels by Bomb Calorimeter (High Precision Method),
approved October 31, 1988.
ASTM D 2879-92, Standard Test Method for Vapor Pressure-
Temperature Relationship and Initial Decomposition Temperature of
Liquids by Isoteniscope, approved 1992.
ASTM D 3828-87, Standard Test Methods for Flash Point of Liquids
by Setaflash Closed Tester, approved December 14, 1988.
ASTM E 168-88, Standard Practices for General Techniques of
Infrared Quantitative Analysis, approved May 27, 1988.
ASTM E 169-87, Standard Practices for General Techniques of
Ultraviolet-Visible Quantitative Analysis, approved February 1, 1987.
ASTM E 260-85, Standard Practice for Packed Column Gas
Chromatography, approved June 28, 1985.
ASTM Method G 21-70 (1984a) -- Standard Practice for Determining
Resistance of Synthetic Polymer Materials to Fungi.
ASTM Method G 22-76 (1984b) -- Standard Practice for Determining
Resistance of Plastics to Bacteria.
MICE. Methods Information Communication Exchange Service, 703-821-
4690:
“Test Methods for Evaluating Solid Waste, Physical/Chemical
35
Methods”, USEPA Publication number SW-846, Update IIIA (April
1998).
GPO. Available from the Superintendent of Documents, U.S. Government
Printing Office, Washington, D.C. 20402, 202-783-3238202-512-1800:
Standard Industrial Classification Manual (1972), and 1977
Supplement, republished in 1983.
“Test Methods for Evaluating Solid Waste, Physical/Chemical
Methods”, USEPA Publication number SW-846 (Third Edition,
November, 1986), as amended by Updates I (July, 1992), II
(September, 1994), IIA (August, 1993), IIB (January, 1995), and III
(December, 1996) (Document Number 955-001-00000-1).
NACE. Available from the National Association of Corrosion Engineers, 1400
South Creek Dr., Houston, TX 77084, 713-492-0535:
“Control of External Corrosion on Metallic Buried, Partially Buried, or
Submerged Liquid Storage Systems”, NACE Recommended Practice
RP-02-85, approved March, 1985.
NFPA. Available from the National Fire Protection Association, Batterymarch
Park, Boston, MA 02269, 617-770-3000 or 800-344-3555:
“Flammable and Combustible Liquids Code” NFPA 30, issued July 17,
1987. Also available from ANSI.
NTIS. Available from the U.S. Department of Commerce, National Technical
Information Service, 5285 Port Royal Road, Springfield, VA 22161, 703-
487-4600 703-605-6000 or 800-553-6847:
APTI Course 415: Control of Gaseous Emissions, USEPA Publication
EPA-450/2-81-005, December, 1981.
“Generic Quality Assurance Project Plan for Land Disposal Restrictions
Program”, EPA/530-SW-87-011, March 15, 1987 (Document
number PB 88-170766).
“Guideline on Air Quality Models”, Revised 1986. (Document number
PB86-245-248 (Guideline) and PB88-150-958 (Supplement), also set
forth at 40 CFR 51, Appendix W).
36
“Method 164, Revision A, n-Hexane Extractable Material (HEM; Oil
and Grease) and Silica Gel Treated n-Hexane Extractable Material
(SGT-HEM; Non-polar Material) by Extraction and Gravimetry.”
Document number PB99-121949.
“Methods for Chemical Analysis of Water and Wastes”, Third Edition,
March, 1983 (Document number 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, Second
Edition”, EPA/530-R-93-007, March, 1993 (Document Number PB
93-169 365).
“Screening Procedures for Estimating the Air Quality Impact of
Stationary Sources”, October, 1992, Publication Number EPA-450/R-
92-019.
“Test Methods for Evaluating Solid Waste, Physical/Chemical
Methods”, USEPA Publication number SW-846 (Third Edition,
November, 1986), as amended by Updates I (July, 1992), II
(September, 1994), IIA (August, 1993), IIB (January, 1995), and III
(December, 1996), and IIIA (April 1998) (Document Number 955-
001-00000-1).
OECD. Organisation for Economic Co-operation and Development,
Environment Directorate, 2 rue Andre Pascal, 75775 Paris Cedex 16, France):
OECD Guideline for Testing of Chemicals, Method 301B: “CO
2
Evolution (Modified Sturm Test)”, adopted 17 July 1992.
Table 2.B of the Annex of OECD Council Decision C(88)90(Final) of
27 May 1988.
STI. Available from the Steel Tank Institute, 728 Anthony Trail, Northbrook,
IL 60062, 708-498-1980:
“Standard for Dual Wall Underground Steel Storage Tanks” (1986).
U.S. DOD. Available from the United States Department of Defense:
“DOD Ammunition and Explosive Safety Standards” (DOD 6055.9-
37
STD), as in effect on November 8, 1995.
The Motor Vehicle Inspection Report (DD Form 626), as in effect on
November 8, 1995.
Requisition Tracking Form (DD Form 1348), as in effect on November
8, 1995.
The Signature and Talley Tally Record (DD Form 1907), as in effect on
November 8, 1995.
Special Instructions for Motor Vehicle Drivers (DD Form 836), as in
effect on November 8, 1995.
USEPA. Available from United States Environmental Protection Agency,
Office of Drinking Water, State Programs Division, WH 550 E, Washington,
D.C. 20460:
“Technical Assistance Document: Corrosion, Its Detection and Control
in Injection Wells”, EPA 570/9-87-002, August, 1987.
USEPA. Available from Receptor Analysis Branch, USEPA (MD-14),
Research Triangle Park, NC 27711:
“Screening Procedures for Estimating the Air Quality Impact of
Stationary Sources, Revised”, October, 1992, Publication Number
EPA-450/R-92-019.
USEPA. Available from RCRA Information Center (RIC), 1235 Jefferson-
Davis Highway, first floor, Arlington, VA 22203 (Docket # F-94-IEHF-
FFFFF):
OECD Amber List of Wastes, Appendix 4 to the OECD Council
Decision C(92)39/FINAL (Concerning the Control of Transfrontier
Movements of Wastes Destined for Recovery Operations) (May
1993).
OECD Green List of Wastes, Appendix 3 to the OECD Council
Decision C(92)39/FINAL (Concerning the Control of Transfrontier
Movements of Wastes Destined for Recovery Operations) (May
1994).
OECD Red List of Wastes, Appendix 5 to the OECD Council
38
Decision C(92)39/FINAL (Concerning the Control of Transfrontier
Movements of Wastes Destined for Recovery Operations) (May
1993).
Table 2.B of the Annex of OECD Council Decision C(88)90(Final)
(May 27, 1988).
U.S. GSA. Available from the United States Government Services
Administration:
Government Bill of Lading (GBL) (GSA Standard Form 1109), as in
effect on November 8, 1995.
b)
Code of Federal Regulations. Available from the Superintendent of Documents, U.S.
Government Printing Office, Washington, D.C. 20401, 202-783-3238:
10 CFR 20, Appendix B (1998)
40 CFR 51.100(ii) (1998)
40 CFR 51, Appendix W (1998)
40 CFR 52.741, Appendix B (1998)
40 CFR 60 (1998)
40 CFR 61, Subpart V (1998)
40 CFR 63 (1998)
40 CFR 136 (1998), as corrected at 63 Fed. Reg. 38756 (July 20, 1998) and
63 Fed. Reg. 44146 (Aug. 18, 1998) and amended at 63 Fed. Reg. 50387
(Sep. 21, 1998), 64 Fed. Reg. 4975 (Feb. 2, 1999), 64 Fed. Reg. 26315
(May 14, 1999), and 64 Fed. Reg. 30417 (June 8, 1999)
40 CFR 142 (1998)
40 CFR 220 (1998)
40 CFR 232.2 (1998)
40 CFR 260.20 (1998)
39
40 CFR 264 (1998)
40 CFR 268.41 (1990)
40 CFR 268.Appendix IX (1998)
40 CFR 270.5 (1998)
40 CFR 302.4, 302.5, and 302.6 (1998)
40 CFR 761 (1998)
49 CFR 171 (1998)
49 CFR 173 (1998)
49 CFR 178 (1998)
c)
Federal Statutes
Section 3004 of the Resource Conservation and Recovery Act (42 USC 6901
et seq.), as amended through December 31, 1987.
Sections 201(v), 201(w), and 360b(j) of the Federal Food, Drug, and
Cosmetic Act (FFDCA; 21 USC 321(v), 321(w), and 512(j)), as amended
through October 25, 1994.
Section 1412 of the Department of Defense Authorization Act of 1986, Pub. L.
99-145, 50 USC 1521(j)(1) (1997).
d)
This Section incorporates no later editions or amendments.
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
TITLE 35: ENVIRONMENTAL PROTECTION
SUBTITLE G: WASTE DISPOSAL
CHAPTER I: POLLUTION CONTROL BOARD
SUBCHAPTER c: HAZARDOUS WASTE OPERATING REQUIREMENTS
PART 722
STANDARDS APPLICABLE TO GENERATORS OF HAZARDOUS WASTE
40
SUBPART A: GENERAL
Section
722.110
Purpose, Scope and Applicability
722.111
Hazardous Waste Determination
722.112
USEPA Identification Numbers
SUBPART B: THE MANIFEST
Section
722.120
General Requirements
722.121
Acquisition of Manifests
722.122
Number of Copies
722.123
Use of the Manifest
SUBPART C: PRE-TRANSPORT REQUIREMENTS
Section
722.130
Packaging
722.131
Labeling
722.132
Marking
722.133
Placarding
722.134
Accumulation Time
SUBPART D: RECORDKEEPING AND REPORTING
Section
722.140
Recordkeeping
722.141
Annual Reporting
722.142
Exception Reporting
722.143
Additional Reporting
722.144
Special Requirements for Generators of between 100 and 1000 kilograms per month
SUBPART E: EXPORTS OF HAZARDOUS WASTE
Section
722.150
Applicability
722.151
Definitions
722.152
General Requirements
722.153
Notification of Intent to Export
722.154
Special Manifest Requirements
722.155
Exception Report
722.156
Annual Reports
722.157
Recordkeeping
722.158
International Agreements
41
SUBPART F: IMPORTS OF HAZARDOUS WASTE
Section
722.160
Imports of Hazardous Waste
SUBPART G: FARMERS
Section
722.170
Farmers
SUBPART H: TRANSFRONTIER SHIPMENTS OF HAZARDOUS WASTE
FOR RECOVERY WITHIN THE OECD
Section
722.180
Applicability
722.181
Definitions
722.182
General Conditions
722.183
Notification and Consent
722.184
Tracking Document
722.185
Contracts
722.186
Provisions Relating to Recognized Traders
722.187
Reporting and Recordkeeping
722.189
OECD Waste Lists
722.Appendix A
Hazardous Waste Manifest
AUTHORITY: Implementing Sections 7.2 and 22.4 and authorized by Section 27 of the Environmental
Protection Act [415 ILCS 5/7.2, 22.4, and 27].
SOURCE: Adopted in R81-22, 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. 11236,
effective August 1, 1996; amended in R96-10/R97-3/R97-5 at 22 Ill. Reg. 603, effective December
16, 1997; amended in R97-21/R98-3/R98-5 at 22 Ill. Reg. 17950, effective September 28, 1998;
amended in R00-5 at 24 Ill. Reg. ________, effective ______________________.
42
SUBPART C: PRE-TRANSPORT REQUIREMENTS
Section 722.134
Accumulation Time
a)
Except as provided in subsection (d), (e), or (f) of this Section, a generator is exempt
from all the requirements in 35 Ill. Adm. Code 725.Subparts G and H, except for 35 Ill.
Adm. Code 725.211 and 725.214, and may accumulate hazardous waste on-site for
90 days or less without a permit or without having interim status, provided that the
following conditions are fulfilled:
1)
The waste is placed in or on one of the following:
A)
In containers, and the generator complies with 35 Ill. Adm. Code
725.Subparts I, AA, BB, and CC; or
B)
In tanks, and the generator complies with 35 Ill. Adm. Code
725.Subparts J, AA, BB, and CC, except 35 Ill. Adm. Code
725.297(c) and 725.300; or
C)
On drip pads, and the generator complies with 35 Ill. Adm. Code
725.Subpart W and maintains the following records at the facility:
i)
A description of the procedures that will be followed to ensure
that all wastes are removed from the drip pad and associated
collection system at least once every 90 days, and
ii)
Documentation of each waste removal, including the quantity of
waste removed from the drip pad and the sump or collection
system and the date and time of removal; or
D)
In containment buildings, and the generator complies with 35 Ill. Adm.
Code 725.Subpart DD (has placed its Professional Engineer (PE)
certification that the building complies with the design standards
specified in 35 Ill. Adm. Code 725.1101 in the facility’s operating
record prior to the date of initial operation of the unit). The owner or
operator shall maintain the following records at the facility:
i)
A written description of procedures to ensure that each waste
volume remains in the unit for no more than 90 days, a written
description of the waste generation and management practices
for the facility showing that they are consistent with respecting
43
the 90 day limit, and documentation that the procedures are
complied with; or
ii)
Documentation that the unit is emptied at least once every 90
days;
BOARD NOTE: The “in addition” hanging subsection that appears in the
Federal rules after 40 CFR 262.34(a)(1)(iv)(B) is in the introduction to
subsection (a) of this Section.
2)
The date upon which each period of accumulation begins is clearly marked and
visible for inspection on each container;
3)
While being accumulated on-site, each container and tank is labeled or marked
clearly with the words “Hazardous Waste”; and
4)
The generator complies with the requirements for treatment, storage, and
disposal facility owners or operators in 35 Ill. Adm. Code 725.Subparts C and
D and with 35 Ill. Adm. Code 725.116 and 728.107(a)(4).
b)
A generator that accumulates hazardous waste for more than 90 days is an operator of
a storage facility and is subject to the requirements of 35 Ill. Adm. Code 724 and 725
and the permit requirements of 35 Ill. Adm. Code 702, 703 and 705 unless the
generator has been granted an extension of the 90-day period. If hazardous wastes
must remain on-site for longer than 90 days due to unforeseen, temporary, and
uncontrollable circumstances, the generator may seek an extension of up to 30 days by
means of a variance or provisional variance, pursuant to Section 37 of the
Environmental Protection Act and 35 Ill. Adm. Code 180 (Agency procedural
regulations).
c)
Accumulation near the point of generation.
1)
A generator may accumulate as much as 55 gallons of hazardous waste or one
quart of acutely hazardous waste listed in 35 Ill. Adm. Code 721.133(e) in
containers at or near any point of generation where wastes initially accumulate
that is under the control of the operator of the process generating the waste
without a permit or interim status and without complying with subsection (a) of
this Section, provided the generator does the following:
A)
Complies with 35 Ill. Adm. Code 725.271, 725.272, and 725.273(a),;
and
B)
Marks the generator’s containers either with the words “Hazardous
44
Waste” or with other words that identify the contents of the containers.
2)
A generator that accumulates either hazardous waste or acutely hazardous
waste listed in 35 Ill. Adm. Code 721.133(e) in excess of the amounts listed in
subsection (c)(1) of this Section at or near any point of generation must, with
respect to that amount of excess waste, comply within three days with
subsection (a) of this Section or other applicable provisions of this Chapter.
During the three day period the generator must continue to comply with
subsection (c)(1) of this Section. The generator must mark the container
holding the excess accumulation of hazardous waste with the date the excess
amount began accumulating.
d)
A generator that generates greater than 100 kilograms but less than 1000 kilograms of
hazardous waste in a calendar month may accumulate hazardous waste on-site for 180
days or less without a permit or without having interim status provided that the following
conditions are fulfilled:
1)
The quantity of waste accumulated on-site never exceeds 6000 kilograms;
2)
The generator complies with the requirements of 35 Ill. Adm. Code
725.Subpart I (except 35 Ill. Adm. Code 725.276 and 725.278);
3)
The generator complies with the requirements of 35 Ill. Adm. Code 725.301;
4)
The generator complies with the requirements of subsections (a)(2) and (c)(3)
(a)(3) of this Section, 35 Ill. Adm. Code 725.Subpart C, and 35 Ill. Adm.
Code 728.107(a)(4) 728.107(a)(5); and
5)
The generator complies with the following requirements:
A)
At all times there must be at least one employee either on the premises
or on call (i.e., available to respond to an emergency by reaching the
facility within a short period of time) with the responsibility for
coordinating all emergency response measures specified in subsection
(d)(5)(D) of this Section. The employee is the emergency coordinator.
B)
The generator shall post the following information next to the telephone:
i)
The name and telephone number of the emergency coordinator;
ii)
Location of fire extinguishers and spill control material and, if
present, fire alarm; and
45
iii)
The telephone number of the fire department, unless the facility
has a direct alarm.
C)
The generator shall ensure that all employees are thoroughly familiar
with proper waste handling and emergency procedures, relevant to their
responsibilities during normal facility operations and emergencies.
D)
The emergency coordinator or designee shall respond to any
emergencies that arise. The applicable responses are as follows:
i)
In the event of a fire, call the fire department or attempt to
extinguish it using a fire extinguisher;
ii)
In the event of a spill, contain the flow of hazardous waste to
the extent possible and, as soon as is practicable, clean up the
hazardous waste and any contaminated materials or soil;
iii)
In the event of a fire, explosion, or other release that could
threaten human health outside the facility, or when the generator
has knowledge that a spill has reached surface water, the
generator shall immediately notify the National Response Center
(using its 24-hour toll free number 800-424-8802). The report
must include the following information: the name, address, and
USEPA identification number (Section 722.112 of this Part) of
the generator; the date, time, and type of incident (e.g., spill or
fire); the quantity and type of hazardous waste involved in the
incident; the extent of injuries, if any; and the estimated quantity
and disposition of recoverable materials, if any.
e)
A generator that generates greater than 100 kilograms but less than 1000 kilograms of
hazardous waste in a calendar month and that must transport the waste or offer the
waste for transportation over a distance of 200 miles or more for off-site treatment,
storage, or disposal may accumulate hazardous waste on-site for 270 days or less
without a permit or without having interim status, provided that the generator complies
with the requirements of subsection (d) of this Section.
f)
A generator that generates greater than 100 kilograms but less than 1000 kilograms of
hazardous waste in a calendar month and that accumulates hazardous waste in quantities
exceeding 6000 kg or accumulates hazardous waste for more than 180 days (or for
more than 270 days if the generator must transport the waste or offer the waste for
transportation over a distance of 200 miles or more) is an operator of a storage facility
and is subject to the requirements of 35 Ill. Adm. Code 724 and 725 and the permit
requirements of 35 Ill. Adm. Code 703, unless the generator has been granted an
46
extension to the 180-day (or 270-day if applicable) period. If hazardous wastes must
remain on-site for longer than 180 days (or 270 days if applicable) due to unforeseen,
temporary, and uncontrollable circumstances, the generator may seek an extension of
up to 30 days by means of variance or provisional variance pursuant to Section 37 of
the Environmental Protection Act.
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
TITLE 35: ENVIRONMENTAL PROTECTION
SUBTITLE G: WASTE DISPOSAL
CHAPTER I: POLLUTION CONTROL BOARD
SUBCHAPTER c: HAZARDOUS WASTE OPERATING REQUIREMENTS
PART 724
STANDARDS FOR OWNERS AND OPERATORS OF HAZARDOUS WASTE
TREATMENT, STORAGE, AND DISPOSAL FACILITIES
SUBPART A: GENERAL PROVISIONS
Section
724.101
Purpose, Scope, and Applicability
724.103
Relationship to Interim Status Standards
SUBPART B: GENERAL FACILITY STANDARDS
Section
724.110
Applicability
724.111
Identification Number
724.112
Required Notices
724.113
General Waste Analysis
724.114
Security
724.115
General Inspection Requirements
724.116
Personnel Training
724.117
General Requirements for Ignitable, Reactive or Incompatible Wastes
724.118
Location Standards
724.119
Construction Quality Assurance Program
SUBPART C: PREPAREDNESS AND PREVENTION
Section
724.130
Applicability
724.131
Design and Operation of Facility
724.132
Required Equipment
724.133
Testing and Maintenance of Equipment
724.134
Access to Communications or Alarm System
47
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 CARE
Section
724.210
Applicability
724.211
Closure Performance Standard
48
724.212
Closure Plan; Amendment of Plan
724.213
Closure; Time Allowed For Closure
724.214
Disposal or Decontamination of Equipment, Structures and Soils
724.215
Certification of Closure
724.216
Survey Plat
724.217
Post-closure Care and Use of Property
724.218
Post-Closure Care Plan; Amendment of Plan
724.219
Post-closure Notices
724.220
Certification of Completion of Post-closure Care
SUBPART H: FINANCIAL REQUIREMENTS
Section
724.240
Applicability
724.241
Definitions of Terms As Used In This Subpart
724.242
Cost Estimate for Closure
724.243
Financial Assurance for Closure
724.244
Cost Estimate for Post-closure Care
724.245
Financial Assurance for Post-closure Care
724.246
Use of a Mechanism for Financial Assurance of Both Closure and Post-closure Care
724.247
Liability Requirements
724.248
Incapacity of Owners or Operators, Guarantors or Financial Institutions
724.251
Wording of the Instruments
SUBPART I: USE AND MANAGEMENT OF CONTAINERS
Section
724.270
Applicability
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
49
724.295
Inspections
724.296
Response to Leaks or Spills and Disposition of Leaking or unfit-for-use Tank Systems
724.297
Closure and Post-Closure Care
724.298
Special Requirements for Ignitable or Reactive Waste
724.299
Special Requirements for Incompatible Wastes
724.300
Air Emission Standards
SUBPART K: SURFACE IMPOUNDMENTS
Section
724.320
Applicability
724.321
Design and Operating Requirements
724.322
Action Leakage Rate
724.323
Response Actions
724.326
Monitoring and Inspection
724.327
Emergency Repairs; Contingency Plans
724.328
Closure and Post-closure Care
724.329
Special Requirements for Ignitable or Reactive Waste
724.330
Special Requirements for Incompatible Wastes
724.331
Special Requirements for Hazardous Wastes F020, F021, F022, F023, F026 and
F027
724.332
Air Emission Standards
SUBPART L: WASTE PILES
Section
724.350
Applicability
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
50
724.379
Recordkeeping
724.380
Closure and Post-closure Care
724.381
Special Requirements for Ignitable or Reactive Waste
724.382
Special Requirements for Incompatible Wastes
724.383
Special Requirements for Hazardous Wastes F020, F021, F022, F023, F026 and
F027
SUBPART N: LANDFILLS
Section
724.400
Applicability
724.401
Design and Operating Requirements
724.402
Action Leakage Rate
724.403
Monitoring and Inspection
724.404
Response Actions
724.409
Surveying and Recordkeeping
724.410
Closure and Post-closure Care
724.412
Special Requirements for Ignitable or Reactive Waste
724.413
Special Requirements for Incompatible Wastes
724.414
Special Requirements for Bulk and Containerized Liquids
724.415
Special Requirements for Containers
724.416
Disposal of Small Containers of Hazardous Waste in Overpacked Drums (Lab Packs)
724.417
Special Requirements for Hazardous Wastes F020, F021, F022, F023, F026 and
F027
SUBPART O: INCINERATORS
Section
724.440
Applicability
724.441
Waste Analysis
724.442
Principal Organic Hazardous Constituents (POHCs)
724.443
Performance Standards
724.444
Hazardous Waste Incinerator Permits
724.445
Operating Requirements
724.447
Monitoring and Inspections
724.451
Closure
SUBPART S: CORRECTIVE ACTION FOR SOLID WASTE MANAGEMENT
UNITS
Section
724.652
Corrective Action Management Units
724.653
Temporary Units
724.654
Staging Piles
51
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
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
52
724.965
Reporting Requirements
SUBPART CC: AIR EMISSION STANDARDS FOR TANKS, SURFACE
IMPOUNDMENTS, AND CONTAINERS
Section
724.980
Applicability
724.981
Definitions
724.982
Standards: General
724.983
Waste Determination Procedures
724.984
Standards: Tanks
724.985
Standards: Surface Impoundments
724.986
Standards: Containers
724.987
Standards: Closed-vent Systems and Control Devices
724.988
Inspection and Monitoring Requirements
724.989
Recordkeeping Requirements
724.990
Reporting Requirements
724.991
Alternative Control Requirements for Tanks
SUBPART DD: CONTAINMENT BUILDINGS
Section
724.1100
Applicability
724.1101
Design and operating standards
724.1102
Closure and Post-closure Care
SUBPART EE: HAZARDOUS WASTE MUNITIONS AND EXPLOSIVES
STORAGE
Section
724.1200
Applicability
724.1201
Design and Operating Standards
724.1202
Closure and Post-Closure Care
724.Appendix A
Recordkeeping Instructions
724.Appendix B
EPA Report Form and Instructions (Repealed)
724.Appendix D
Cochran’s Approximation to the Behrens-Fisher Student’s T-Test
724.Appendix E
Examples of Potentially Incompatible Waste
724.Appendix I
Groundwater Monitoring List
AUTHORITY: Implementing Sections 7.2 and 22.4 and authorized by Section 27 of the Environmental
Protection Act [415 ILCS 5/7.2, 22.4, and 27].
SOURCE: Adopted in R82-19, 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;
53
amended in R86-28 at 11 Ill. Reg. 6138, effective March 24, 1987; amended in R86-28 at 11 Ill. Reg.
8684, effective April 21, 1987; amended in R86-46 at 11 Ill. Reg. 13577, effective August 4, 1987;
amended in R87-5 at 11 Ill. Reg. 19397, effective November 12, 1987; amended in R87-39 at 12 Ill.
Reg. 13135, effective July 29, 1988; amended in R88-16 at 13 Ill. Reg. 458, effective December 28,
1988; amended in R89-1 at 13 Ill. Reg. 18527, effective November 13, 1989; amended in R90-2 at
14 Ill. Reg. 14511, effective August 22, 1990; amended in R90-10 at 14 Ill. Reg. 16658, effective
September 25, 1990; amended in R90-11 at 15 Ill. Reg. 9654, effective June 17, 1991; amended in
R91-1 at 15 Ill. Reg. 14572, effective October 1, 1991; amended in R91-13 at 16 Ill. Reg. 9833,
effective June 9, 1992; amended in R92-1 at 16 Ill. Reg. 17702, effective November 6, 1992;
amended in R92-10 at 17 Ill. Reg. 5806, effective March 26, 1993; amended in R93-4 at 17 Ill. Reg.
20830, effective November 22, 1993; amended in R93-16 at 18 Ill. Reg. 6973, effective April 26,
1994; amended in R94-7 at 18 Ill. Reg. 12487, effective July 29, 1994; amended in R94-17 at 18 Ill.
Reg. 17601, effective November 23, 1994; amended in R95-6 at 19 Ill. Reg. 9951, effective June 27,
1995; amended in R95-20 at 20 Ill. Reg. 11244, effective August 1, 1996; amended in R96-10/R97-
3/R97-5 at 22 Ill. Reg. 636, effective December 16, 1997; amended in R98-12 at 22 Ill. Reg. 7638,
effective April 15, 1998; amended in R97-21/R98-3/R98-5 at 22 Ill. Reg. 17972, effective September
28, 1998; amended in R98-21/R99-2/R99-7 at 23 Ill. Reg. 2186, effective January 19, 1999;
amended in R99-15 at 23 Ill. Reg. 9437, effective July 26, 1999; amended in R00-5 at 24 Ill. Reg.
________, effective ______________________.
SUBPART AA: AIR EMISSION STANDARDS FOR PROCESS VENTS
Section 724.931
Definitions
As used in this Subpart, all terms not defined in the this Subpart have the meaning given them in the
Resource Conservation and Recovery Act and 35 Ill. Adm. Code 720 through 726.
“Air stripping operation” is means a desorption operation employed to transfer one or
more volatile components from a liquid mixture into a gas (air) either with or without the
application of heat to the liquid. Packed towers, spray towers and bubble-cap, sieve,
or valve-type plate towers are among the process configurations used for contacting the
air and a liquid.
“Bottoms receiver” means a container or tank used to receive and collect the heavier
bottoms fractions of the distillation feed stream that remain in the liquid phase.
“Btu” means British thermal unit.
“Closed-vent system” means a system that is not open to the atmosphere and that is
composed of piping, connections, and, if necessary, flow-inducing devices that transport
gas or vapor from a piece or pieces of equipment to a control device.
54
“Condenser” means a heat-transfer device that reduces a thermodynamic fluid from its
vapor phase to its liquid phase.
“Connector” means flanged, screwed, welded or other joined fittings used to connect
two pipelines or a pipeline and a piece of equipment. For the purposes of reporting and
recordkeeping, “connector” means flanged fittings that are not covered by insulation or
other materials that prevent location of the fittings.
“Continuous recorder” means a data-recording device recording an instantaneous data
value at least once every 15 minutes.
“Control device” means an enclosed combustion device, vapor recovery system, or
flare. Any device the primary function of which is the recovery or capture of solvents or
other organics for use, reuse, or sale (e.g., a primary condenser on a solvent recovery
unit) is not a control device.
“Control device shutdown” means the cessation of operation of a control device for any
purpose.
“Distillate receiver” means a container or tank used to receive and collect liquid material
(condensed) from the overhead condenser of a distillation unit and from which the
condensed liquid is pumped to larger storage tanks or other process units.
“Distillation operation” means an operation, either batch or continuous, separating one
or more feed stream(s) into two or more exit streams, each exit stream having
component concentrations different from those in the feed stream(s). The separation is
achieved by the redistribution of the components between the liquid and vapor phase as
they approach equilibrium within the distillation unit.
“Double block and bleed system” means two block valves connected in series with a
bleed valve or line that can vent the line between the two block valves.
“Equipment” means each valve, pump, compressor, pressure relief device, sampling
connection system, open-ended valve or line, or flange or other connector, and any
control devices or systems required by this Subpart.
“First attempt at repair” means to take rapid action for the purpose of stopping or
reducing leakage of organic material to the atmosphere using best practices.
“Flame zone” means the portion of the combustion chamber in a boiler occupied by the
flame envelope.
“Flow indicator” means a device that indicates whether gas flow is present in a vent
55
stream.
“Fractionation operation” means a distillation operation or method used to separate a
mixture of several volatile components of different boiling points in successive stages,
each stage removing from the mixture some proportion of one of the components.
“ft” means foot.
“h” means hour.
“Hazardous waste management unit shutdown” means a work practice or operational
procedure that stops operation of a hazardous waste management unit or part of a
hazardous waste management unit. An unscheduled work practice or operational
procedure that stops operation of a hazardous waste management unit or part of a
hazardous waste management unit for less than 24 hours is not a hazardous waste
management unit shutdown. The use of spare equipment and technically feasible
bypassing of equipment without stopping operation are not hazardous waste
management unit shutdowns.
“Hot well” means a container for collecting condensate as in a steam condenser serving
a vacuum-jet or steam-jet ejector.
“In gas-vapor service” means that the piece of equipment contains or contacts a
hazardous waste stream that is in the gaseous state at operating conditions.
“In heavy liquid service” means that the piece of equipment is not in gas-vapor service
or in light liquid service.
“In light liquid service” means that the piece of equipment contains or contacts a waste
stream where the vapor pressure of one or more of the organic components in the
stream is greater than 0.3 kilopascals (kPa) at 20° C, the total concentration of the pure
organic components having a vapor pressure greater than 0.3 kPa at 20° C is equal to
or greater than 20 percent by weight, and the fluid is a liquid at operating conditions.
“In situ sampling systems” means nonextractive samplers or in-line samplers.
“In vacuum service” means that equipment is operating at an internal pressure that is at
least 5 kPa below ambient pressure.
“Kg” means kilogram.
“kPa” means kilopascals.
56
“lb” means pound.
“m” means meter.
“Mg” means Megagrams, or metric tonnes.
“MJ” means Megajoules, or ten to the sixth Joules.
“MW” means Megawatts.
“Malfunction” means any sudden failure of a control device or a hazardous waste
management unit or failure of a hazardous waste management unit to operate in a normal
or usual manner, so that organic emissions are increased.
“Open-ended valve or line” means any valve, except a pressure relief valves valve,
having that has one side of the valve seat in contact with process fluid hazardous waste
and one side open to the atmosphere, either directly or through open piping.
“ppmv” means parts per million by volume.
“ppmw” means parts per million by weight.
“Pressure release” means the emission of materials resulting from the system pressure
being greater than the set pressure of the pressure relief device.
“Process heater” means a device that transfers heat liberated by burning fuel to fluids
contained in tubes, including all fluids except water that are heated to produce steam.
“Process vent” means any open-ended pipe or stack that is vented to the atmosphere
either directly, through a vacuum-producing system, or through a tank (e.g., distillate
receiver, condenser, bottoms receiver, surge control tank, separator tank, or hot well)
associated with hazardous waste distillation, fractionation, thin-film evaporation, solvent
extraction, or air or steam stripping operations.
“Repaired” means that equipment is adjusted, or otherwise altered, to eliminate a leak.
“s” means second.
“Sampling connection system” means an assembly of equipment within a process or
waste management unit that is used during periods of representative operation to take
samples of the process or waste fluid. Equipment that is used to take non-routine grab
samples is not considered a sampling connection system.
57
“scm” means standard cubic meter.
“scft” means standard cubic foot.
“Sensor” means a device that measures a physical quantity or the change in a physical
quantity, such as temperature, pressure, flow rate, pH, or liquid level.
“Separator tank” means a device used for separation of two immiscible liquids.
“Solvent extraction operation” means an operation or method of separation in which a
solid or solution is contracted with a liquid solvent (the two being mutually insoluble) to
preferentially dissolve and transfer one or more components into the solvent.
“Startup” means the setting in operation of a hazardous waste management unit or
control device for any purpose.
“Steam stripping operation” means a distillation operation in which vaporization of the
volatile constituents of a liquid mixture takes place by the introduction of steam directly
in to the charge.
“Surge control tank” means a large-sized pipe or storage reservoir sufficient to contain
the surging liquid discharge of the process tank to which it is connected.
“Thin-film evaporation operation” means a distillation operation that employs a heating
surface consisting of a large diameter tube that may be either straight or tapered,
horizontal or vertical. Liquid is spread on the tube wall by a rotating assembly of blades
that maintain a close clearance from the wall or actually ride on the film of liquid on the
wall.
“USDOT” means the United States Department of Transportation.
“Vapor incinerator” means any enclosed combustion device that is used for destroying
organic compounds and does not extract energy in the form of steam or process heat.
“Vented” means discharged through an opening, typically an open-ended pipe or stack,
allowing the passage of a stream of liquids, gases, or fumes into the atmosphere. The
passage of liquids, gases, or fumes is caused by mechanical means, such as
compressors or vacuum-producing systems, or by process-related means, such as
evaporation produced by heating, and not caused by tank loading and unloading
(working losses) or by natural means, such as diurnal temperature changes.
“yr” means year.
58
(Source: Amended at 24 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 to owners and operators of all facilities that
treat, store, or dispose of hazardous waste in tanks, surface impoundments, or
containers subject to Subpart I, J, or K of this Part, except as Section 724.101 and
subsection (b) of this Section provide otherwise.
b)
The requirements of this Subpart do not apply to the following waste management units
at the facility:
1)
A waste management unit that holds hazardous waste placed in the unit before
December 6, 1996, and in which no hazardous waste is added to the unit on or
after December 6, 1996.
2)
A container that has a design capacity less than or equal to 0.1 m
3
(3.5 ft
3
or
26.4 gal).
3)
A tank in which an owner or operator has stopped adding hazardous waste and
the owner or operator has begun implementing or completed closure pursuant
to an approved closure plan.
4)
A surface impoundment in which an owner or operator has stopped adding
hazardous waste (except to implement an approved closure plan) and the
owner or operator has begun implementing or completed closure pursuant to an
approved closure plan.
5)
A waste management unit that is used solely for on-site treatment or storage of
hazardous waste that is generated placed in the unit as the a result of
implementing remedial activities required pursuant to the Act or Board
regulations or under the corrective action authorities of RCRA section 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 USC 2011 et seq.) and the Nuclear Waste Policy
Act.
59
7)
A hazardous waste management unit that the owner or operator certifies is
equipped with and operating air emission controls in accordance with the
requirements of an applicable federal Clean Air Act regulation codified under
40 CFR 60, 61, or 63. For the purpose of complying with this subsection
(b)(7), a tank for which the air emission control includes an enclosure, as
opposed to a cover, must be in compliance with the enclosure and control
device requirements of Section 724.984(i), except as provided in Section
724.982(c)(5).
8)
A tank that has a process vent, as defined in 35 Ill. Adm. Code 724.931.
c)
For the owner and operator of a facility subject to this Subpart and that received a final
RCRA permit prior to December 6, 1996, the requirements of this Subpart shall 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. Until such the
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 structural derivative of hydrogen
peroxide where one or both of the hydrogen atoms has been replaced by an
organic radical.
2)
The owner or operator prepares documentation, in accordance with Section
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 by the organic peroxide manufacturing process or
60
processes meeting the conditions of subsection (d)(1) of this Section.
3)
The owner or operator notifies the Agency in writing that hazardous waste
generated by an organic peroxide manufacturing process or processes meeting
the conditions of subsection (d)(1) of this Section are managed at the facility in
tanks or containers meeting the conditions of subsection (d)(2) of this Section.
The notification must state the name and address of the facility and be signed
and dated by an authorized representative of the facility owner or operator.
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
Section 724.983
Waste Determination Procedures
a)
Waste determination procedure for average volatile organic (VO) concentration of a
hazardous waste at the point of waste origination.
1)
An owner or operator shall determine the average VO concentration at the
point of waste origination for each hazardous waste placed in a waste
management unit exempted under the provisions of Section 724.982(c)(1) from
using air emission controls in accordance with standards specified in Section
724.984 through Section 724.987, as applicable to the waste management unit.
A) An owner or operator shall make an initial determination of the average
VO concentration of the waste stream before the first time any portion
of the material in the hazardous waste stream is placed in a waste
management unit exempted under the provisions of Section
724.982(c)(1) from using air emission controls. Thereafter, an owner
or operator shall make an initial determination of the average VO
concentration of the waste stream for each averaging period that a
hazardous waste is managed in the unit.
B) An owner or operator shall perform a new waste determination
whenever changes to the source generating the waste stream are
reasonably likely to cause the average VO concentration of the
hazardous waste to increase to a level that is equal to or greater than the
applicable VO concentration limits specified in Section 724.982.
2)
For a waste determination that is required by subsection (a)(1) of this Section,
the average VO concentration of a hazardous waste at the point of waste
origination shall must be determined in accordance with the procedures
specified in 35 Ill. Adm. Code 725.984(a)(2) through (a)(4).
b)
Waste determination procedures for treated hazardous waste.
61
1)
An owner or operator shall perform the applicable waste determination for each
treated hazardous waste placed in a waste management unit exempted under
the provisions of Section 724.982(c)(2)(A) through (c)(2)(F from using air
emission controls in accordance with standards specified in Sections 724.984
through 724.987, as applicable to the waste management unit.
A) An owner or operator shall make an initial determination of the average
VO concentration of the waste stream before the first time any portion
of the material in the treated waste stream is placed in the exempt waste
management unit. Thereafter, an owner or operator shall update the
information used for the waste determination at least once every 12
months following the date of the initial waste determination.
B) An owner or operator shall perform a new waste determination
whenever changes to the process generating or treating the waste
stream are reasonably likely to cause the average VO concentration of
the hazardous waste to increase to such a level that the applicable
treatment conditions specified in Section 724.982(c)(2) are not
achieved.
2)
The waste determination for a treated hazardous waste shall must be performed
in accordance with the procedures specified in 35 Ill. Adm. Code
725.984(b)(2) through (b)(9), as applicable to the treated hazardous waste.
c)
Procedure to determine the maximum organic vapor pressure of a hazardous waste in a
tank.
1)
An owner or operator shall determine the maximum organic vapor pressure for
each hazardous waste placed in a tank using Tank Level 1 controls in
accordance with standards specified in Section 724.984(c).
2)
The maximum organic vapor pressure of the hazardous waste may be
determined in accordance with the procedures specified in 35 Ill. Adm. Code
725.984(c)(2) through (c)(4).
d)
The procedure for determining no detectable organic emissions for the purpose of
complying with this Subpart must be conducted in accordance with the procedures
specified in 35 Ill. Adm. Code 725.984(d).
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
62
Section 724.984
Standards: Tanks
a)
The provisions of this Section apply to the control of air pollutant emissions from tanks
for which Section 724.982(b) references the use of this Section for such air emission
control.
b)
The owner or operator shall control air pollutant emissions from each tank subject to
this Section in accordance with the following requirements, as applicable:
1)
For a tank that manages hazardous waste that meets all of the conditions
specified in subsections (b)(1)(A) through (b)(1)(C) of this Section, the owner
or operator shall control air pollutant emissions from the tank in accordance
with the Tank Level 1 controls specified in subsection (c) of this Section or the
Tank Level 2 controls specified in subsection (d) of this Section.
A)
The hazardous waste in the tank has a maximum organic vapor pressure
that is less than the maximum organic vapor pressure limit for the tank’s
design capacity category as follows:
i)
For a tank design capacity equal to or greater than 151 m
3
(39,900 gal), the maximum organic vapor pressure limit for the
tank is 5.2 kPa (0.75 psig).
ii)
For a tank design capacity equal to or greater than 75 m
3
(19,800 gal) but less than 151 m
3
(39,900 gal), the maximum
organic vapor pressure limit for the tank is 27.6 kPa (4.00
psig).
iii)
For a tank design capacity less than 75 m
3
(19,800 gal), the
maximum organic vapor pressure limit for the tank is 76.6 kPa
(11.1 psig).
B)
The hazardous waste in the tank is not heated by the owner or operator
to a temperature that is greater than the temperature at which the
maximum organic vapor pressure of the hazardous waste is determined
for the purpose of complying with subsection (b)(1)(A) of this Section.
C)
The owner or operator does not treat the hazardous waste in the tank is
not treated by the owner or operator using a waste stabilization
process, as defined in 35 Ill. Adm. Code 725.981.
2)
For a tank that manages hazardous waste that does not meet all of the
conditions specified in subsections (b)(1)(A) through (b)(1)(C) of this Section,
63
the owner or operator shall control air pollutant emissions from the tank by
using Tank Level 2 controls in accordance with the requirements of subsection
(d) of this Section. Examples of tanks required to use Tank Level 2 controls
include a tank used for a waste stabilization process and a tank for which the
hazardous waste in the tank has a maximum organic vapor pressure that is equal
to or greater than the maximum organic vapor pressure limit for the tank’s
design capacity category as specified in subsection (b)(1)(A) of this Section.
c)
Owners and operators controlling air pollutant emissions from a tank using Tank Level 1
controls must meet the requirements specified in subsections (c)(1) through (c)(4) of this
Section:
1)
The owner or operator shall determine the maximum organic vapor pressure for
a hazardous waste to be managed in the tank using Tank Level 1 controls
before the first time the hazardous waste is placed in the tank. The maximum
organic vapor pressure must be determined using the procedures specified in
Section 724.983(c). Thereafter, the owner or operator shall perform a new
determination whenever changes to the hazardous waste managed in the tank
could potentially cause the maximum organic vapor pressure to increase to a
level that is equal to or greater than the maximum organic vapor pressure limit
for the tank design capacity category specified in subsection (b)(1)(A) of this
Section, as applicable to the tank.
2)
The tank must be equipped with a fixed roof designed to meet the following
specifications:
A)
The fixed roof and its closure devices must be designed to form a
continuous barrier over the entire surface area of the hazardous waste in
the tank. The fixed roof may be a separate cover installed on the tank
(e.g., a removable cover mounted on an open-top tank) or may be an
integral part of the tank structural design (e.g., a horizontal cylindrical
tank equipped with a hatch).
B)
The fixed roof must be installed in such a manner such that there are no
visible cracks, holes, gaps, or other open spaces between roof section
joints or between the interface of the roof edge and the tank wall.
C)
Either of the following must be true of each opening in the fixed roof and
of any manifold system associated with the fixed roof:
i)
The opening or manifold system is equipped with a closure
device designed to operate such so that when the closure
device is secured in the closed position there are no visible
64
cracks, holes, gaps, or other open spaces in the closure device
or between the perimeter of the opening and the closure device;
or
ii)
The opening or manifold system is connected by a closed-vent
system that is vented to a control device. The control device
must remove or destroy organics in the vent stream, and it must
be operating whenever hazardous waste is managed in the tank,
except as provided for in subsection (c)(2)(E) of this Section.
D)
The fixed roof and its closure devices must be made of suitable
materials that will minimize exposure of the hazardous waste to the
atmosphere, to the extent practical, and will maintain the integrity of the
fixed roof and closure devices throughout their intended service life.
Factors to be considered when selecting the materials for and designing
the fixed roof and closure devices must include the following: the
organic vapor permeability; the effects of any contact with the
hazardous waste or its vapors managed in the tank; the effects of
outdoor exposure to wind, moisture, and sunlight; and the operating
practices used for the tank on which the fixed roof is installed.
E)
The control device operated pursuant to subsection (c)(2)(C) of this
Section needs not remove or destroy organics in the vent stream under
the following conditions:
i)
During periods when it is necessary to provide access to the
tank for performing the activities of subsection (c)(2)(E)(ii) of
this Section, venting of the vapor headspace underneath the
fixed roof to the control device is not required, opening of
closure devices is allowed, and removal of the fixed roof is
allowed. Following completion of the activity, the owner or
operator shall promptly secure the closure device in the closed
position or reinstall the cover, as applicable, and resume
operation of the control device; and
ii)
During periods of routine inspection, maintenance, or other
activities needed for normal operations, and for removal of
accumulated sludge or other residues from the bottom of the
tank.
BOARD NOTE: Subsections (c)(2)(E)(i) and (c)(2)(E)(ii) are derived
from 40 CFR 264.1084(c)(2)(iii)(B)(
1
) and (c)(2)(iii)(B)(
2
), which the
Board has codified here to comport with Illinois Administrative Code
65
format requirements.
3)
Whenever a hazardous waste is in the tank, the fixed roof must be installed with
each closure device secured in the closed position, except as follows:
A)
Opening of closure devices or removal of the fixed roof is allowed at
the following times:
i)
To provide access to the tank for performing routine inspection,
maintenance, or other activities needed for normal operations.
Examples of such activities include those times when a worker
needs to open a port to sample the liquid in the tank, or when a
worker needs to open a hatch to maintain or repair equipment.
Following completion of the activity, the owner or operator shall
promptly secure the closure device in the closed position or
reinstall the cover, as applicable, to the tank.
ii)
To remove accumulated sludge or other residues from the
bottom of the tank.
B)
Opening of a spring-loaded pressure-vacuum relief valve, conservation
vent, or similar type of pressure relief device which that vents to the
atmosphere is allowed during normal operations for the purpose of
maintaining the tank internal pressure in accordance with the tank design
specifications. The device must be designed to operate with no
detectable organic emissions when the device is secured in the closed
position. The settings at which the device opens must be established
such so that the device remains in the closed position whenever the tank
internal pressure is within the internal pressure operating range
determined by the owner or operator based on the tank manufacturer
recommendations, applicable regulations, fire protection and prevention
codes, standard engineering codes and practices, or other requirements
for the safe handling of flammable, ignitable, explosive, reactive, or
hazardous materials. Examples of normal operating conditions that may
require these devices to open are during those times when the tank
internal pressure exceeds the internal pressure operating range for the
tank as a result of loading operations or diurnal ambient temperature
fluctuations.
C)
Opening of a safety device, as defined in 35 Ill. Adm. Code 725.981, is
allowed at any time conditions require doing so to avoid an unsafe
condition.
66
4)
The owner or operator shall inspect the air emission control equipment in
accordance with the following requirements.
A)
The fixed roof and its closure devices must be visually inspected by the
owner or operator to check for defects that could result in air pollutant
emissions. Defects include, but are not limited to, visible cracks, holes,
or gaps in the roof sections or between the roof and the tank wall;
broken, cracked, or otherwise damaged seals or gaskets on closure
devices; and broken or missing hatches, access covers, caps, or other
closure devices.
B)
The owner or operator shall perform an initial inspection of the fixed
roof and its closure devices on or before the date that the tank becomes
subject to this Section. Thereafter, the owner or operator shall perform
the inspections at least once every year except under the special
conditions provided for in subsection (l) of this Section.
C)
In the event that a defect is detected, the owner or operator shall repair
the defect in accordance with the requirements of subsection (k) of this
Section.
D)
The owner or operator shall maintain a record of the inspection in
accordance with the requirements specified in Section 724.989(b).
d)
Owners and operators controlling air pollutant emissions from a tank using Tank Level 2
controls must use one of the following tanks:
1)
A fixed-roof tank equipped with an internal floating roof in accordance with the
requirements specified in subsection (e) of this Section;
2)
A tank equipped with an external floating roof in accordance with the
requirements specified in subsection (f) of this Section;
3)
A tank vented through a closed-vent system to a control device in accordance
with the requirements specified in subsection (g) of this Section;
4)
A pressure tank designed and operated in accordance with the requirements
specified in subsection (h) of this Section; or
5)
A tank located inside an enclosure that is vented through a closed-vent system
to an enclosed combustion control device in accordance with the requirements
specified in subsection (i) of this Section.
67
e)
The owner or operator that controls air pollutant emissions from a tank using a fixed
roof with an internal floating roof shall meet the requirements specified in subsections
(e)(1) through (e)(3) of this Section.
1)
The tank must be equipped with a fixed roof and an internal floating roof in
accordance with the following requirements:
A)
The internal floating roof must be designed to float on the liquid surface
except when the floating roof must be supported by the leg supports.
B)
The internal floating roof must be equipped with a continuous seal
between the wall of the tank and the floating roof edge that meets either
of the following requirements:
i)
A single continuous seal that is either a liquid-mounted seal or a
metallic shoe seal, as defined in 35 Ill. Adm. Code 725.981; or
ii)
Two continuous seals mounted one above the other. The lower
seal may be a vapor-mounted seal.
C)
The internal floating roof must meet the following specifications:
i)
Each opening in a noncontact internal floating roof except for
automatic bleeder vents (vacuum breaker vents) and the rim
space vents is to provide a projection below the liquid surface.
ii)
Each opening in the internal floating roof must be equipped with
a gasketed cover or a gasketed lid except for leg sleeves,
automatic bleeder vents, rim space vents, column wells, ladder
wells, sample wells, and stub drains.
iii)
Each penetration of the internal floating roof for the purpose of
sampling must have a slit fabric cover that covers at least 90
percent of the opening.
iv)
Each automatic bleeder vent and rim space vent must be
gasketed.
v)
Each penetration of the internal floating roof that allows for
passage of a ladder must have a gasketed sliding cover.
vi)
Each penetration of the internal floating roof that allows for
passage of a column supporting the fixed roof must have a
68
flexible fabric sleeve seal or a gasketed sliding cover.
2)
The owner or operator shall operate the tank in accordance with the following
requirements:
A)
When the floating roof is resting on the leg supports, the process of
filling, emptying, or refilling must be continuous and must be completed
as soon as practical.
B)
Automatic bleeder vents are to be set closed at all times when the roof
is floating, except when the roof is being floated off or is being landed
on the leg supports.
C)
Prior to filling the tank, each cover, access hatch, gauge float well or lid
on any opening in the internal floating roof must be bolted or fastened
closed (i.e., no visible gaps). Rim space vents must be set to open only
when the internal floating roof is not floating or when the pressure
beneath the rim exceeds the manufacturer’s recommended setting.
3)
The owner or operator shall inspect the internal floating roof in accordance with
the procedures specified as follows:
A)
The floating roof and its closure devices must be visually inspected by
the owner or operator to check for defects that could result in air
pollutant emissions. Defects include, but are not limited to, any of the
following: when the internal floating roof is not floating on the surface of
the liquid inside the tank; when liquid has accumulated on top of the
internal floating roof; when any portion of the roof seals have detached
from the roof rim; when holes, tears, or other openings are visible in the
seal fabric; when the gaskets no longer close off the hazardous waste
surface from the atmosphere; or when the slotted membrane has more
than 10 percent open area.
B)
The owner or operator shall inspect the internal floating roof
components as follows, except as provided in subsection (e)(3)(C) of
this Section:
i)
Visually inspect the internal floating roof components through
openings on the fixed-roof (e.g., manholes and roof hatches) at
least once every 12 months after initial fill, and
ii)
Visually inspect the internal floating roof, primary seal,
secondary seal (if one is in service), gaskets, slotted
69
membranes, and sleeve seals (if any) each time the tank is
emptied and degassed and at least once every 10 years.
C)
As an alternative to performing the inspections specified in subsection
(e)(3)(B) of this Section for an internal floating roof equipped with two
continuous seals mounted one above the other, the owner or operator
may visually inspect the internal floating roof, primary and secondary
seals, gaskets, slotted membranes, and sleeve seals (if any) each time
the tank is emptied and degassed and at least every five years.
D)
Prior to each inspection required by subsection (e)(3)(B) or (e)(3)(C)
of this Section, the owner or operator shall notify the Agency in
advance of each inspection to provide the Agency with the opportunity
to have an observer present during the inspection. The owner or
operator shall notify the Agency of the date and location of the
inspection as follows:
i)
Prior to each visual inspection of an internal floating roof in a
tank that has been emptied and degassed, written notification
must be prepared and sent by the owner or operator so that it is
received by the Agency at least 30 calendar days before refilling
the tank, except when an inspection is not planned, as provided
for in subsection (e)(3)(D)(ii) of this Section.
ii)
When a visual inspection is not planned and the owner or
operator could not have known about the inspection 30
calendar days before refilling the tank, the owner or operator
shall notify the Agency as soon as possible, but no later than
seven calendar days before refilling of the tank. This notification
may be made by telephone and immediately followed by a
written explanation for why the inspection is unplanned.
Alternatively, written notification, including the explanation for
the unplanned inspection, may be sent so that it is received by
the Agency at least seven calendar days before refilling the tank.
E)
In the event that a defect is detected, the owner or operator shall repair
the defect in accordance with the requirements of subsection (k) of this
Section.
F)
The owner or operator shall maintain a record of the inspection in
accordance with the requirements specified in Section 724.989(b).
4)
Safety devices, as defined in 35 Ill. Adm. Code 725.981, may be installed and
70
operated as necessary on any tank complying with the requirements of this
subsection (e).
f)
The owner or operator that controls air pollutant emissions from a tank using an external
floating roof must meet the requirements specified in subsections (f)(1) through (f)(3) of
this Section.
1)
The owner or operator shall design the external floating roof in accordance with
the following requirements:
A)
The external floating roof must be designed to float on the liquid surface
except when the floating roof must be supported by the leg supports.
B)
The floating roof must be equipped with two continuous seals, one
above the other, between the wall of the tank and the roof edge. The
lower seal is referred to as the primary seal, and the upper seal is
referred to as the secondary seal.
i)
The primary seal must be a liquid-mounted seal or a metallic
shoe seal, as defined in 35 Ill. Adm. Code 725.981. The total
area of the gaps between the tank wall and the primary seal
must not exceed 212 square centimeters (cm
2
) per meter (10.0
square inches (in
2
) per foot) of tank diameter, and the width of
any portion of these gaps must not exceed 3.8 centimeters (cm)
(1.5 in). If a metallic shoe seal is used for the primary seal, the
metallic shoe seal must be designed so that one end extends into
the liquid in the tank and the other end extends a vertical
distance of at least 61 cm (24 in) above the liquid surface.
ii)
The secondary seal must be mounted above the primary seal
and cover the annular space between the floating roof and the
wall of the tank. The total area of the gaps between the tank
wall and the secondary seal must not exceed 21.2 cm
2
per
meter (1.00 in
2
per foot) of tank diameter, and the width of any
portion of these gaps must not exceed 1.3 cm (0.51 in).
C)
The external floating roof must meet the following specifications:
i)
Except for automatic bleeder vents (vacuum breaker vents) and
rim space vents, each opening in a noncontact external floating
roof must provide a projection below the liquid surface.
ii)
Except for automatic bleeder vents, rim space vents, roof
71
drains, and leg sleeves, each opening in the roof must be
equipped with a gasketed cover, seal, or lid.
iii)
Each access hatch and each gauge float well must be equipped
with a cover designed to be bolted or fastened when the cover
is secured in the closed position.
iv)
Each automatic bleeder vent and each rim space vent must be
equipped with a gasket.
v)
Each roof drain that empties into the liquid managed in the tank
must be equipped with a slotted membrane fabric cover that
covers at least 90 percent of the area of the opening.
vi)
Each unslotted and slotted guide pole well must be equipped
with a gasketed sliding cover or a flexible fabric sleeve seal.
vii)
Each unslotted guide pole must be equipped with a gasketed
cap on the end of the pole.
viii)
Each slotted guide pole must be equipped with a gasketed float
or other device which that closes off the liquid surface from the
atmosphere.
ix)
Each gauge hatch and each sample well must be equipped with
a gasketed cover.
2)
The owner or operator shall operate the tank in accordance with the following
requirements:
A)
When the floating roof is resting on the leg supports, the process of
filling, emptying, or refilling must be continuous and must be completed
as soon as practical.
B)
Except for automatic bleeder vents, rim space vents, roof drains, and
leg sleeves, each opening in the roof must be secured and maintained in
a closed position at all times except when the closure device must be
open for access.
C)
Covers on each access hatch and each gauge float well must be bolted
or fastened when secured in the closed position.
D)
Automatic bleeder vents must be set closed at all times when the roof is
72
floating, except when the roof is being floated off or is being landed on
the leg supports.
E)
Rim space vents must be set to open only at those times that the roof is
being floated off the roof leg supports or when the pressure beneath the
rim seal exceeds the manufacturer’s recommended setting.
F)
The cap on the end of each unslotted guide pole must be secured in the
closed position at all times except when measuring the level or collecting
samples of the liquid in the tank.
G)
The cover on each gauge hatch or sample well must be secured in the
closed position at all times except when the hatch or well must be
opened for access.
H)
Both the primary seal and the secondary seal must completely cover the
annular space between the external floating roof and the wall of the tank
in a continuous fashion except during inspections.
3)
The owner or operator shall inspect the external floating roof in accordance with
the procedures specified as follows:
A)
The owner or operator shall measure the external floating roof seal gaps
in accordance with the following requirements:
i)
The owner or operator shall perform measurements of gaps
between the tank wall and the primary seal within 60 calendar
days after initial operation of the tank following installation of the
floating roof and, thereafter, at least once every five years.
ii)
The owner or operator shall perform measurements of gaps
between the tank wall and the secondary seal within 60
calendar days after initial operation of the tank following
installation of the floating roof and, thereafter, at least once
every year.
iii)
If a tank ceases to hold hazardous waste for a period of one
year or more, subsequent introduction of hazardous waste into
the tank must be considered an initial operation for the purposes
of subsections (f)(3)(A)(i) and (f)(3)(A)(ii) of this Section.
iv)
The owner or operator shall determine the total surface area of
gaps in the primary seal and in the secondary seal individually
73
using the procedure of subsection (f)(3)(D) of this Section.
v)
In the event that the seal gap measurements do not conform to
the specifications in subsection (f)(1)(B) of this Section, the
owner or operator shall repair the defect in accordance with the
requirements of subsection (k) of this Section.
vi)
The owner or operator shall maintain a record of the inspection
in accordance with the requirements specified in Section
724.989(b).
B)
The owner or operator shall visually inspect the external floating roof in
accordance with the following requirements:
i)
The floating roof and its closure devices must be visually
inspected by the owner or operator to check for defects that
could result in air pollutant emissions. Defects include, but are
not limited to, any of the following conditions: holes, tears, or
other openings in the rim seal or seal fabric of the floating roof;
a rim seal detached from the floating roof; all or a portion of the
floating roof deck being submerged below the surface of the
liquid in the tank; broken, cracked, or otherwise damaged seals
or gaskets on closure devices; and broken or missing hatches,
access covers, caps, or other closure devices.
ii)
The owner or operator shall perform an initial inspection of the
external floating roof and its closure devices on or before the
date that the tank becomes subject to this Section. Thereafter,
the owner or operator shall perform the inspections at least
once every year except for the special conditions provided for
in subsection (l) of this Section.
iii)
In the event that a defect is detected, the owner or operator
shall repair the defect in accordance with the requirements of
subsection (k) of this Section.
iv)
The owner or operator shall maintain a record of the inspection
in accordance with the requirements specified in Section
724.989(b).
C)
Prior to each inspection required by subsection (f)(3)(A) or (f)(3)(B) of
this Section, the owner or operator shall notify the Agency in advance
of each inspection to provide the Agency with the opportunity to have
74
an observer present during the inspection. The owner or operator shall
notify the Agency of the date and location of the inspection as follows:
i)
Prior to each inspection to measure external floating roof seal
gaps as required under subsection (f)(3)(A) of this Section,
written notification must be prepared and sent by the owner or
operator so that it is received by the Agency at least 30
calendar days before the date the measurements are scheduled
to be performed.
ii)
Prior to each visual inspection of an external floating roof in a
tank that has been emptied and degassed, written notification
must be prepared and sent by the owner or operator so that it is
received by the Agency at least 30 calendar days before refilling
the tank, except when an inspection is not planned as provided
for in subsection (f)(3)(C)(iii) of this Section.
iii)
When a visual inspection is not planned and the owner or
operator could not have known about the inspection 30
calendar days before refilling the tank, the owner or operator
shall notify the Agency as soon as possible, but no later than
seven calendar days before refilling of the tank. This notification
may be made by telephone and immediately followed by a
written explanation for why the inspection is unplanned.
Alternatively, written notification, including the explanation for
the unplanned inspection, may be sent so that it is received by
the Agency at least seven calendar days before refilling the tank.
D)
Procedure for determining the total surface area of gaps in the primary
seal and the secondary seal:
i)
The seal gap measurements must be performed at one or more
floating roof levels when the roof is floating off the roof
supports.
ii)
Seal gaps, if any, must be measured around the entire perimeter
of the floating roof in each place where a 0.32 cm (0.125 in)
diameter uniform probe passes freely (without forcing or binding
against the seal) between the seal and the wall of the tank and
measure the circumferential distance of each such location.
iii)
For a seal gap measured under subsection (f)(3) of this Section,
the gap surface area must be determined by using probes of
75
various widths to measure accurately the actual distance from
the tank wall to the seal and multiplying each such width by its
respective circumferential distance.
iv)
The total gap area must be calculated by adding the gap surface
areas determined for each identified gap location for the primary
seal and the secondary seal individually, and then dividing the
sum for each seal type by the nominal diameter of the tank.
These total gap areas for the primary seal and secondary seal
are then compared to the respective standards for the seal type,
as specified in subsection (f)(1)(B) of this Section.
BOARD NOTE: Subsections (f)(3)(D)(i) through (f)(3)(D)(iv) are
derived from 40 CFR 264.1084(f)(3)(i)(D)(1) through (f)(3)(i)(D)(4),
which the Board has codified here to comport with Illinois
Administrative Code format requirements.
4)
Safety devices, as defined in 35 Ill. Adm. Code 725.981, may be installed and
operated as necessary on any tank complying with the requirements of
subsection (f) of this Section.
g)
The owner or operator that controls air pollutant emissions from a tank by venting the
tank to a control device shall meet the requirements specified in subsections (g)(1)
through (g)(3) of this Section.
1)
The tank must be covered by a fixed roof and vented directly through a closed-
vent system to a control device in accordance with the following requirements:
A)
The fixed roof and its closure devices must be designed to form a
continuous barrier over the entire surface area of the liquid in the tank.
B)
Each opening in the fixed roof not vented to the control device must be
equipped with a closure device. If the pressure in the vapor headspace
underneath the fixed roof is less than atmospheric pressure when the
control device is operating, the closure devices must be designed to
operate such so that when the closure device is secured in the closed
position there are no visible cracks, holes, gaps, or other open spaces in
the closure device or between the perimeter of the cover opening and
the closure device. If the pressure in the vapor headspace underneath
the fixed roof is equal to or greater than atmospheric pressure when the
control device is operating, the closure device must be designed to
operate with no detectable organic emissions.
76
C)
The fixed roof and its closure devices must be made of suitable
materials that will minimize exposure of the hazardous waste to the
atmosphere, to the extent practical, and will maintain the integrity of the
fixed roof and closure devices throughout their intended service life.
Factors to be considered when selecting the materials for and designing
the fixed roof and closure devices must include the following: organic
vapor permeability; the effects of any contact with the liquid and its
vapor managed in the tank; the effects of outdoor exposure to wind,
moisture, and sunlight; and the operating practices used for the tank on
which the fixed roof is installed.
D)
The closed-vent system and control device must be designed and
operated in accordance with the requirements of Section 724.987.
2)
Whenever a hazardous waste is in the tank, the fixed roof must be installed with
each closure device secured in the closed position and the vapor headspace
underneath the fixed roof vented to the control device except as follows:
A)
Venting to the control device is not required, and opening of closure
devices or removal of the fixed roof is allowed at the following times:
i)
To provide access to the tank for performing routine inspection,
maintenance, or other activities needed for normal operations.
Examples of such activities include those times when a worker
needs to open a port to sample liquid in the tank, or when a
worker needs to open a hatch to maintain or repair equipment.
Following completion of the activity, the owner or operator shall
promptly secure the closure device in the closed position or
reinstall the cover, as applicable, to the tank.
ii)
To remove accumulated sludge or other residues from the
bottom of a tank.
B)
Opening of a safety device, as defined in 35 Ill. Adm. Code 725.981, is
allowed at any time conditions require doing so to avoid an unsafe
condition.
3)
The owner or operator shall inspect and monitor the air emission control
equipment in accordance with the following procedures:
A)
The fixed roof and its closure devices must be visually inspected by the
owner or operator to check for defects that could result in air pollutant
emissions. Defects include, but are not limited to, any of the following:
77
visible cracks, holes, or gaps in the roof sections or between the roof
and the tank wall; broken, cracked, or otherwise damaged seals or
gaskets on closure devices; and broken or missing hatches, access
covers, caps, or other closure devices.
B)
The closed-vent system and control device must be inspected and
monitored by the owner or operator in accordance with the procedures
specified in Section 724.987.
C)
The owner or operator shall perform an initial inspection of the air
emission control equipment on or before the date that the tank becomes
subject to this Section. Thereafter, the owner or operator shall perform
the inspections at least once every year except for the special conditions
provided for in subsection (l) of this Section.
D)
In the event that a defect is detected, the owner or operator shall repair
the defect in accordance with the requirements of subsection (k) of this
Section.
E)
The owner or operator shall maintain a record of the inspection in
accordance with the requirements specified in Section 724.989(b).
h)
The owner or operator that controls air pollutant emissions by using a pressure tank
must meet the following requirements:
1)
The tank must be designed not to vent to the atmosphere as a result of
compression of the vapor headspace in the tank during filling of the tank to its
design capacity.
2)
All tank openings must be equipped with closure devices designed to operate
with no detectable organic emissions as determined using the procedure
specified in Section 724.983(d).
3)
Whenever a hazardous waste is in the tank, the tank must be operated as a
closed-vent system that does not vent to the atmosphere, except in the event
that a safety device, as defined in 35 Ill. Adm. Code 725.981, is required to
open to avoid an unsafe condition. under either of the following two conditions:
A) The tank does not need to be operated as a closed-vent system at
those times when the opening of a safety device, as defined in 35 Ill.
Adm. Code 725.981, is required to avoid an unsafe condition.
B) The tank does not need to be operated as a closed-vent system at
78
those times when the purging of inerts from the tank is required and the
purge stream is routed to a closed-vent system and control device
designed and operated in accordance with the requirements of Section
724.987.
i)
The owner or operator that controls air pollutant emissions by using an enclosure vented
through a closed-vent system to an enclosed combustion control device must shall meet
the requirements specified in subsections (i)(1) through (i)(4) of this Section.
1)
The tank must be located inside an enclosure. The enclosure must be designed
and operated in accordance with the criteria for a permanent total enclosure, as
specified in “Procedure T--Criteria for and Verification of a Permanent or
Temporary Total Enclosure” under 40 CFR 52.741, appendix B, incorporated
by reference in 35 Ill. Adm. Code 720.111. The enclosure may have
permanent or temporary openings to allow worker access; passage of material
into or out of the enclosure by conveyor, vehicles, or other mechanical means;
entry of permanent mechanical or electrical equipment; or direct airflow into the
enclosure. The owner or operator shall perform the verification procedure for
the enclosure, as specified in Section 5.0 to “Procedure T--Criteria for and
Verification of a Permanent or Temporary Total Enclosure”, initially when the
enclosure is first installed and, thereafter, annually.
2)
The enclosure must be vented through a closed-vent system to an enclosed
combustion control device that is designed and operated in accordance with the
standards for either a vapor incinerator, boiler, or process heater specified in
Section 724.987.
3)
Safety devices, as defined in 35 Ill. Adm. Code 725.981, may be installed and
operated as necessary on any enclosure, closed-vent system, or control device
used to comply with the requirements of subsections (i)(1) and (i)(2) of this
Section.
4)
The owner or operator shall inspect and monitor the closed-vent system and
control device as specified in Section 724.987.
j)
The owner or operator shall transfer hazardous waste to a tank subject to this Section in
accordance with the following requirements:
1)
Transfer of hazardous waste, except as provided in subsection (j)(2) of this
Section, to the tank from another tank subject to this Section or from a surface
impoundment subject to Section 724.985 must be conducted using continuous
hard-piping or another closed system that does not allow exposure of the
hazardous waste to the atmosphere. For the purpose of complying with this
79
provision, an individual drain system is considered to be a closed system when it
meets the requirements of 40 CFR 63, subpart RR, “National Emission
Standards for Individual Drain Systems”, incorporated by reference in 35 Ill.
Adm. Code 720.111.
2)
The requirements of subsection (j)(1) of this Section do not apply when
transferring a hazardous waste to the tank under any of the following conditions:
A)
The hazardous waste meets the average VO concentration conditions
specified in Section 724.982(c)(1) at the point of waste origination.
B)
The hazardous waste has been treated by an organic destruction or
removal process to meet the requirements in Section 724.982(c)(2).
C)
The hazardous waste meets the requirements of Section 724.982(c)(4).
k)
The owner or operator shall repair each defect detected during an inspection performed
in accordance with the requirements of subsection (c)(4), (e)(3), (f)(3), or (g)(3) of this
Section, as follows:
1)
The owner or operator shall make first efforts at repair of the defect no later
than five calendar days after detection, and repair must be completed as soon
as possible but no later than 45 calendar days after detection except as
provided in subsection (k)(2) of this Section.
2)
Repair of a defect may be delayed beyond 45 calendar days if the owner or
operator determines that repair of the defect requires emptying or temporary
removal from service of the tank and no alternative tank capacity is available at
the site to accept the hazardous waste normally managed in the tank. In this
case, the owner or operator shall repair the defect the next time the process or
unit that is generating the hazardous waste managed in the tank stops operation.
Repair of the defect must be completed before the process or unit resumes
operation.
l)
Following the initial inspection and monitoring of the cover, as required by the
applicable provisions of this Subpart, subsequent inspection and monitoring may be
performed at intervals longer than one year under the following special conditions:
1)
In the case when inspecting or monitoring the cover would expose a worker to
dangerous, hazardous, or other unsafe conditions, then the owner or operator
may designate a cover as an “unsafe to inspect and monitor cover” and comply
with all of the following requirements:
80
A)
Prepare a written explanation for the cover stating the reasons why the
cover is unsafe to visually inspect or to monitor, if required.
B)
Develop and implement a written plan and schedule to inspect and
monitor the cover, using the procedures specified in the applicable
Section of this Subpart, as frequently as practicable during those times
when a worker can safely access the cover.
2)
In the case when a tank is buried partially or entirely underground, an owner or
operator is required to inspect and monitor, as required by the applicable
provisions of this Section, only those portions of the tank cover and those
connections to the tank (e.g., fill ports, access hatches, gauge wells, etc.) that
are located on or above the ground surface.
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
Section 724.986
Standards: Containers
a)
The provisions of this Section apply to the control of air pollutant emissions from
containers for which Section 724.982(b) references the use of this Section for such air
emission control.
b)
General requirements.
1)
The owner or operator shall control air pollutant emissions from each container
subject to this Section in accordance with the following requirements, as
applicable to the container, except when the special provisions for waste
stabilization processes specified in subsection (b)(2) of this Section apply to the
container.
A)
For a container having a design capacity greater than 0.1 m
3
(26 gal)
and less than or equal to 0.46 m
3
(120 gal), the owner or operator shall
control air pollutant emissions from the container in accordance with the
Container Level 1 standards specified in subsection (c) of this Section.
B)
For a container having a design capacity greater than 0.46 m
3
(120 gal)
that is not in light material service, the owner or operator shall control
air pollutant emissions from the container in accordance with the
Container Level 1 standards specified in subsection (c) of this Section.
C)
For a container having a design capacity greater than 0.46 m
3
(120 gal)
that is in light material service, the owner or operator shall control air
pollutant emissions from the container in accordance with the Container
81
Level 2 standards specified in subsection (d) of this Section.
2)
When a container having a design capacity greater than 0.1 m
3
(26 gal) is used
for treatment of a hazardous waste by a waste stabilization process, the owner
or operator shall control air pollutant emissions from the container in
accordance with the Container Level 3 standards specified in subsection (e) of
this Section at those times during the waste stabilization process when the
hazardous waste in the container is exposed to the atmosphere.
c)
Container Level 1 standards.
1)
A container using Container Level 1 controls is one of the following:
A)
A container that meets the applicable U.S. Department of
Transportation (USDOT) regulations on packaging hazardous materials
for transportation, as specified in subsection (f) of this Section.
B)
A container equipped with a cover and closure devices that form a
continuous barrier over the container openings so that when the cover
and closure devices are secured in the closed position there are no
visible holes, gaps, or other open spaces into the interior of the
container. The cover may be a separate cover installed on the container
(e.g., a lid on a drum or a suitably secured tarp on a roll-off box) or
may be an integral part of the container structural design (e.g., a
“portable tank” or bulk cargo container equipped with a screw-type
cap).
C)
An open-top container in which an organic-vapor suppressing barrier is
placed on or over the hazardous waste in the container such so that no
hazardous waste is exposed to the atmosphere. One example of such a
barrier is application of a suitable organic-vapor suppressing foam.
2)
A container used to meet the requirements of subsection (c)(1)(B) or (c)(1)(C)
of this Section must be equipped with covers and closure devices, as applicable
to the container, that are composed of suitable materials to minimize exposure
of the hazardous waste to the atmosphere and to maintain the equipment
integrity, for as long as it is in service. Factors to be considered in selecting the
materials of construction and designing the cover and closure devices must
include the following: the organic vapor permeability; the effects of contact with
the hazardous waste or its vapor managed in the container; the effects of
outdoor exposure of the closure device or cover material to wind, moisture, and
sunlight; and the operating practices for which the container is intended to be
used.
82
3)
Whenever a hazardous waste is in a container using Container Level 1 controls,
the owner or operator shall install all covers and closure devices for the
container, as applicable to the container, and secure and maintain each closure
device in the closed position except as follows:
A)
Opening of a closure device or cover is allowed for the purpose of
adding hazardous waste or other material to the container as follows:
i)
In the case when the container is filled to the intended final level
in one continuous operation, the owner or operator shall
promptly secure the closure devices in the closed position and
install the covers, as applicable to the container, upon
conclusion of the filling operation.
ii)
In the case when discrete quantities or batches of material
intermittently are added to the container over a period of time,
the owner or operator shall promptly secure the closure devices
in the closed position and install covers, as applicable to the
container, upon either the container being filled to the intended
final level; the completion of a batch loading after which no
additional material will be added to the container within 15
minutes; the person performing the loading operation leaving the
immediate vicinity of the container; or the shutdown of the
process generating the material being added to the container,
whichever condition occurs first.
B)
Opening of a closure device or cover is allowed for the purpose of
removing hazardous waste from the container as follows:
i)
For the purpose of meeting the requirements of this Section, an
empty container, as defined in 35 Ill. Adm. Code 721.107(b),
may be open to the atmosphere at any time (i.e., covers and
closure devices are not required to be secured in the closed
position on an empty container).
ii)
In the case when discrete quantities or batches of material are
removed from the container but the container does not meet the
conditions to be an empty container as defined in 35 Ill. Adm.
Code 721.107(b), the owner or operator shall promptly secure
the closure devices in the closed position and install covers, as
applicable to the container, upon the completion of a batch
removal after which no additional material will be removed from
83
the container within 15 minutes or the person performing the
unloading operation leaves the immediate vicinity of the
container, whichever condition occurs first.
C)
Opening of a closure device or cover is allowed when access inside the
container is needed to perform routine activities other than transfer of
hazardous waste. Examples of such activities include those times when
a worker needs to open a port to measure the depth of or sample the
material in the container, or when a worker needs to open a manhole
hatch to access equipment inside the container. Following completion
of the activity, the owner or operator shall promptly secure the closure
device in the closed position or reinstall the cover, as applicable to the
container.
D)
Opening of a spring-loaded pressure-vacuum relief valve, conservation
vent, or similar type of pressure relief device which that vents to the
atmosphere is allowed during normal operations for the purpose of
maintaining the internal pressure of the container in accordance with the
container design specifications. The device must be designed to
operate with no detectable organic emissions when the device is
secured in the closed position. The settings at which the device opens
must be established such so that the device remains in the closed
position whenever the internal pressure of the container is within the
internal pressure operating range determined by the owner or operator
based on container manufacturer recommendations, applicable
regulations, fire protection and prevention codes, standard engineering
codes and practices, or other requirements for the safe handling of
flammable, ignitable, explosive, reactive, or hazardous materials.
Examples of normal operating conditions that may require these devices
to open are during those times when the internal pressure of the
container exceeds the internal pressure operating range for the container
as a result of loading operations or diurnal ambient temperature
fluctuations.
E)
Opening of a safety device, as defined in 35 Ill. Adm. Code 725.981, is
allowed at any time conditions require doing so to avoid an unsafe
condition.
4)
The owner or operator of containers using Container Level 1 controls shall
inspect the containers and their covers and closure devices as follows:
A)
In the case when a hazardous waste already is in the container at the
time the owner or operator first accepts possession of the container at
84
the facility and the container is not emptied within 24 hours after the
container is accepted at the facility (i.e., it does not meet the conditions
for an empty container as specified in 35 Ill. Adm. Code 721.107(b)),
the owner or operator shall visually inspect the container and its cover
and closure devices to check for visible cracks, holes, gaps, or other
open spaces into the interior of the container when the cover and
closure devices are secured in the closed position. The container visual
inspection must be conducted on or before the date on which the
container is accepted at the facility (i.e., the date when the container
becomes subject to the Subpart CC container standards). For the
purposes of this requirement, the date of acceptance is the date of
signature that the facility owner or operator enters on Item 20 of the
Uniform Hazardous Waste Manifest incorporated by reference in 35 Ill.
Adm. Code 722.Appendix A (USEPA Forms 8700-22 and 8700-
22A), as required under Section 724.171. If a defect is detected, the
owner or operator shall repair the defect in accordance with the
requirements of subsection (c)(4)(C) of this Section.
B)
In the case when a container used for managing hazardous waste
remains at the facility for a period of one year or more, the owner or
operator shall visually inspect the container and its cover and closure
devices initially and thereafter, at least once every 12 months, to check
for visible cracks, holes, gaps, or other open spaces into the interior of
the container when the cover and closure devices are secured in the
closed position. If a defect is detected, the owner or operator shall
repair the defect in accordance with the requirements of subsection
(c)(4)(C) of this Section.
C)
When a defect is detected for the container, cover, or closure devices,
the owner or operator shall make first efforts at repair of the defect no
later than 24 hours after detection and repair must be completed as
soon as possible but no later than five calendar days after detection. If
repair of a defect cannot be completed within five calendar days, then
the hazardous waste must be removed from the container and the
container must not be used to manage hazardous waste until the defect
is repaired.
5)
The owner or operator shall maintain at the facility a copy of the procedure
used to determine that containers with capacity of 0.46 m
3
(120 gal) or greater,
which do not meet applicable DOT regulations, as specified in subsection (f) of
this Section, are not managing hazardous waste in light material service.
d)
Container Level 2 standards.
85
1)
A container using Container Level 2 controls is one of the following:
A)
A container that meets the applicable U.S. Department of
Transportation (USDOT) regulations on packaging hazardous materials
for transportation as specified in subsection (f) of this Section.
B)
A container that operates with no detectable organic emissions, as
defined in 35 Ill. Adm. Code 725.981, and determined in accordance
with the procedure specified in subsection (g) of this Section.
C)
A container that has been demonstrated within the preceding 12 months
to be vapor-tight by using 40 CFR 60, appendix A, Method 27,
incorporated by reference in 35 Ill. Adm. Code 720.111, in
accordance with the procedure specified in subsection (h) of this
Section.
2)
Transfer of hazardous waste in or out of a container using Container Level 2
controls must be conducted in such a manner as to minimize exposure of the
hazardous waste to the atmosphere, to the extent practical, considering the
physical properties of the hazardous waste and good engineering and safety
practices for handling flammable, ignitable, explosive, reactive, or other
hazardous materials. Examples of container loading procedures that the
USEPA considers to meet the requirements of this subsection (d)(2) include
using any one of the following: a submerged-fill pipe or other submerged-fill
method to load liquids into the container; a vapor-balancing system or a vapor-
recovery system to collect and control the vapors displaced from the container
during filling operations; or a fitted opening in the top of a container through
which the hazardous waste is filled and subsequently purging the transfer line
before removing it from the container opening.
3)
Whenever a hazardous waste is in a container using Container Level 2 controls,
the owner or operator shall install all covers and closure devices for the
container, and secure and maintain each closure device in the closed position,
except as follows:
A)
Opening of a closure device or cover is allowed for the purpose of
adding hazardous waste or other material to the container as follows:
i)
In the case when the container is filled to the intended final level
in one continuous operation, the owner or operator shall
promptly secure the closure devices in the closed position and
install the covers, as applicable to the container, upon
86
conclusion of the filling operation.
ii)
In the case when discrete quantities or batches of material
intermittently are added to the container over a period of time,
the owner or operator shall promptly secure the closure devices
in the closed position and install covers, as applicable to the
container, upon either the container being filled to the intended
final level; the completion of a batch loading after which no
additional material will be added to the container within 15
minutes; the person performing the loading operation leaving the
immediate vicinity of the container; or the shutdown of the
process generating the material being added to the container,
whichever condition occurs first.
B)
Opening of a closure device or cover is allowed for the purpose of
removing hazardous waste from the container as follows:
i)
For the purpose of meeting the requirements of this Section, an
empty container as defined in 35 Ill. Adm. Code 721.107(b)
may be open to the atmosphere at any time (i.e., covers and
closure devices are not required to be secured in the closed
position on an empty container).
ii)
In the case when discrete quantities or batches of material are
removed from the container but the container does not meet the
conditions to be an empty container as defined in 35 Ill. Adm.
Code 721.107(b), the owner or operator shall promptly secure
the closure devices in the closed position and install covers, as
applicable to the container, upon the completion of a batch
removal after which no additional material will be removed from
the container within 15 minutes or the person performing the
unloading operation leaves the immediate vicinity of the
container, whichever condition occurs first.
C)
Opening of a closure device or cover is allowed when access inside the
container is needed to perform routine activities other than transfer of
hazardous waste. Examples of such activities include those times when
a worker needs to open a port to measure the depth of or sample the
material in the container, or when a worker needs to open a manhole
hatch to access equipment inside the container. Following completion
of the activity, the owner or operator shall promptly secure the closure
device in the closed position or reinstall the cover, as applicable to the
container.
87
D)
Opening of a spring-loaded, pressure-vacuum relief valve, conservation
vent, or similar type of pressure relief device which that vents to the
atmosphere is allowed during normal operations for the purpose of
maintaining the internal pressure of the container in accordance with the
container design specifications. The device must be designed to operate
with no detectable organic emission when the device is secured in the
closed position. The settings at which the device opens must be
established such so that the device remains in the closed position
whenever the internal pressure of the container is within the internal
pressure operating range determined by the owner or operator based
on container manufacturer recommendations, applicable regulations, fire
protection and prevention codes, standard engineering codes and
practices, or other requirements for the safe handling of flammable,
ignitable, explosive, reactive, or hazardous materials. Examples of
normal operating conditions that may require these devices to open are
during those times when the internal pressure of the container exceeds
the internal pressure operating range for the container as a result of
loading operations or diurnal ambient temperature fluctuations.
E)
Opening of a safety device, as defined in 35 Ill. Adm. Code 725.981, is
allowed at any time conditions require doing so to avoid an unsafe
condition.
4)
The owner or operator of containers using Container Level 2 controls shall
inspect the containers and their covers and closure devices as follows:
A)
In the case when a hazardous waste already is in the container at the
time the owner or operator first accepts possession of the container at
the facility and the container is not emptied within 24 hours after the
container is accepted at the facility (i.e., it does not meet the conditions
for an empty container as specified in 35 Ill. Adm. Code 721.107(b)),
the owner or operator shall visually inspect the container and its cover
and closure devices to check for visible cracks, holes, gaps, or other
open spaces into the interior of the container when the cover and
closure devices are secured in the closed position. The container visual
inspection must be conducted on or before the date on which the
container is accepted at the facility (i.e., the date when the container
becomes subject to the Subpart CC container standards). For the
purposes of this requirement, the date of acceptance is the date of
signature that the facility owner or operator enters on Item 20 of the
Uniform Hazardous Waste Manifest incorporated by reference in the
appendix to 40 CFR 262 (USEPA Forms 8700-22 and 8700-22A),
88
as required under Section 724.171. If a defect is detected, the owner
or operator shall repair the defect in accordance with the requirements
of subsection (d)(4)(C) of this Section.
B)
In the case when a container used for managing hazardous waste
remains at the facility for a period of one year or more, the owner or
operator shall visually inspect the container and its cover and closure
devices initially and thereafter, at least once every 12 months, to check
for visible cracks, holes, gaps, or other open spaces into the interior of
the container when the cover and closure devices are secured in the
closed position. If a defect is detected, the owner or operator shall
repair the defect in accordance with the requirements of subsection
(d)(4)(C) of this Section.
C)
When a defect is detected for the container, cover, or closure devices,
the owner or operator shall make first efforts at repair of the defect no
later than 24 hours after detection, and repair must be completed as
soon as possible but no later than five calendar days after detection. If
repair of a defect cannot be completed within five calendar days, then
the hazardous waste must be removed from the container and the
container must not be used to manage hazardous waste until the defect
is repaired.
e)
Container Level 3 standards.
1)
A container using Container Level 3 controls is one of the following:
A)
A container that is vented directly through a closed-vent system to a
control device in accordance with the requirements of subsection
(e)(2)(B) of this Section.
B)
A container that is vented inside an enclosure which is exhausted
through a closed-vent system to a control device in accordance with the
requirements of subsections (e)(2)(A) and (e)(2)(B) of this Section.
2)
The owner or operator shall meet the following requirements, as applicable to
the type of air emission control equipment selected by the owner or operator:
A)
The container enclosure must be designed and operated in accordance
with the criteria for a permanent total enclosure as specified in
“Procedure T--Criteria for and Verification of a Permanent or
Temporary Total Enclosure” under 40 CFR 52.741, appendix B,
incorporated by reference in 35 Ill. Adm. Code 720.111. The
89
enclosure may have permanent or temporary openings to allow worker
access; passage of containers through the enclosure by conveyor or
other mechanical means; entry of permanent mechanical or electrical
equipment; or direct airflow into the enclosure. The owner or operator
shall perform the verification procedure for the enclosure as specified in
Section 5.0 to “Procedure T--Criteria for and Verification of a
Permanent or Temporary Total Enclosure” initially when the enclosure is
first installed and, thereafter, annually.
B)
The closed-vent system and control device must be designed and
operated in accordance with the requirements of Section 724.987.
3)
Safety devices, as defined in 35 Ill. Adm. Code 725.981, may be installed and
operated as necessary on any container, enclosure, closed-vent system, or
control device used to comply with the requirements of subsection (e)(1) of this
Section.
4)
Owners and operators using Container Level 3 controls in accordance with the
provisions of this Subpart shall inspect and monitor the closed-vent systems and
control devices as specified in Section 724.987.
5)
Owners and operators that use Container Level 3 controls in accordance with
the provisions of this Subpart shall prepare and maintain the records specified in
Section 724.989(d).
6) The transfer of hazardous waste into or out of a container using Container Level
3 controls must be conducted in such a manner as to minimize exposure of the
hazardous waste to the atmosphere, to the extent practical considering the
physical properties of the hazardous waste and good engineering and safety
practices for handling flammable, ignitable, explosive, reactive, or other
hazardous materials. Examples of container loading procedures that USEPA
considers to meet the requirements of this subsection (e)(6) include using any
one of the following: the use of a submerged-fill pipe or other submerged-fill
method to load liquids into the container; the use of a vapor-balancing system or
a vapor-recovery system to collect and control the vapors displaced from the
container during filling operations; or the use of a fitted opening in the top of a
container through which the hazardous waste is filled and subsequently purging
the transfer line before removing it from the container opening.
f)
For the purpose of compliance with subsection (c)(1)(A) or (d)(1)(A) of this Section,
containers must be used that meet the applicable U.S. Department of Transportation
(USDOT) regulations on packaging hazardous materials for transportation as follows:
90
1)
The container meets the applicable requirements specified in 49 CFR 178,
“Specifications for Packaging”, or 49 CFR 179, “Specifications for Tank
Cars”, both incorporated by reference in 35 Ill. Adm. Code 720.111.
2)
Hazardous waste is managed in the container in accordance with the applicable
requirements specified in 49 CFR 107, Subpart B, “Exemptions”; 49 CFR 172,
“Hazardous Materials Table, Special Provisions, Hazardous Materials
Communications, Emergency Response Information, and Training
Requirements”; 49 CFR 173, “Shippers--General Requirements for Shipments
and Packages”; and 49 CFR 180, “Continuing Qualification and Maintenance
of Packagings”, each incorporated by reference in 35 Ill. Adm. Code 720.111.
3)
For the purpose of complying with this Subpart, no exceptions to the 49 CFR
178 or 179 regulations are allowed, except as provided for in subsection (f)(4)
of this Section.
4)
For a lab pack that is managed in accordance with the requirements of 49 CFR
178, incorporated by reference in 35 Ill. Adm. Code 720.111, for the purpose
of complying with this Subpart, an owner or operator may comply with the
exceptions for combination packagings specified in 49 CFR 173.12(b).
g)
To determine compliance with the no detectable organic emissions requirement of
subsection (d)(1)(B) of this Section, the procedure specified in Section 724.983(d)
must be used.
1)
Each potential leak interface (i.e., a location where organic vapor leakage could
occur) on the container, its cover, and associated closure devices, as applicable
to the container, must be checked. Potential leak interfaces that are associated
with containers include, but are not limited to, the following: the interface of the
cover rim and the container wall; the periphery of any opening on the container
or container cover and its associated closure device; and the sealing seat
interface on a spring-loaded pressure-relief valve.
2)
The test must be performed when the container is filled with a material having a
volatile organic concentration representative of the range of volatile organic
concentrations for the hazardous wastes expected to be managed in this type of
container. During the test, the container cover and closure devices must be
secured in the closed position.
h)
Procedure for determining a container to be vapor-tight using Method 27 of 40 CFR
60, appendix A for the purpose of complying with subsection (d)(1)(C) of this Section.
1)
The test must be performed in accordance with Method 27 of 40 CFR 60,
91
appendix A, incorporated by reference in 35 Ill. Adm. Code 720.111.
2)
A pressure measurement device must be used that has a precision of ± 2.5 mm
(0.098 in) water and that is capable of measuring above the pressure at which
the container is to be tested for vapor tightness.
3)
If the test results determined by Method 27 indicate that the container sustains a
pressure change less than or equal to 750 Pascals (0.11 psig) within five
minutes after it is pressurized to a minimum of 4,500 Pascals (0.65 psig), then
the container is determined to be vapor-tight.
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
TITLE 35: ENVIRONMENTAL PROTECTION
SUBTITLE G: WASTE DISPOSAL
CHAPTER I: POLLUTION CONTROL BOARD
SUBCHAPTER c: HAZARDOUS WASTE OPERATING REQUIREMENTS
PART 725
INTERIM STATUS STANDARDS FOR OWNERS AND OPERATORS OF
HAZARDOUS WASTE TREATMENT, STORAGE, AND DISPOSAL
FACILITIES
SUBPART A: GENERAL PROVISIONS
Section
725.101
Purpose, Scope, and Applicability
725.104
Imminent Hazard Action
SUBPART B: GENERAL FACILITY STANDARDS
Section
725.110
Applicability
725.111
USEPA Identification Number
725.112
Required Notices
725.113
General Waste Analysis
725.114
Security
725.115
General Inspection Requirements
725.116
Personnel Training
725.117
General Requirements for Ignitable, Reactive, or Incompatible Wastes
725.118
Location Standards
725.119
Construction Quality Assurance Program
92
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
725.191
Groundwater Monitoring System
725.192
Sampling and Analysis
725.193
Preparation, Evaluation and Response
725.194
Recordkeeping and Reporting
SUBPART G: CLOSURE AND POST-CLOSURE CARE
Section
725.210
Applicability
725.211
Closure Performance Standard
93
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 Care Plan; Amendment of Plan
725.219
Post-Closure Notices
725.220
Certification of Completion of Post-Closure Care
725.221
Alternative Post-Closure Care Requirements
SUBPART H: FINANCIAL REQUIREMENTS
Section
725.240
Applicability
725.241
Definitions of Terms as Used in this Subpart
725.242
Cost Estimate for Closure
725.243
Financial Assurance for Closure
725.244
Cost Estimate for Post-closure Care
725.245
Financial Assurance for Post-closure Monitoring and Maintenance
725.246
Use of a Mechanism for Financial Assurance of Both Closure and Post-closure Care
725.247
Liability Requirements
725.248
Incapacity of Owners or Operators, Guarantors or Financial Institutions
725.251
Promulgation of Forms (Repealed)
SUBPART I: USE AND MANAGEMENT OF CONTAINERS
Section
725.270
Applicability
725.271
Condition of Containers
725.272
Compatibility of Waste with Container
725.273
Management of Containers
725.274
Inspections
725.276
Special Requirements for Ignitable or Reactive Waste
725.277
Special Requirements for Incompatible Wastes
725.278
Air Emission Standards
SUBPART J: TANK SYSTEMS
Section
725.290
Applicability
725.291
Assessment of Existing Tank System’s Integrity
725.292
Design and Installation of New Tank Systems or Components
725.293
Containment and Detection of Releases
725.294
General Operating Requirements
725.295
Inspections
94
725.296
Response to leaks or spills and disposition of Tank Systems
725.297
Closure and Post-Closure Care
725.298
Special Requirements for Ignitable or Reactive Waste
725.299
Special Requirements for Incompatible Wastes
725.300
Waste Analysis and Trial Tests
725.301
Generators of 100 to 1000 Kilograms of Hazardous Waste Per Month
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
95
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
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
96
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
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
97
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 (Repealed)
SUBPART DD: CONTAINMENT BUILDINGS
Section
725.1100
Applicability
725.1101
Design and operating standards
725.1102
Closure and Post Closure-Care
SUBPART EE: HAZARDOUS WASTE MUNITIONS AND EXPLOSIVES
STORAGE
Section
725.1200
Applicability
725.1201
Design and Operating Standards
725.1202
Closure and Post-Closure Care
725.Appendix A
Recordkeeping Instructions
725.Appendix B
EPA Report Form and Instructions (Repealed)
725.Appendix C
EPA Interim Primary Drinking Water Standards
725.Appendix D
Tests for Significance
725.Appendix E
Examples of Potentially Incompatible Waste
725.Appendix F
Compounds With Henry’s Law Constant Less Than 0.1 Y/X (at 25°C)
AUTHORITY: Implementing Sections 7.2 and 22.4 and authorized by Section 27 of the Environmental
Protection Act [415 ILCS 5/7.2, 22.4, and 27].
SOURCE: Adopted in R81-22, 43 PCB 427, at 5 Ill. Reg. 9781, effective May 17, 1982; amended
98
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. 11078, effective August 1,
1996; amended in R96-10/R97-3/R97-5 at 22 Ill. Reg. 369, effective December 16, 1997; amended
in R98-12 at 22 Ill. Reg. 7620, effective April 15, 1998; amended in R97-21/R98-3/R98-5 at 22 Ill.
Reg. 17620, effective September 28, 1998; amended in R98-21/R99-2/R99-7 at 23 Ill. Reg. 1850,
effective January 19, 1999; amended in R99-15 at 23 Ill. Reg. 9168, effective July 26, 1999; amended
in R00-5 at 24 Ill. Reg. ________, effective ______________________.
SUBPART CC: AIR EMISSION STANDARDS FOR TANKS, SURFACE
IMPOUNDMENTS, AND CONTAINERS
Section 725.980
Applicability
a)
The requirements of this Subpart apply to owners and operators of all facilities that
treat, store, or dispose of hazardous waste in tanks, surface impoundments, or
containers that are subject to Subpart I, J, or K of this Part, except as Section 725.101
and subsection (b) of this Section provide otherwise.
b)
The requirements of this Subpart do not apply to the following waste management units
at the facility:
1)
A waste management unit that holds hazardous waste placed in the unit before
December 6, 1996, and in which no hazardous waste is added to the unit on or
after December 6, 1996.
2)
A container that has a design capacity less than or equal to 0.1 m
3
(3.5 ft
3
or
99
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 placed in the unit as the a 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 USC 2011 et seq.) and the Nuclear Waste Policy
Act.
7)
A hazardous waste management unit that the owner or operator certifies is
equipped with and operating air emission controls in accordance with the
requirements of an applicable federal Clean Air Act regulation codified under
40 CFR 60, 61, or 63. For the purpose of complying with this subsection
(b)(7), a tank for which the air emission control includes an enclosure, as
opposed to a cover, must be in compliance with the enclosure and control
device requirements of Section 725.985(i), except as provided in Section
725.983(c)(5).
8)
A tank that has a process vent, as defined in 35 Ill. Adm. Code 725.931.
c)
For the owner and operator of a facility subject to this Subpart that has received a final
RCRA permit prior to December 6, 1996, the following requirements apply:
1)
The requirements of 35 Ill. Adm. Code 724.Subpart CC must be incorporated
into the permit when the permit is reissued, renewed, or modified in accordance
with the requirements of 35 Ill. Adm. Code 703 and 705.
2)
Until the date when the permit is reissued, renewed, or modified in accordance
with the requirements of 35 Ill. Adm. Code 703 and 705, the owner and
100
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 structural derivative of hydrogen
peroxide where one or both of the hydrogen atoms has been replaced by an
organic radical.
2)
The owner or operator prepares documentation, in accordance with Section
725.990(i), explaining why an undue safety hazard would be created if air
emission controls specified in Sections 725.985 through 725.988 are installed
and operated on the tanks and containers used at the facility to manage the
hazardous waste generated by the organic peroxide manufacturing process or
processes meeting the conditions of subsection (d)(1) of this Section.
3)
The owner or operator notifies the Agency in writing that hazardous waste
generated by an organic peroxide manufacturing process or processes meeting
the conditions of subsection (d)(1) of this Section are managed at the facility in
tanks or containers meeting the conditions of subsection (d)(2) of this Section.
The notification must state the name and address of the facility and be signed
and dated by an authorized representative of the facility owner or operator.
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
Section 725.984
Waste Determination Procedures
a)
Waste determination procedure for volatile organic (VO) concentration of a hazardous
waste at the point of waste origination.
1)
An owner or operator shall determine the average VO concentration at the
point of waste origination for each hazardous waste placed in a waste
101
management unit exempted under the provisions of Section 725.983(c)(1) from
using air emission controls in accordance with standards specified in Section
725.985 through Section 725.988, as applicable to the waste management unit.
A) An owner or operator shall make an initial determination of the average
VO concentration of the waste stream before the first time any portion
of the material in the hazardous waste stream is placed in a waste
management unit exempted under the provisions of Section
725.983(c)(1) from using air emission controls. Thereafter, an owner
or operator shall make an initial determination of the average VO
concentration of the waste stream for each averaging period that a
hazardous waste is managed in the unit.
B) An owner or operator shall perform a new waste determination
whenever changes to the source generating the waste stream are
reasonably likely to cause the average VO concentration of the
hazardous waste to increase to a level that is equal to or greater than the
VO concentration limits specified in Section 725.983(c)(1).
2)
For a waste determination that is required by subsection (a)(1) of this Section,
the average VO concentration of a hazardous waste at the point of waste
origination must be determined using either direct measurement, as specified in
subsection (a)(3) of this Section, or by knowledge of the waste, as specified in
subsection (a)(4) of this Section.
3)
Direct measurement to determine average VO concentration of a hazardous
waste at the point of waste origination.
A)
Identification. The owner or operator shall identify and record the point
of waste origination for the hazardous waste.
B)
Sampling. Samples of the hazardous waste stream must be collected at
the point of waste origination in such a manner such that volatilization of
organics contained in the waste and in the subsequent sample is
minimized and an adequately representative sample is collected and
maintained for analysis by the selected method.
i)
The averaging period to be used for determining the average
VO concentration for the hazardous waste stream on a mass-
weighted average basis must be designated and recorded. The
averaging period can represent any time interval that the owner
or operator determines is appropriate for the hazardous waste
stream but must not exceed one year.
102
ii)
A sufficient number of samples, but no fewer than four samples,
must be collected for a hazardous waste determination. All of
the samples for a given waste determination must be collected
within a one-hour period. The average of the four or more
sample results constitutes a waste determination for the waste
stream. One or more waste determinations may be required to
represent the complete range of waste compositions and
quantities that occur during the entire averaging period due to
normal variations in the operating conditions for the source or
process generating the hazardous waste stream. Examples of
such normal variations are seasonal variations in waste quantity
or fluctuations in ambient temperature.
iii)
All samples must be collected and handled in accordance with
written procedures prepared by the owner or operator and
documented in a site sampling plan. This plan must describe the
procedure by which representative samples of the hazardous
waste stream are collected such so that a minimum loss of
organics occurs throughout the sample collection and handling
process, and by which sample integrity is maintained. A copy
of the written sampling plan must be maintained on-site in the
facility operating records. An example of an acceptable
sampling plan includes a plan incorporating sample collection
and handling procedures in accordance with the requirements
specified in “Test Methods for Evaluating Solid Waste,
Physical/Chemical Methods,” USEPA Publication SW-846,
incorporated by reference in 35 Ill. Adm. Code 720.111, or in
Method 25D in 40 CFR 60, appendix A, incorporated by
reference in 35 Ill. Adm. Code 720.111.
iv)
Sufficient information, as specified in the “site sampling plan”
required under subsection (a)(3)(B)(iii) of this Section, must be
prepared and recorded to document the waste quantity
represented by the samples and, as applicable, the operating
conditions for the source or process generating the hazardous
waste represented by the samples.
C)
Analysis. Each collected sample must be prepared and analyzed in
accordance with one or more of the methods listed in subsections
(a)(3)(C)(i) through (a)(3)(C)(ix) of this Section, including the
appropriate quality assurance and quality control (QA/QC) checks and
use of target compounds for calibration. If Method 25D in 40 CFR 60,
103
appendix A, incorporated by reference in 35 Ill. Adm. Code 720.111,
is not used, then one or more methods should be chosen that are
appropriate to ensure that the waste determination accounts for and
reflects all organic compounds in the waste with Henry’s law constant
values at least 0.1 mole-fraction-in-the-gas-phase/mole-fraction-in-the-
liquid-phase (0.1 Y/X) (which can also be expressed as 1.8
×
10
-6
atmospheres/gram-mole/m
3
) at 25° C (77° F). Each of the analytical
methods listed in subsections (a)(3)(C)(ii) through (a)(3)(C)(vii) of this
Section has an associated list of approved chemical compounds for
which USEPA considers the method appropriate for measurement. If
an owner or operator uses USEPA Method 624, 625, 1624, or 1625
in 40 CFR 136, appendix A, incorporated by reference in 35 Ill. Adm.
Code 720.111, to analyze one or more compounds that are not on that
method’s published list, the Alternative Test Procedure contained in 40
CFR 136.4 and 136.5, incorporated by reference in 35 Ill. Adm. Code
720.111, must be followed. If an owner or operator uses USEPA
Method 8260 or 8270 in “Test Methods for Evaluating Solid Waste,
Physical/Chemical Methods”, USEPA Publication SW-846,
incorporated by reference in 35 Ill. Adm. Code 720.111, to analyze
one or more compounds that are not on that method’s published list, the
procedures in subsection (a)(3)(C)(viii) of this Section must be
followed. At the owner’s or operator’s discretion, the concentration of
each individual chemical constituent owner or operator may adjust test
data measured in the waste by a method other than Method 25D may
be corrected to the corresponding average VO concentration it value
that would have had been obtained, had it the waste samples been
measured analyzed using Method 25D. To adjust these data, by
multiplying the measured concentration of each individual chemical
constituent contained in the waste is multiplied by the constituent-
specific adjustment factor (f
m25D
), as specified in subsection (a)(4)(C) of
this Section. If the owner or operator elects to adjust test data, the
adjustment must be made to all individual chemical constituents with a
Henry's law constant value greater than or equal to 0.1 Y/X at 25° C
contained in the waste. Constituent-specific adjustment factors (f
m25D
)
can be obtained by contacting the USEPA, Waste and Chemical
Processes Group, Office of Air Quality Planning and Standards,
Research Triangle Park, NC 27711.
i)
Method 25D in 40 CFR 60, appendix A, incorporated by
reference in 35 Ill. Adm. Code 720.111.
ii)
Method 624 in 40 CFR 136, appendix A, incorporated by
reference in 35 Ill. Adm. Code 720.111.
104
iii)
Method 625 in 40 CFR 136, appendix A, incorporated by
reference in 35 Ill. Adm. Code 720.111. Perform corrections
to the compounds for which the analysis is being conducted
based on the “accuracy as recovery” using the factors in Table
7 of the method.
iv)
Method 1624 in 40 CFR 136, appendix A, incorporated by
reference in 35 Ill. Adm. Code 720.111.
v)
Method 1625 in 40 CFR 136, appendix A, incorporated by
reference in 35 Ill. Adm. Code 720.111.
vi)
Method 8260 in “Test Methods for Evaluating Solid Waste,
Physical/Chemical Methods”, USEPA Publication SW-846,
incorporated by reference in 35 Ill. Adm. Code 720.111.
Maintain a formal quality assurance program consistent with the
requirements of Method 8260. The quality assurance program
must include the elements set forth in subsection (a)(3)(F) of this
Section.
vii)
Method 8270 in “Test Methods for Evaluating Solid Waste,
Physical/Chemical Methods”, USEPA Publication SW-846,
incorporated by reference in 35 Ill. Adm. Code 720.111.
Maintain a formal quality assurance program consistent with the
requirements of Method 8270. The quality assurance program
must include the elements set forth in subsection (a)(3)(F) of this
Section.
viii)
Any other USEPA standard method that has been validated in
accordance with “Alternative Validation Procedure for USEPA
Waste and Wastewater Methods”, 40 CFR 63, appendix D,
incorporated by reference in 35 Ill. Adm. Code 720.111. As
an alternative, other USEPA standard methods may be
validated by the procedure specified in subsection (a)(3)(C)(ix)
of this Section.
ix)
Any other analysis method that has been validated in
accordance with the procedures specified in Section 5.1 or
Section 5.3, and the corresponding calculations in Section 6.1
or Section 6.3, of Method 301 in 40 CFR 63, appendix A,
incorporated by reference in 35 Ill. Adm. Code 720.111. The
data are acceptable if they meet the criteria specified in Section
105
6.1.5 or Section 6.3.3 of Method 301. If correction is required
under Section 6.3.3 of Method 301, the data are acceptable if
the correction factor is within the range 0.7 to 1.30. Other
Sections of Method 301 are not required.
D)
Calculations.
i)
The average VO concentration ( C ) on a mass-weighted basis
must be calculated by using the results for all waste
determinations conducted in accordance with subsections
(a)(3)(B) and (a)(3)(C) of this Section and the following
equation:
C =
1
Q
x
n
i = 1
(Q x C )
T
i
i
∑
Where:
C =
Average VO concentration of the hazardous waste at
the point of waste origination on a mass-weighted basis,
in ppmw.
i =
Individual waste determination “i” of the hazardous
waste.
n =
Total number of waste determinations of the hazardous
waste conducted for the averaging period (not to
exceed one year).
Q
i
=
Mass quantity of the hazardous waste stream
represented by C
i
, in kg/hr.
Q
T
=
Total mass quantity of the hazardous waste during the
averaging period, in kg/hr.
C
i
=
Measured VO concentration of waste determination “i”,
as determined in accordance with subsection (a)(3)(C)
of this Section (i.e., the average of the four or more
samples specified in subsection (a)(3)(B)(ii) of this
Section), in ppmw.
106
ii)
For the purpose of determining C
i
, for individual waste samples
analyzed in accordance with subsection (a)(3)(C) of this
Section, the owner or operator shall account for VO
concentrations determined to be below the limit of detection of
the analytical method by using the VO concentration determined
according to subsection (a)(3)(G) of this Section.
E)
Provided that the test method is appropriate for the waste as required
under subsection (a)(3)(C) of this Section, the Agency must determine
compliance based on the test method used by the owner or operator as
recorded pursuant to Section 725.990(f)(1).
F)
The quality assurance program elements required under subsections
(a)(3)(C)(vi) and (a)(3)(C)(vii) of this Section are as follows:
i)
Documentation of site-specific procedures to minimize the loss
of compounds due to volatilization, biodegradation, reaction, or
sorption during the sample collection, storage, preparation,
introduction, and analysis steps.
ii)
Measurement of the overall accuracy and precision of the
specific procedures.
BOARD NOTE: Subsections (a)(3)(F)(i) and (a)(3)(F)(ii) are derived
from 40 CFR 265.984(a)(3)(iii)(F)(1), (a)(3)(iii)(F)(2),
(a)(3)(iii)(G)(1), and (a)(3)(iii)(G)(2), which the Board has codified
here to comport with Illinois Administrative Code format requirements.
G)
VO concentrations below the limit of detection must be considered to
be as follows:
i)
If Method 25D in 40 CFR 60, appendix A, incorporated by
reference in 35 Ill. Adm. Code 720.111, is used for the
analysis, the VO concentration must be considered to be one-
half the blank value determined in the method at Section 4.4 of
Method 25D in 40 CFR 60, appendix A.
ii)
If any other analytical method is used, the VO concentration
must be considered to be one-half the sum of the limits of
detection established for each organic constituent in the waste
that has a Henry’s law constant value at least 0.1 mole-fraction-
in-the-gas-phase/mole-fraction-in-the-liquid-phase (0.1 Y/X)
(which can also be expressed as 1.8 x 10
-6
atmospheres/gram-
107
mole/m
3
) at 25° C.
BOARD NOTE: Subsections (a)(3)(G)(i) and (a)(3)(G)(ii) are derived
from 40 CFR 265.984(a)(3)(iv)(A)(1) and (a)(3)(iv)(A)(2), which the
Board has codified here to comport with Illinois Administrative Code
format requirements.
4)
Use of owner or operator knowledge to determine average VO concentration
of a hazardous waste at the point of waste origination.
A)
Documentation must be prepared that presents the information used as
the basis for the owner’s or operator’s knowledge of the hazardous
waste stream’s average VO concentration. Examples of information
that may be used as the basis for knowledge include the following:
material balances for the source or process generating the hazardous
waste stream; constituent-specific chemical test data for the hazardous
waste stream from previous testing that are still applicable to the current
waste stream; previous test data for other locations managing the same
type of waste stream; or other knowledge based on information
included in manifests, shipping papers, or waste certification notices.
B)
If test data are used as the basis for knowledge, then the owner or
operator shall document the test method, sampling protocol, and the
means by which sampling variability and analytical variability are
accounted for in the determination of the average VO concentration.
For example, an owner or operator may use organic concentration test
data for the hazardous waste stream that are validated in accordance
with Method 301 in 40 CFR 63, appendix A, incorporated by
reference in 35 Ill. Adm. Code 720.111, as the basis for knowledge of
the waste.
C)
An owner or operator using chemical constituent-specific concentration
test data as the basis for knowledge of the hazardous waste may adjust
the test data to the corresponding average VO concentration value
which that would have been obtained had the waste samples been
analyzed using Method 25D in 40 CFR 60, appendix A, incorporated
by reference in 35 Ill. Adm. Code 720.111. To adjust these data, the
measured concentration for each individual chemical constituent
contained in the waste is multiplied by the appropriate constituent-
specific adjustment factor (f
m25D
).
D)
In the event that the Agency and the owner or operator disagree on a
determination of the average VO concentration for a hazardous waste
108
stream using knowledge, then the results from a determination of
average VO concentration using direct measurement, as specified in
subsection (a)(3) of this Section, must be used to establish compliance
with the applicable requirements of this Subpart. The Agency may
perform or request that the owner or operator perform this
determination using direct measurement. The owner or operator may
choose one or more appropriate methods to analyze each collected
sample in accordance with the requirements of subsection (a)(3)(C) of
this Section.
b)
Waste determination procedures for treated hazardous waste.
1)
An owner or operator shall perform the applicable waste determination for each
treated hazardous waste placed in a waste management unit exempted under
the provisions of Section 725.983(c)(2)(A) through (c)(2)(F) from using air
emission controls in accordance with the standards specified in Sections
725.985 through 725.988, as applicable to the waste management unit.
A) An owner or operator shall make an initial determination of the average
VO concentration of the waste stream before the first time any portion
of the material in the treated waste stream is placed in the waste
management unit exempt under Section 725.983(c)(2), (c)(3), or (c)(4)
from using air emission controls. Thereafter, an owner or operator shall
update the information used for the waste determination at least once
every 12 months following the date of the initial waste determination.
B) An owner or operator shall perform a new waste determination
whenever changes to the process generating or treating the waste
stream are reasonably likely to cause the average VO concentration of
the hazardous waste to increase to such a level that the applicable
treatment conditions specified in Section 725.983 (c)(2), (c)(3), or
(c)(4) are not achieved.
2)
The owner or operator shall designate and record the specific provision in
Section 725.983(c)(2) under which the waste determination is being
performed. The waste determination for the treated hazardous waste must be
performed using the applicable procedures specified in subsections (b)(3)
through (b)(9) of this Section.
3)
Procedure to determine the average VO concentration of a hazardous waste at
the point of waste treatment.
A)
Identification. The owner or operator shall identify and record the point
109
of waste treatment for the hazardous waste.
B)
Sampling. Samples of the hazardous waste stream must be collected at
the point of waste treatment in such a manner such that volatilization of
organics contained in the waste and in the subsequent sample is
minimized and an adequately representative sample is collected and
maintained for analysis by the selected method.
i)
The averaging period to be used for determining the average
VO concentration for the hazardous waste stream on a mass-
weighted average basis must be designated and recorded. The
averaging period can represent any time interval that the owner
or operator determines is appropriate for the hazardous waste
stream but must not exceed one year.
ii)
A sufficient number of samples, but no fewer than four samples,
must be collected and analyzed for a hazardous waste
determination. All of the samples for a given waste
determination must be collected within a one-hour period. The
average of the four or more sample results constitutes a waste
determination for the hazardous waste stream. One or more
waste determinations may be required to represent the
complete range of waste compositions and quantities that occur
during the entire averaging period due to normal variations in the
operating conditions for the source or process generating or
treating the hazardous waste stream. Examples of such normal
variations are seasonal variations in waste quantity or
fluctuations in ambient temperature.
iii)
All samples must be collected and handled in accordance with
written procedures prepared by the owner or operator and
documented in a site sampling plan. This plan must describe the
procedure by which representative samples of the hazardous
waste stream are collected such so that a minimum loss of
organics occurs throughout the sample collection and handling
process, and by which sample integrity is maintained. A copy
of the written sampling plan must be maintained on-site in the
facility operating records. An example of an acceptable
sampling plan includes a plan incorporating sample collection
and handling procedures in accordance with the requirements
specified in “Test Methods for Evaluating Solid Waste,
Physical/Chemical Methods,” USEPA Publication No. SW-
846, incorporated by reference in 35 Ill. Adm. Code 720.111,
110
or in Method 25D in 40 CFR 60, appendix A, incorporated by
reference in 35 Ill. Adm. Code 720.111.
iv)
Sufficient information, as specified in the “site sampling plan”
required under subsection (a)(3)(B)(iii) of this Section, must be
prepared and recorded to document the waste quantity
represented by the samples and, as applicable, the operating
conditions for the process treating the hazardous waste
represented by the samples.
C)
Analysis. Each collected sample must be prepared and analyzed in
accordance with one or more of the methods listed in subsections
(b)(3)(C)(i) through (b)(3)(C)(ix) of this Section, including appropriate
quality assurance and quality control (QA/QC) checks and use of target
compounds for calibration. When the owner or operator is making a
waste determination for a treated hazardous waste that is to be
compared to an average VO concentration at the point of waste
origination or the point of waste entry to the treatment system, to
determine if the conditions of 35 Ill. Adm. Code 724.982(c)(2)(A)
through (c)(2)(F) or Section 725.983(c)(2)(A) through (c)(2)(F) are
met, then the waste samples shall must be prepared and analyzed using
the same method or methods as were used in making the initial waste
determinations at the point of waste origination or at the point of entry
to the treatment system. If Method 25D in 40 CFR 60, appendix A is
not used, then one or more methods should be chosen that are
appropriate to ensure that the waste determination accounts for and
reflects all organic compounds in the waste with Henry’s law constant
values at least 0.1 mole-fraction-in-the-gas-phase/mole-fraction-in-the-
liquid-phase (0.1 Y/X) [which can also be expressed as 1.8
×
10
-6
atmospheres/gram-mole/m
3
] at 25 degrees Celsius. Each of the
analytical methods listed in subsections (b)(3)(C)(ii) through
(b)(3)(C)(vii) of this Section has an associated list of approved chemical
compounds, for which USEPA considers the method appropriate for
measurement. If an owner or operator uses USEPA Method 624, 625,
1624, or 1625 in 40 CFR 136, appendix A, incorporated by reference
in 35 Ill. Adm. Code 720.111, to analyze one or more compounds that
are not on that method’s published list, the Alternative Test Procedure
contained in 40 CFR 136.4 and 136.5, incorporated by reference in 35
Ill. Adm. Code 720.111, must be followed. If an owner or operator
uses USEPA Method 8260 or 8270 in “Test Methods for Evaluating
Solid Waste, Physical/Chemical Methods”, USEPA Publication SW-
846, incorporated by reference in 35 Ill. Adm. Code 720.111, to
analyze one or more compounds that are not on that method’s
111
published list, the procedures in subsection (b)(3)(C)(viii) of this Section
must be followed. At the owner’s or operator’s discretion, the
concentration of each individual chemical constituent owner or operator
may adjust test data measured in the waste by a method other than
Method 25D may be corrected to the corresponding average VO
concentration it value that would have had been obtained, had it the
waste samples been measured analyzed using Method 25D. To adjust
these data, by multiplying the measured concentration of each individual
chemical constituent contained in the waste is multiplied by the
constituent-specific adjustment factor (f
m25D
), as specified in subsection
(a)(4)(C) of this Section. If the owner or operator elects to adjust test
data, the adjustment must be made to all individual chemical constituents
with a Henry's law constant value greater than or equal to 0.1 Y/X at
25° C contained in the waste. Constituent-specific adjustment factors
(f
m25D
) can be obtained by contacting the USEPA, Waste and Chemical
Processes Group, Office of Air Quality Planning and Standards,
Research Triangle Park, NC 27711.
i)
Method 25D in 40 CFR 60, appendix A, incorporated by
reference in 35 Ill. Adm. Code 720.111.
ii)
Method 624 in 40 CFR 136, appendix A, incorporated by
reference in 35 Ill. Adm. Code 720.111.
iii)
Method 625 in 40 CFR 136, appendix A, incorporated by
reference in 35 Ill. Adm. Code 720.111. Perform corrections
to the compounds for which the analysis is being conducted
based on the “accuracy as recovery” using the factors in Table
7 of the method.
iv)
Method 1624 in 40 CFR 136, appendix A, incorporated by
reference in 35 Ill. Adm. Code 720.111.
v)
Method 1625 in 40 CFR 136, appendix A, incorporated by
reference in 35 Ill. Adm. Code 720.111.
vi)
Method 8260 in “Test Methods for Evaluating Solid Waste,
Physical/Chemical Methods”, USEPA Publication SW-846,
incorporated by reference in 35 Ill. Adm. Code 720.111.
Maintain a formal quality assurance program consistent with the
requirements of Method 8260. The quality assurance program
must include the elements set forth in subsection (b)(3)(E) of
this Section.
112
vii)
Method 8270 in “Test Methods for Evaluating Solid Waste,
Physical/Chemical Methods”, USEPA Publication SW-846,
incorporated by reference in 35 Ill. Adm. Code 720.111.
Maintain a formal quality assurance program consistent with the
requirements of Method 8270. The quality assurance program
must include the elements set forth in subsection (b)(3)(E) of
this Section.
viii)
Any other USEPA standard method that has been validated in
accordance with “Alternative Validation Procedure for EPA
Waste and Wastewater Methods”, 40 CFR 63, appendix D,
incorporated by reference in 35 Ill. Adm. Code 720.111. As
an alternative, other USEPA standard methods may be
validated by the procedure specified in subsection (b)(3)(C)(ix)
of this Section.
ix)
Any other analysis method that has been validated in
accordance with the procedures specified in Section 5.1 or
Section 5.3, and the corresponding calculations in Section 6.1
or Section 6.3, of Method 301 in 40 CFR 63, appendix A.
The data are acceptable if they meet the criteria specified in
Section 6.1.5 or Section 6.3.3 of Method 301. If correction is
required under Section 6.3.3 of Method 301, the data are
acceptable if the correction factor is within the range 0.7 to
1.30. Other Sections of Method 301 are not required.
D)
Calculations. The average VO concentration ( C ) on a mass-weighted
basis must be calculated by using the results for all samples analyzed in
accordance with subsection (b)(3)(C) of this Section and the following
equation:
C =
1
Q
x
n
i = 1
(Q x C )
T
i
i
∑
Where:
C =
Average VO concentration of the hazardous waste at
the point of waste treatment on a mass-weighted basis,
in ppmw.
113
i =
Individual determination “i” of the hazardous waste.
n =
Total number of waste determinations of the hazardous
waste collected for the averaging period (not to exceed
1 year).
Q
i
=
Mass quantity of the hazardous waste stream
represented by C
i
, in kg/hr.
Q
T
=
Total mass quantity of hazardous waste during the
averaging period, in kg/hr.
C
i
=
Measured VO concentration of waste determinations
“i”, as determined in accordance with the requirements
of subsection (b)(3)(C) of this Section (i.e., the
average of the four or more samples specified in
subsection (b)(3)(B)(ii) of this Section), in ppmw.
E)
Provided that the test method is appropriate for the waste as required
under subsection (b)(3)(C) of this Section, compliance shall must be
determined based on the test method used by the owner or operator as
recorded pursuant to Section 725.990(f)(1).
4)
Procedure to determine the exit concentration limit (C
t
) for a treated hazardous
waste.
A)
The point of waste origination for each hazardous waste treated by the
process at the same time must be identified.
B)
If a single hazardous waste stream is identified in subsection (b)(4)(A)
of this Section, then the exit concentration limit (C
t
) must be 500 ppmw.
C)
If more than one hazardous waste stream is identified in subsection
(b)(4)(A) of this Section, then the average VO concentration of each
hazardous waste stream at the point of waste origination must be
determined in accordance with the requirements of subsection (a) of this
Section. The exit concentration limit (C
t
) must be calculated by using
the results determined for each individual hazardous waste stream and
the following equation:
114
t
x
x
y
x
y
C
=
m
x = 1
(Q
x C
) +
n
y = 1
(Q
x500ppmw)
m
x = 1
Q
+
n
y = 1
Q
∑
∑
∑
∑
Where:
C
t
=
Exit concentration limit for treated hazardous waste, in
ppmw.
x =
Individual hazardous waste stream “x” that has an
average VO concentration less than 500 ppmw at the
point of waste origination, as determined in accordance
with the requirements of subsection (a) of this Section.
y =
Individual hazardous waste stream “y” that has an
average VO concentration equal to or greater than 500
ppmw at the point of waste origination, as determined in
accordance with the requirements of subsection (a) of
this Section.
m =
Total number of “x” hazardous waste streams treated
by process.
n =
Total number of “y” hazardous waste streams treated
by process.
Q
x
=
Annual mass quantity of hazardous waste stream “x”, in
kg/yr.
Q
y
=
Annual mass quantity of hazardous waste stream “y”, in
kg/yr.
C
x
=
Average VO concentration of hazardous waste stream
“x” at the point of waste origination, as determined in
accordance with the requirements of subsection (a) of
this Section, in ppmw.
5)
Procedure to determine the organic reduction efficiency (R) for a treated
hazardous waste.
115
A)
The organic reduction efficiency (R) for a treatment process must be
determined based on results for a minimum of three consecutive runs.
B)
All hazardous waste streams entering the process and all hazardous
waste streams exiting the treatment process must be identified. The
owner or operator shall prepare a sampling plan for measuring these
streams that accurately reflects the retention time of the hazardous
waste in the process.
C)
For each run, information must be determined for each hazardous waste
stream identified in subsection (b)(5)(B) of this Section, using the
following procedures:
i)
The mass quantity of each hazardous waste stream entering the
process (Q
b
) and the mass quantity of each hazardous waste
stream exiting the process (Q
a
) must be determined.
ii)
The average VO concentration at the point of waste origination
of each hazardous waste stream entering the process (C
b
)
during the run must be determined in accordance with the
requirements of subsections (a)(3) of this Section. The average
VO concentration at the point of waste treatment of each
hazardous waste stream exiting the process (C
a
) during the run
must be determined in accordance with the requirements of
subsection (b)(3) of this Section.
D)
The waste volatile organic mass flow entering the process (E
b
) and the
waste volatile organic mass flow exiting the process (E
a
) must be
calculated by using the results determined in accordance with subsection
(b)(5)(C) of this Section and the following equations:
b
6
bj
bj
E
=
1
10
m
j = 1
(Q
xC
)
∑
a
6
aj
aj
E
=
1
10
m
j = 1
(Q
xC
)
∑
Where:
116
E
a
=
Waste volatile organic mass flow exiting the process, in
kg/hr.
E
b
=
Waste volatile organic mass flow entering the process,
in kg/hr.
m =
Total number of runs (at least 3)
j =
Individual run “j”
Q
bj
=
Mass quantity of hazardous waste entering the process
during run “j”, in kg/hr.
Q
aj
=
Average mass quantity of waste exiting the process
during run “j”, in kg/hr.
aj
C
=
Average VO concentration of hazardous waste exiting
the process during run “j”, as determined in accordance
with the requirements of subsection (b)(3) of this
Section, in ppmw.
bj
C
=
Average VO concentration of hazardous waste entering
the process during run “j”, as determined in accordance
with the requirements of subsection 725.984 (a)(3) of
this Section, in ppmw.
E)
The organic reduction efficiency of the process must be calculated by
using the results determined in accordance with subsection (b)(5)(D) of
this Section and the following equation:
R =
E
- E
E
x100%
b
a
b
Where:
R =
Organic reduction efficiency, in percent.
E
b
=
Waste volatile organic mass flow entering the process
as determined in accordance with the requirements of
subsection (b)(5)(D) of this Section, in kg/hr.
E
a
=
Waste volatile organic mass flow exiting the process as
117
determined in accordance with the requirements of
subsection (b)(5)(D) of this Section, in kg/hr.
6)
Procedure to determine the organic biodegradation efficiency (R
bio
) for a
treated hazardous waste.
A)
The fraction of organics biodegraded (F
bio
) must be determined using
the procedure specified in 40 CFR 63, Appendix C, incorporated by
reference in 35 Ill. Adm. Code 720.111.
B)
The organic biodegradation efficiency (R
bio
) must be calculated by using
the following equation:
bio
bio
R
= F
x100%
Where
R
bio
=
Organic biodegradation efficiency, in percent.
F
bio
=
Fraction of organic biodegraded, as determined in
accordance with the requirements of subsection
(b)(6)(A) of this Section.
7)
Procedure to determine the required organic mass removal rate (RMR) for a
treated hazardous waste.
A)
All of the hazardous waste streams entering the treatment process must
be identified.
B)
The average VO concentration of the hazardous waste stream at the
point of waste origination must be determined in accordance with the
requirements of subsection (a) of this Section.
C)
For each individual hazardous waste stream that has an average volatile
organic concentration equal to or greater than 500 ppmw at the point of
waste origination, the average volumetric flow rate of hazardous waste
and the density of the hazardous waste stream at the point of waste
origination must be determined.
D)
The required organic mass removal rate (RMR) for the hazardous
waste must be calculated by using the average VO concentration,
average volumetric flow rate, and density determined for each individual
hazardous waste stream, and the following equation:
118
RMR =
n
y = 1
V
x k
x
(C
-500ppmw)
10
y
y
y
6
∑
Where:
RMR =
Required organic mass removal rate, in kg/hr.
y =
Individual hazardous waste stream “y” that has an average
volatile organic (VO) concentration equal to or greater than 500
ppmw at the point of waste origination, as determined in
accordance with the requirements of subsection (a) of this
Section.
n =
Total number of “y” hazardous waste streams treated by
process.
V
y
=
Average volumetric flow rate of hazardous waste stream “y” at
the point of waste origination, in m
3
/hr.
k
y
=
Density of hazardous waste stream “y”, in kg/m
3
C
y
=
Average VO concentration of hazardous waste stream “y” at
the point of waste origination, as determined in accordance with
the requirements of subsection (a) of this Section, in ppmw.
8)
Procedure to determine the actual organic mass removal rate (MR) for a treated
hazardous waste.
A)
The actual organic mass removal rate (MR) must be determined based
on results for a minimum of three consecutive runs. The sampling time
for each run must be one hour.
B)
The waste volatile organic mass flow entering the process (E
b
) and the
waste volatile organic mass flow exiting the process (E
a
) must be
determined in accordance with the requirements of subsection (b)(5)(D)
of this Section.
C)
The actual organic mass removal rate (MR) must be calculated by using
the mass flow rate determined in accordance with the requirements of
subsection (b)(8)(B) of this Section and the following equation:
119
MR = E
- E
b
a
Where:
MR =
Actual organic mass removal rate, in kg/hr.
E
b
=
Waste volatile organic mass flow entering the process,
as determined in accordance with the requirements of
subsection (b)(5)(D) of this Section, in kg/hr.
E
a
=
Waste volatile organic mass flow exiting the process, as
determined in accordance with the requirements of
subsection (b)(5)(D) of this Section, in kg/hr.
9)
Procedure to determine the actual organic mass biodegradation rate (MR
bio
) for
a treated hazardous waste.
A)
The actual organic mass biodegradation rate (MR
bio
) must be
determined based on results for a minimum of three consecutive runs.
The sampling time for each run must be one hour.
B)
The waste organic mass flow entering the process (E
b
) must be
determined in accordance with the requirements of subsection (b)(5)(D)
of this Section.
C)
The fraction of organic biodegraded (F
bio
) must be determined using the
procedure specified in 40 CFR 63, Appendix C, incorporated by
reference in 35 Ill. Adm. Code 720.111.
D)
The actual organic mass biodegradation rate (MR
bio
) must be calculated
by using the mass flow rates and fraction of organic biodegraded, as
determined in accordance with the requirements of subsections
(b)(9)(B) and (b)(9)(C) of this Section, respectively, and the following
equation:
bio
b
bio
MR
= E
x F
Where:
MR
bio
=
Actual organic mass biodegradation rate, in
kg/hr.
120
E
b
=
Waste organic mass flow entering the process, as
determined in accordance with the requirements of
subsection (b)(5)(D) of this Section, in kg/hr.
F
bio
=
Fraction of organic biodegraded, as determined in
accordance with the requirements of subsection
(b)(9)(C) of this Section.
c)
Procedure to determine the maximum organic vapor pressure of a hazardous waste in a
tank.
1)
An owner or operator shall determine the maximum organic vapor pressure for
each hazardous waste placed in a tank using Tank Level 1 controls in
accordance with standards specified in Section 725.985(c).
2)
An owner or operator shall use either direct measurement, as specified in
subsection (c)(3) of this Section, or knowledge of the waste, as specified by
subsection (c)(4) of this Section, to determine the maximum organic vapor
pressure that is representative of the hazardous waste composition stored or
treated in the tank.
3)
Direct measurement to determine the maximum organic vapor pressure of a
hazardous waste.
A)
Sampling. A sufficient number of samples must be collected to be
representative of the waste contained in the tank. All samples must be
conducted and handled in accordance with written procedures
prepared by the owner or operator and documented in a site sampling
plan. This plan must describe the procedure by which representative
samples of the hazardous waste are collected such so that a minimum
loss of organics occurs throughout the sample collection and handling
process and by which sample integrity is maintained. A copy of the
written sampling plan must be maintained on-site in the facility operating
records. An example of an acceptable sampling plan includes a plan
incorporating sample collection and handling procedures in accordance
with the requirements specified in “Test Methods for Evaluating Solid
Waste, Physical/Chemical Methods”, USEPA Publication No. SW-
846, incorporated by reference in 35 Ill. Adm. Code 720.111, or in
Method 25D in 40 CFR 60, appendix A, incorporated by reference in
35 Ill. Adm. Code 720.111.
B)
Analysis. Any appropriate one of the following methods may be used
to analyze the samples and compute the maximum organic vapor
121
pressure of the hazardous waste:
i)
Method 25E in 40 CFR 60, Appendix A, incorporated by
reference in 35 Ill. Adm. Code 720.111;
ii)
Methods described in American Petroleum Institute Publication
2517, incorporated by reference in 35 Ill. Adm. Code
720.111;
iii)
Methods obtained from standard reference texts;
iv)
ASTM Method D 2879-92, incorporated by reference in 35
Ill. Adm. Code 720.111; or
v)
Any other method approved by the Agency.
4)
Use of knowledge to determine the maximum organic vapor pressure of the
hazardous waste. Documentation must be prepared and recorded that presents
the information used as the basis for the owner’s or operator’s knowledge that
the maximum organic vapor pressure of the hazardous waste is less than the
maximum vapor pressure limit listed in Section 725.985(b)(1)(A) for the
applicable tank design capacity category. An example of information that may
be used is documentation that the hazardous waste is generated by a process
for which at other locations it previously has been determined by direct
measurement that the waste maximum organic vapor pressure is less than the
maximum vapor pressure limit for the appropriate tank design capacity
category.
d)
Procedure for determining no detectable organic emissions for the purpose of complying
with this Subpart:
1)
The test must be conducted in accordance with the procedures specified in
Method 21 of 40 CFR 60, appendix A, incorporated by reference in 35 Ill.
Adm. Code 720.111. Each potential leak interface (i.e., a location where
organic vapor leakage could occur) on the cover and associated closure
devices must be checked. Potential leak interfaces that are associated with
covers and closure devices include, but are not limited to any of the following:
the interface of the cover and its foundation mounting, the periphery of any
opening on the cover and its associated closure device, and the sealing seat
interface on a spring-loaded pressure relief valve.
2)
The test must be performed when the unit contains a hazardous waste having an
organic concentration representative of the range of concentrations for the
122
hazardous waste expected to be managed in the unit. During the test, the cover
and closure devices must be secured in the closed position.
3)
The detection instrument must meet the performance criteria of Method 21 of
40 CFR 60, appendix A, incorporated by reference in 35 Ill. Adm. Code
720.111, except the instrument response factor criteria in Section 3.1.2(a) of
Method 21 must be for the average composition of the organic constituents in
the hazardous waste placed in the waste management unit, not for each
individual organic constituent.
4)
The detection instrument must be calibrated before use on each day of its use
by the procedures specified in Method 21 of 40 CFR 60, appendix A,
incorporated by reference in 35 Ill. Adm. Code 720.111.
5)
Calibration gases must be as follows:
A)
Zero air (less than 10 ppmv hydrocarbon in air), and
B)
A mixture of methane or n-hexane in air at a concentration of
approximately, but less than, 10,000 ppmv methane or n-hexane.
6)
The background level must be determined according to the procedures in
Method 21 of 40 CFR 60, appendix A, incorporated by reference in 35 Ill.
Adm. Code 720.111.
7)
Each potential leak interface must be checked by traversing the instrument
probe around the potential leak interface as close to the interface as possible, as
described in Method 21 of 40 CFR 60, appendix A, incorporated by reference
in 35 Ill. Adm. Code 720.111. In the case when the configuration of the cover
or closure device prevents a complete traverse of the interface, all accessible
portions of the interface must be sampled. In the case when the configuration of
the closure device prevents any sampling at the interface and the device is
equipped with an enclosed extension or horn (e.g., some pressure relief
devices), the instrument probe inlet must be placed at approximately the center
of the exhaust area to the atmosphere.
8)
The arithmetic difference between the maximum organic concentration indicated
by the instrument and the background level must be compared with the value of
500 ppmv except when monitoring a seal around a rotating shaft that passes
through a cover opening, in which case the comparison must be as specified in
subsection (d)(9) of this Section. If the difference is less than 500 ppmv, then
the potential leak interface is determined to operate with no detectable organic
emissions.
123
9)
For the seals around a rotating shaft that passes through a cover opening, the
arithmetic difference between the maximum organic concentration indicated by
the instrument and the background level must be compared with the value of
10,000 ppmw. If the difference is less than 10,000 ppmw, then the potential
leak interface is determined to operate with no detectable organic emissions.
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
Section 725.985
Standards: Tanks
a)
The provisions of this Section apply to the control of air pollutant emissions from tanks
for which Section 725.983(b) references the use of this Section for such air emission
control.
b)
The owner or operator shall control air pollutant emissions from each tank subject to
this Section in accordance with the following requirements, as applicable:
1)
For a tank that manages hazardous waste which meets all of the conditions
specified in subsections (b)(1)(A) through (b)(1)(C) of this Section, the owner
or operator shall control air pollutant emissions from the tank in accordance
with the Tank Level 1 controls specified in subsection (c) of this Section or the
Tank Level 2 controls specified in subsection (d) of this Section.
A)
The hazardous waste in the tank has a maximum organic vapor pressure
that is less than the maximum organic vapor pressure limit for the tank’s
design capacity category, as follows:
i)
For a tank design capacity equal to or greater than 151 m
3
(5333 ft
3
or 39,887 gal), the maximum organic vapor pressure
limit for the tank is 5.2 kPa (0.75 psia or 39 mm Hg);
ii)
For a tank design capacity equal to or greater than 75 m
3
(2649
ft
3
or 19,810 gal) but less than 151 m
3
(5333 ft
3
or 39,887 gal),
the maximum organic vapor pressure limit for the tank is 27.6
kPa (4.0 psia or 207 mm Hg); or
iii)
For a tank design capacity less than 75 m
3
(2649 ft
3
or 19,810
gal), the maximum organic vapor pressure limit for the tank is
76.6 kPa (11.1 psia or 574 mm Hg).
B)
The hazardous waste in the tank is not heated by the owner or operator
to a temperature that is greater than the temperature at which the
124
maximum organic vapor pressure of the hazardous waste is determined
for the purpose of complying with subsection (b)(1)(A) of this Section.
C)
The hazardous waste in the tank is not treated by the owner or operator
using a waste stabilization process, as defined in Section 725.981.
2)
For a tank that manages hazardous waste that does not meet all of the
conditions specified in subsections (b)(1)(A) through (b)(1)(C) of this Section,
the owner or operator shall control air pollutant emissions from the tank by
using Tank Level 2 controls in accordance with the requirements of subsection
(d) of this Section. Examples of tanks required to use Tank Level 2 controls
include the following: a tank used for a waste stabilization process and a tank
for which the hazardous waste in the tank has a maximum organic vapor
pressure that is equal to or greater than the maximum organic vapor pressure
limit for the tank’s design capacity category, as specified in subsection (b)(1)(A)
of this Section.
c)
Owners and operators controlling air pollutant emissions from a tank using Tank Level 1
controls shall meet the requirements specified in subsections (c)(1) through (c)(4) of this
Section:
1)
The owner or operator shall determine the maximum organic vapor pressure for
a hazardous waste to be managed in the tank using Tank Level 1 controls
before the first time the hazardous waste is placed in the tank. The maximum
organic vapor pressure must be determined using the procedures specified in
Section 725.984(c). Thereafter, the owner or operator shall perform a new
determination whenever changes to the hazardous waste managed in the tank
could potentially cause the maximum organic vapor pressure to increase to a
level that is equal to or greater than the maximum organic vapor pressure limit
for the tank design capacity category specified in subsection (b)(1)(A) of this
Section, as applicable to the tank.
2)
The tank must be equipped with a fixed roof designed to meet the following
specifications:
A)
The fixed roof and its closure devices must be designed to form a
continuous barrier over the entire surface area of the hazardous waste in
the tank. The fixed roof may be a separate cover installed on the tank
(e.g., a removable cover mounted on an open-top tank) or may be an
integral part of the tank structural design (e.g., a horizontal cylindrical
tank equipped with a hatch).
B)
The fixed roof must be installed in such a manner such that there are no
125
visible cracks, holes, gaps, or other open spaces between roof section
joints or between the interface of the roof edge and the tank wall.
C)
Either of the following must be true of each opening in the fixed roof and
of any manifold system associated with the fixed roof must be either:
i)
The opening or manifold system is equipped with a closure
device designed to operate such so that when the closure
device is secured in the closed position there are no visible
cracks, holes, gaps, or other open spaces in the closure device
or between the perimeter of the opening and the closure device;
or
ii)
The opening or manifold system is connected by a closed-vent
system that is vented to a control device. The control device
must remove or destroy organics in the vent stream, and it must
be operating whenever hazardous waste is managed in the tank,
except as provided for in subsection (c)(2)(E).
D)
The fixed roof and its closure devices must be made of suitable
materials that will minimize exposure of the hazardous waste to the
atmosphere, to the extent practical, and which will maintain the integrity
of the fixed roof and closure devices throughout their intended service
life. Factors to be considered when selecting the materials for and
designing the fixed roof and closure devices must include the following:
organic vapor permeability; the effects of any contact with the
hazardous waste or its vapors managed in the tank; the effects of
outdoor exposure to wind, moisture, and sunlight; and the operating
practices used for the tank on which the fixed roof is installed.
E)
The control device operated pursuant to subsection (c)(2)(C) of this
Section needs not remove or destroy organics in the vent stream under
the following conditions:
i)
During periods when it is necessary to provide access to the
tank for performing the activities of subsection (c)(2)(E)(ii) of
this Section, venting of the vapor headspace underneath the
fixed roof to the control device is not required, opening of
closure devices is allowed, and removal of the fixed roof is
allowed. Following completion of the activity, the owner or
operator shall promptly secure the closure device in the closed
position or reinstall the cover, as applicable, and resume
operation of the control device; and
126
ii)
During periods of routine inspection, maintenance, or other
activities needed for normal operations, and for the removal of
accumulated sludge or other residues from the bottom of the
tank.
BOARD NOTE: Subsections (c)(2)(E)(i) and (c)(2)(E)(ii) are derived
from 40 CFR 265.985(c)(2)(iii)(B)(1) and (c)(2)(iii)(B)(2), which the
Board has codified here to comport with Illinois Administrative Code
format requirements.
3)
Whenever a hazardous waste is in the tank, the fixed roof must be installed with
each closure device secured in the closed position, except as follows:
A)
Opening of closure devices or removal of the fixed roof is allowed at
the following times:
i)
To provide access to the tank for performing routine inspection,
maintenance, or other activities needed for normal operations.
Examples of such activities include those times when a worker
needs to open a port to sample the liquid in the tank, or when a
worker needs to open a hatch to maintain or repair equipment.
Following completion of the activity, the owner or operator shall
promptly secure the closure device in the closed position or
reinstall the cover, as applicable, to the tank.
ii)
To remove accumulated sludge or other residues from the
bottom of tank.
B)
Opening of a spring-loaded pressure-vacuum relief valve, conservation
vent, or similar type of pressure relief device which that vents to the
atmosphere is allowed during normal operations for the purpose of
maintaining the tank internal pressure in accordance with the tank design
specifications. The device must be designed to operate with no
detectable organic emissions when the device is secured in the closed
position. The settings at which the device opens must be established
such so that the device remains in the closed position whenever the tank
internal pressure is within the internal pressure operating range
determined by the owner or operator based on the tank manufacturer
recommendations; applicable regulations; fire protection and prevention
codes; standard engineering codes and practices; or other requirements
for the safe handling of flammable, ignitable, explosive, reactive, or
hazardous materials. Examples of normal operating conditions that may
127
require these devices to open are during those times when the tank
internal pressure exceeds the internal pressure operating range for the
tank as a result of loading operations or diurnal ambient temperature
fluctuations.
C)
Opening of a safety device, as defined in Section 725.981, is allowed at
any time conditions require doing so to avoid an unsafe condition.
4)
The owner or operator shall inspect the air emission control equipment in
accordance with the following requirements.
A)
The fixed roof and its closure devices must be visually inspected by the
owner or operator to check for defects that could result in air pollutant
emissions. Defects include, but are not limited to, visible cracks, holes,
or gaps in the roof sections or between the roof and the tank wall;
broken, cracked, or otherwise damaged seals or gaskets on closure
devices; and broken or missing hatches, access covers, caps, or other
closure devices.
B)
The owner or operator shall perform an initial inspection of the fixed
roof and its closure devices on or before the date that the tank becomes
subject to this Section. Thereafter, the owner or operator shall perform
the inspections at least once every year, except under the special
conditions provided for in subsection (l) of this Section.
C)
In the event that a defect is detected, the owner or operator shall repair
the defect in accordance with the requirements of subsection (k) of this
Section.
D)
The owner or operator shall maintain a record of the inspection in
accordance with the requirements specified in Section 725.990(b).
d)
Owners and operators controlling air pollutant emissions from a tank using Tank Level 2
controls shall use one of the following tanks:
1)
A fixed-roof tank equipped with an internal floating roof in accordance with the
requirements specified in subsection (e) of this Section;
2)
A tank equipped with an external floating roof in accordance with the
requirements specified in subsection (f) of this Section;
3)
A tank vented through a closed-vent system to a control device in accordance
with the requirements specified in subsection (g) of this Section;
128
4)
A pressure tank designed and operated in accordance with the requirements
specified in subsection (h) of this Section; or
5)
A tank located inside an enclosure that is vented through a closed-vent system
to an enclosed combustion control device in accordance with the requirements
specified in subsection (i) of this Section.
e)
The owner or operator that controls air pollutant emissions from a tank using a fixed
roof with an internal floating roof shall meet the requirements specified in subsections
(e)(1) through (e)(3) of this Section.
1)
The tank must be equipped with a fixed roof and an internal floating roof in
accordance with the following requirements:
A)
The internal floating roof must be designed to float on the liquid surface
except when the floating roof must be supported by the leg supports.
B)
The internal floating roof must be equipped with a continuous seal
between the wall of the tank and the floating roof edge that meets either
of the following requirements:
i)
A single continuous seal that is either a liquid-mounted seal or a
metallic shoe seal, as defined in Section 725.981; or
ii)
Two continuous seals mounted one above the other. The lower
seal may be a vapor-mounted seal.
C)
The internal floating roof must meet the following specifications:
i)
Each opening in a noncontact internal floating roof except for
automatic bleeder vents (vacuum breaker vents) and the rim
space vents is to provide a projection below the liquid surface.
ii)
Each opening in the internal floating roof must be equipped with
a gasketed cover or a gasketed lid except for leg sleeves,
automatic bleeder vents, rim space vents, column wells, ladder
wells, sample wells, and stub drains.
iii)
Each penetration of the internal floating roof for the purpose of
sampling must have a slit fabric cover that covers at least 90
percent of the opening.
129
iv)
Each automatic bleeder vent and rim space vent must be
gasketed.
v)
Each penetration of the internal floating roof that allows for
passage of a ladder must have a gasketed sliding cover.
vi)
Each penetration of the internal floating roof that allows for
passage of a column supporting the fixed roof must have a
flexible fabric sleeve seal or a gasketed sliding cover.
2)
The owner or operator shall operate the tank in accordance with the following
requirements:
A)
When the floating roof is resting on the leg supports, the process of
filling, emptying, or refilling must be continuous and must be completed
as soon as practical.
B)
Automatic bleeder vents are to be set closed at all times when the roof
is floating, except when the roof is being floated off or is being landed
on the leg supports.
C)
Prior to filling the tank, each cover, access hatch, gauge float well or lid
on any opening in the internal floating roof must be bolted or fastened
closed (i.e., no visible gaps). Rim space vents are to be set to open
only when the internal floating roof is not floating or when the pressure
beneath the rim exceeds the manufacturer’s recommended setting.
3)
The owner or operator shall inspect the internal floating roof in accordance with
the procedures specified as follows:
A)
The floating roof and its closure devices must be visually inspected by
the owner or operator to check for defects that could result in air
pollutant emissions. Defects include, but are not limited to, the
following: when the internal floating roof is not floating on the surface of
the liquid inside the tank; when liquid has accumulated on top of the
internal floating roof; when any portion of the roof seals have detached
from the roof rim; when holes, tears, or other openings are visible in the
seal fabric; when the gaskets no longer close off the hazardous waste
surface from the atmosphere; or when the slotted membrane has more
than 10 percent open area.
B)
The owner or operator shall inspect the internal floating roof
components as follows, except as provided in subsection (e)(3)(C) of
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this Section:
i)
Visually inspect the internal floating roof components through
openings on the fixed roof (e.g., manholes and roof hatches) at
least once every 12 months after initial fill, and
ii)
Visually inspect the internal floating roof, primary seal,
secondary seal (if one is in service), gaskets, slotted
membranes, and sleeve seals (if any) each time the tank is
emptied and degassed and at least once every 10 years.
C)
As an alternative to performing the inspections specified in subsection
(e)(3)(B) of this Section for an internal floating roof equipped with two
continuous seals mounted one above the other, the owner or operator
may visually inspect the internal floating roof, primary and secondary
seals, gaskets, slotted membranes, and sleeve seals (if any) each time
the tank is emptied and degassed and at least every five years.
D)
Prior to each inspection required by subsection (e)(3)(B) or (e)(3)(C)
of this Section, the owner or operator shall notify the Agency in
advance of each inspection to provide the Agency with the opportunity
to have an observer present during the inspection. The owner or
operator shall notify the Agency of the date and location of the
inspection as follows:
i)
Prior to each visual inspection of an internal floating roof in a
tank that has been emptied and degassed, written notification
must be prepared and sent by the owner or operator so that it is
received by the Agency at least 30 calendar days before refilling
the tank, except when an inspection is not planned, as provided
for in subsection (e)(3)(D)(ii) of this Section.
ii)
When a visual inspection is not planned and the owner or
operator could not have known about the inspection 30
calendar days before refilling the tank, the owner or operator
shall notify the Agency as soon as possible, but no later than
seven calendar days before refilling of the tank. This notification
may be made by telephone and immediately followed by a
written explanation for why the inspection is unplanned.
Alternatively, written notification, including the explanation for
the unplanned inspection, may be sent so that it is received by
the Regional Administrator at least seven calendar days before
refilling the tank.
131
E)
In the event that a defect is detected, the owner or operator shall repair
the defect in accordance with the requirements of subsection (k) of this
Section.
F)
The owner or operator shall maintain a record of the inspection in
accordance with the requirements specified in Section 725.990(b).
4)
Safety devices, as defined in Section 725.981, may be installed and operated as
necessary on any tank complying with the requirements of this subsection (e).
f)
The owner or operator that controls air pollutant emissions from a tank using an external
floating roof shall meet the requirements specified in subsections (f)(1) through (f)(3) of
this Section.
1)
The owner or operator shall design the external floating roof in accordance with
the following requirements:
A)
The external floating roof must be designed to float on the liquid surface
except when the floating roof must be supported by the leg supports.
B)
The floating roof must be equipped with two continuous seals, one
above the other, between the wall of the tank and the roof edge. The
lower seal is referred to as the primary seal, and the upper seal is
referred to as the secondary seal.
i)
The primary seal must be a liquid-mounted seal or a metallic
shoe seal, as defined in Section 725.981. The total area of the
gaps between the tank wall and the primary seal must not
exceed 212 square centimeters (cm
2
) per meter (10.0 in
2
per
foot) of tank diameter, and the width of any portion of these
gaps must not exceed 3.8 centimeters (cm) (1.5 inches). If a
metallic shoe seal is used for the primary seal, the metallic shoe
seal must be designed so that one end extends into the liquid in
the tank and the other end extends a vertical distance of at least
61 centimeters (24 inches) above the liquid surface.
ii)
The secondary seal must be mounted above the primary seal
and cover the annular space between the floating roof and the
wall of the tank. The total area of the gaps between the tank
wall and the secondary seal must not exceed 21.2 cm
2
per
meter (1.0 in
2
per foot) of tank diameter, and the width of any
portion of these gaps must not exceed 1.3 cm (0.5 inch).
132
C)
The external floating roof must meet the following specifications:
i)
Except for automatic bleeder vents (vacuum breaker vents) and
rim space vents, each opening in a noncontact external floating
roof must provide a projection below the liquid surface.
ii)
Except for automatic bleeder vents, rim space vents, roof
drains, and leg sleeves, each opening in the roof must be
equipped with a gasketed cover, seal, or lid.
iii)
Each access hatch and each gauge float well must be equipped
with a cover designed to be bolted or fastened when the cover
is secured in the closed position.
iv)
Each automatic bleeder vent and each rim space vent must be
equipped with a gasket.
v)
Each roof drain that empties into the liquid managed in the tank
must be equipped with a slotted membrane fabric cover that
covers at least 90 percent of the area of the opening.
vi)
Each unslotted and slotted guide pole well must be equipped
with a gasketed sliding cover or a flexible fabric sleeve seal.
vii)
Each unslotted guide pole must be equipped with a gasketed
cap on the end of the pole.
viii)
Each slotted guide pole must be equipped with a gasketed float
or other device which that closes off the liquid surface from the
atmosphere.
ix)
Each gauge hatch and each sample well must be equipped with
a gasketed cover.
2)
The owner or operator shall operate the tank in accordance with the following
requirements:
A)
When the floating roof is resting on the leg supports, the process of
filling, emptying, or refilling must be continuous and must be completed
as soon as practical.
B)
Except for automatic bleeder vents, rim space vents, roof drains, and
133
leg sleeves, each opening in the roof must be secured and maintained in
a closed position at all times except when the closure device must be
open for access.
C)
Covers on each access hatch and each gauge float well must be bolted
or fastened when secured in the closed position.
D)
Automatic bleeder vents must be set closed at all times when the roof is
floating, except when the roof is being floated off or is being landed on
the leg supports.
E)
Rim space vents must be set to open only at those times that the roof is
being floated off the roof leg supports or when the pressure beneath the
rim seal exceeds the manufacturer’s recommended setting.
F)
The cap on the end of each unslotted guide pole must be secured in the
closed position at all times except when measuring the level or collecting
samples of the liquid in the tank.
G)
The cover on each gauge hatch or sample well must be secured in the
closed position at all times except when the hatch or well must be
opened for access.
H)
Both the primary seal and the secondary seal must completely cover the
annular space between the external floating roof and the wall of the tank
in a continuous fashion except during inspections.
3)
The owner or operator shall inspect the external floating roof in accordance with
the procedures specified as follows:
A)
The owner or operator shall measure the external floating roof seal gaps
in accordance with the following requirements:
i)
The owner or operator shall perform measurements of gaps
between the tank wall and the primary seal within 60 calendar
days after initial operation of the tank following installation of the
floating roof and, thereafter, at least once every five years.
ii)
The owner or operator shall perform measurements of gaps
between the tank wall and the secondary seal within 60
calendar days after initial operation of the tank following
installation of the floating roof and, thereafter, at least once
every year.
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iii)
If a tank ceases to hold hazardous waste for a period of one
year or more, subsequent introduction of hazardous waste into
the tank must be considered an initial operation for the purposes
of subsections (f)(3)(A)(i) and (f)(3)(A)(ii) of this Section.
iv)
The owner or operator shall determine the total surface area of
gaps in the primary seal and in the secondary seal individually
using the procedure set forth in subsection (f)(4)(D) of this
Section.
v)
In the event that the seal gap measurements do not conform to
the specifications in subsection (f)(1)(B) of this Section, the
owner or operator must repair the defect in accordance with the
requirements of subsection (k) of this Section.
vi)
The owner or operator shall maintain a record of the inspection
in accordance with the requirements specified in Section
725.990(b).
B)
The owner or operator shall visually inspect the external floating roof in
accordance with the following requirements:
i)
The floating roof and its closure devices must be visually
inspected by the owner or operator to check for defects that
could result in air pollutant emissions. Defects include, but are
not limited to any of the following: holes, tears, or other
openings in the rim seal or seal fabric of the floating roof; a rim
seal detached from the floating roof; all or a portion of the
floating roof deck being submerged below the surface of the
liquid in the tank; broken, cracked, or otherwise damaged seals
or gaskets on closure devices; and broken or missing hatches,
access covers, caps, or other closure devices.
ii)
The owner or operator shall perform an initial inspection of the
external floating roof and its closure devices on or before the
date that the tank becomes subject to this Section. Thereafter,
the owner or operator shall perform the inspections at least
once every year except for the special conditions provided for
in subsection (l) of this Section.
iii)
In the event that a defect is detected, the owner or operator
shall repair the defect in accordance with the requirements of
135
subsection (k) of this Section.
iv)
The owner or operator shall maintain a record of the inspection
in accordance with the requirements specified in Section
725.990(b).
C)
Prior to each inspection required by subsection (f)(3)(A) or (f)(3)(B) of
this Section, the owner or operator shall notify the Agency in advance
of each inspection to provide the Agency with the opportunity to have
an observer present during the inspection. The owner or operator shall
notify the Agency of the date and location of the inspection as follows:
i)
Prior to each inspection to measure external floating roof seal
gaps as required under subsection (f)(3)(A) of this Section,
written notification must be prepared and sent by the owner or
operator so that it is received by the Agency at least 30
calendar days before the date the measurements are scheduled
to be performed.
ii)
Prior to each visual inspection of an external floating roof in a
tank that has been emptied and degassed, written notification
must be prepared and sent by the owner or operator so that it is
received by the Agency at least 30 calendar days before refilling
the tank except when an inspection is not planned, as provided
for in subsection (f)(3)(C)(iii) of this Section.
iii)
When a visual inspection is not planned and the owner or
operator could not have known about the inspection 30
calendar days before refilling the tank, the owner or operator
shall notify the Agency as soon as possible, but no later than
seven calendar days before refilling of the tank. This notification
may be made by telephone and immediately followed by a
written explanation for why the inspection is unplanned.
Alternatively, written notification, including the explanation for
the unplanned inspection, may be sent so that it is received by
the Regional Administrator at least seven calendar days before
refilling the tank.
D)
Procedure for determining gaps in the primary seal and in the secondary
seal for the purposes of subsection (f)(3)(A)(iv) of this Section:
i)
The seal gap measurements must be performed at one or more
floating roof levels when the roof is floating off the roof
136
supports.
ii)
Seal gaps, if any, must be measured around the entire perimeter
of the floating roof in each place where a 0.32-cm (¼-inch)
diameter uniform probe passes freely (without forcing or binding
against the seal) between the seal and the wall of the tank and
measure the circumferential distance of each such location.
iii)
For a seal gap measured under this subsection (f)(3), the gap
surface area must be determined by using probes of various
widths to measure accurately the actual distance from the tank
wall to the seal and multiplying each such width by its respective
circumferential distance.
iv)
The total gap area must be calculated by adding the gap surface
areas determined for each identified gap location for the primary
seal and the secondary seal individually, and then dividing the
sum for each seal type by the nominal diameter of the tank.
These total gap areas for the primary seal and secondary seal
are then compared to the respective standards for the seal type,
as specified in subsection (f)(1)(B) of this Section.
BOARD NOTE: Subsections (f)(3)(D)(i) through (f)(3)(D)(iv) are
derived from 40 CFR 265.1085(f)(3)(i)(D)(1) through (f)(3)(i)(D)(4),
which the Board has codified here to comport with Illinois
Administrative Code format requirements.
4)
Safety devices, as defined in Section 725.981, may be installed and operated as
necessary on any tank complying with the requirements of this subsection (f).
g)
The owner or operator that controls air pollutant emissions from a tank by venting the
tank to a control device shall meet the requirements specified in subsections (g)(1)
through (g)(3) of this Section.
1)
The tank must be covered by a fixed roof and vented directly through a closed-
vent system to a control device in accordance with the following requirements:
A)
The fixed roof and its closure devices must be designed to form a
continuous barrier over the entire surface area of the liquid in the tank.
B)
Each opening in the fixed roof not vented to the control device must be
equipped with a closure device. If the pressure in the vapor headspace
underneath the fixed roof is less than atmospheric pressure when the
137
control device is operating, the closure devices must be designed to
operate such so that when the closure device is secured in the closed
position there are no visible cracks, holes, gaps, or other open spaces in
the closure device or between the perimeter of the cover opening and
the closure device. If the pressure in the vapor headspace underneath
the fixed roof is equal to or greater than atmospheric pressure when the
control device is operating, the closure device must be designed to
operate with no detectable organic emissions.
C)
The fixed roof and its closure devices must be made of suitable
materials that will minimize exposure of the hazardous waste to the
atmosphere, to the extent practical, and will maintain the integrity of the
fixed roof and closure devices throughout their intended service life.
Factors to be considered when selecting the materials for and designing
the fixed roof and closure devices must include the following: organic
vapor permeability; the effects of any contact with the liquid and its
vapor managed in the tank; the effects of outdoor exposure to wind,
moisture, and sunlight; and the operating practices used for the tank on
which the fixed roof is installed.
D)
The closed-vent system and control device must be designed and
operated in accordance with the requirements of Section 725.988.
2)
Whenever a hazardous waste is in the tank, the fixed roof must be installed with
each closure device secured in the closed position and the vapor headspace
underneath the fixed roof vented to the control device except as follows:
A)
Venting to the control device is not required, and opening of closure
devices or removal of the fixed roof is allowed at the following times:
i)
To provide access to the tank for performing routine inspection,
maintenance, or other activities needed for normal operations.
Examples of such activities include those times when a worker
needs to open a port to sample liquid in the tank, or when a
worker needs to open a hatch to maintain or repair equipment.
Following completion of the activity, the owner or operator shall
promptly secure the closure device in the closed position or
reinstall the cover, as applicable, to the tank.
ii)
To remove accumulated sludge or other residues from the
bottom of a tank.
B)
Opening of a safety device, as defined in Section 725.981, is allowed at
138
any time conditions require doing so to avoid an unsafe condition.
3)
The owner or operator shall inspect and monitor the air emission control
equipment in accordance with the following procedures:
A)
The fixed roof and its closure devices must be visually inspected by the
owner or operator to check for defects that could result in air pollutant
emissions. Defects include, but are not limited to any of the following:
visible cracks, holes, or gaps in the roof sections or between the roof
and the tank wall; broken, cracked, or otherwise damaged seals or
gaskets on closure devices; and broken or missing hatches, access
covers, caps, or other closure devices.
B)
The closed-vent system and control device must be inspected and
monitored by the owner or operator in accordance with the procedures
specified in Section 725.988.
C)
The owner or operator shall perform an initial inspection of the air
emission control equipment on or before the date that the tank becomes
subject to this Section. Thereafter, the owner or operator shall perform
the inspections at least once every year except for the special conditions
provided for in subsection (l) of this Section.
D)
In the event that a defect is detected, the owner or operator shall repair
the defect in accordance with the requirements of subsection (k) of this
Section.
E)
The owner or operator shall maintain a record of the inspection in
accordance with the requirements specified in Section 725.990(b).
h)
The owner or operator that controls air pollutant emissions by using a pressure tank
must meet the following requirements.
1)
The tank shall must be designed not to vent to the atmosphere as a result of
compression of the vapor headspace in the tank during filling of the tank to its
design capacity.
2)
All tank openings must be equipped with closure devices designed to operate
with no detectable organic emissions as determined using the procedure
specified in Section 725.984(d).
3)
Whenever a hazardous waste is in the tank, the tank must be operated as a
closed-vent system that does not vent to the atmosphere, except in the event
139
that a safety device, as defined in 35 Ill. Adm. Code 725.981, is required to
open to avoid an unsafe condition. under either of the following two conditions:
A) The tank does not need to be operated as a closed-vent system at
those times when the opening of a safety device, as defined in Section
725.981, is required to avoid an unsafe condition.
B) The tank does not need to be operated as a closed-vent system at
those times when the purging of inerts from the tank is required and the
purge stream is routed to a closed-vent system and control device
designed and operated in accordance with the requirements of Section
724.987.
i)
The owner or operator that controls air pollutant emissions by using an enclosure vented
through a closed-vent system to an enclosed combustion control device shall meet the
requirements specified in subsections (i)(1) through (i)(4) of this Section.
1)
The tank must be located inside an enclosure. The enclosure must be designed
and operated in accordance with the criteria for a permanent total enclosure, as
specified in “Procedure T--Criteria for and Verification of a Permanent or
Temporary Total Enclosure” under 40 CFR 52.741, appendix B, incorporated
by reference in 35 Ill. Adm. Code 720.111. The enclosure may have
permanent or temporary openings to allow worker access; passage of material
into or out of the enclosure by conveyor, vehicles, or other mechanical means;
entry of permanent mechanical or electrical equipment; or direct airflow into the
enclosure. The owner or operator shall perform the verification procedure for
the enclosure as specified in Section 5.0 to “Procedure T--Criteria for and
Verification of a Permanent or Temporary Total Enclosure” initially when the
enclosure is first installed and, thereafter, annually.
2)
The enclosure must be vented through a closed-vent system to an enclosed
combustion control device that is designed and operated in accordance with the
standards for either a vapor incinerator, boiler, or process heater specified in
Section 725.988.
3)
Safety devices, as defined in Section 725.981, may be installed and operated as
necessary on any enclosure, closed-vent system, or control device used to
comply with the requirements of subsections (i)(1) and (i)(2) of this Section.
4)
The owner or operator shall inspect and monitor the closed-vent system and
control device, as specified in Section 725.988.
j)
The owner or operator shall transfer hazardous waste to a tank subject to this Section in
140
accordance with the following requirements:
1)
Transfer of hazardous waste, except as provided in subsection (j)(2) of this
Section, to the tank from another tank subject to this Section or from a surface
impoundment subject to Section 725.986 must be conducted using continuous
hard-piping or another closed system that does not allow exposure of the
hazardous waste to the atmosphere. For the purpose of complying with this
provision, an individual drain system is considered to be a closed system when it
meets the requirements of 40 CFR 63, subpart RR, “National Emission
Standards for Individual Drain Systems”, incorporated by reference in 35 Ill.
Adm. Code 720.111.
2)
The requirements of subsection (j)(1) of this Section do not apply when
transferring a hazardous waste to the tank under any of the following conditions:
A)
The hazardous waste meets the average VO concentration conditions
specified in Section 725.983(c)(1) at the point of waste origination.
B)
The hazardous waste has been treated by an organic destruction or
removal process to meet the requirements in Section 725.983(c)(2).
C)
The hazardous waste meets the requirements of Section 725.983(c)(4).
k)
The owner or operator shall repair each defect detected during an inspection performed
in accordance with the requirements of subsection (c)(4), (e)(3), (f)(3), or (g)(3) of this
Section as follows:
1)
The owner or operator shall make first efforts at repair of the defect no later
than five calendar days after detection, and repair shall must be completed as
soon as possible but no later than 45 calendar days after detection except as
provided in subsection (k)(2) of this Section.
2)
Repair of a defect may be delayed beyond 45 calendar days if the owner or
operator determines that repair of the defect requires emptying or temporary
removal from service of the tank and no alternative tank capacity is available at
the site to accept the hazardous waste normally managed in the tank. In this
case, the owner or operator shall repair the defect the next time the process or
unit that is generating the hazardous waste managed in the tank stops operation.
Repair of the defect must be completed before the process or unit resumes
operation.
l)
Following the initial inspection and monitoring of the cover as required by the applicable
provisions of this Subpart, subsequent inspection and monitoring may be performed at
141
intervals longer than one year under the following special conditions:
1)
Where inspecting or monitoring the cover would expose a worker to
dangerous, hazardous, or other unsafe conditions, then the owner or operator
may designate a cover as an “unsafe to inspect and monitor cover” and comply
with all of the following requirements:
A)
Prepare a written explanation for the cover stating the reasons why the
cover is unsafe to visually inspect or to monitor, if required.
B)
Develop and implement a written plan and schedule to inspect and
monitor the cover, using the procedures specified in the applicable
Section of this Subpart, as frequently as practicable during those times
when a worker can safely access the cover.
2)
In the case when a tank is buried partially or entirely underground, an owner or
operator is required to inspect and monitor, as required by the applicable
provisions of this Section, only those portions of the tank cover and those
connections to the tank (e.g., fill ports, access hatches, gauge wells, etc.) that
are located on or above the ground surface.
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)
Section 725.987
Standards: Containers
a)
The provisions of this Section apply to the control of air pollutant emissions from
containers for which Section 725.983(b) references the use of this Section for such air
emission control.
b)
General requirements.
1)
The owner or operator shall control air pollutant emissions from each container
subject to this Section in accordance with the following requirements, as
applicable to the container, except when the special provisions for waste
stabilization processes specified in subsection (b)(2) of this Section apply to the
container.
A)
For a container having a design capacity greater than 0.1 m
3
(26 gal)
and less than or equal to 0.46 m
3
(120 gal), the owner or operator shall
control air pollutant emissions from the container in accordance with the
Container Level 1 standards specified in subsection (c) of this Section.
B)
For a container having a design capacity greater than 0.46 m
3
(120 gal)
142
that is not in light material service, the owner or operator shall control
air pollutant emissions from the container in accordance with the
Container Level 1 standards specified in subsection (c) of this Section.
C)
For a container having a design capacity greater than 0.46 m
3
(120 gal)
that is in light material service, the owner or operator shall control air
pollutant emissions from the container in accordance with the Container
Level 2 standards specified in subsection (d) of this Section.
2)
When a container having a design capacity greater than 0.1 m
3
(26 gal) is used
for treatment of a hazardous waste by a waste stabilization process, the owner
or operator shall control air pollutant emissions from the container in
accordance with the Container Level 3 standards specified in subsection (e) of
this Section at those times during the waste stabilization process when the
hazardous waste in the container is exposed to the atmosphere.
c)
Container Level 1 standards.
1)
A container using Container Level 1 controls is one of the following:
A)
A container that meets the applicable U.S. Department of
Transportation (USDOT) regulations on packaging hazardous materials
for transportation, as specified in subsection (f) of this Section.
B)
A container equipped with a cover and closure devices that form a
continuous barrier over the container openings so that when the cover
and closure devices are secured in the closed position there are no
visible holes, gaps, or other open spaces into the interior of the
container. The cover may be a separate cover installed on the container
(e.g., a lid on a drum or a suitably secured tarp on a roll-off box) or
may be an integral part of the container structural design (e.g., a
“portable tank” or bulk cargo container equipped with a screw-type
cap).
C)
An open-top container in which an organic-vapor suppressing barrier is
placed on or over the hazardous waste in the container such so that no
hazardous waste is exposed to the atmosphere. One example of such a
barrier is application of a suitable organic-vapor suppressing foam.
2)
A container used to meet the requirements of subsection (c)(1)(B) or (c)(1)(C)
of this Section must be equipped with covers and closure devices, as applicable
to the container, that are composed of suitable materials to minimize exposure
of the hazardous waste to the atmosphere and to maintain the equipment
143
integrity for as long as it is in service. Factors to be considered in selecting the
materials of construction and designing the cover and closure devices must
include the following: the organic vapor permeability, the effects of contact with
the hazardous waste or its vapor managed in the container; the effects of
outdoor exposure of the closure device or cover material to wind, moisture, and
sunlight; and the operating practices for which the container is intended to be
used.
3)
Whenever a hazardous waste is in a container using Container Level 1 controls,
the owner or operator shall install all covers and closure devices for the
container, as applicable to the container, and secure and maintain each closure
device in the closed position except as follows:
A)
Opening of a closure device or cover is allowed for the purpose of
adding hazardous waste or other material to the container as follows:
i)
In the case when the container is filled to the intended final level
in one continuous operation, the owner or operator shall
promptly secure the closure devices in the closed position and
install the covers, as applicable to the container, upon
conclusion of the filling operation.
ii)
In the case when discrete quantities or batches of material
intermittently are added to the container over a period of time,
the owner or operator shall promptly secure the closure devices
in the closed position and install covers, as applicable to the
container, upon either the container being filled to the intended
final level; the completion of a batch loading after which no
additional material will be added to the container within 15
minutes; the person performing the loading operation leaving the
immediate vicinity of the container; or the shutdown of the
process generating the material being added to the container,
whichever condition occurs first.
B)
Opening of a closure device or cover is allowed for the purpose of
removing hazardous waste from the container as follows:
i)
For the purpose of meeting the requirements of this Section, an
empty container, as defined in 35 Ill. Adm. Code 721.107(b),
may be open to the atmosphere at any time (i.e., covers and
closure devices are not required to be secured in the closed
position on an empty container).
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ii)
In the case when discrete quantities or batches of material are
removed from the container but the container does not meet the
conditions to be an empty container, as defined in 35 Ill. Adm.
Code 721.107(b), the owner or operator shall promptly secure
the closure devices in the closed position and install covers, as
applicable to the container, upon the completion of a batch
removal after which no additional material will be removed from
the container within 15 minutes or the person performing the
unloading operation leaves the immediate vicinity of the
container, whichever condition occurs first.
C)
Opening of a closure device or cover is allowed when access inside the
container is needed to perform routine activities other than transfer of
hazardous waste. Examples of such activities include those times when
a worker needs to open a port to measure the depth of or sample the
material in the container, or when a worker needs to open a manhole
hatch to access equipment inside the container. Following completion
of the activity, the owner or operator shall promptly secure the closure
device in the closed position or reinstall the cover, as applicable to the
container.
D)
Opening of a spring-loaded, pressure-vacuum relief valve, conservation
vent, or similar type of pressure relief device which that vents to the
atmosphere is allowed during normal operations for the purpose of
maintaining the container internal pressure in accordance with the design
specifications of the container. The device must be designed to operate
with no detectable organic emissions when the device is secured in the
closed position. The settings at which the device opens must be
established such so that the device remains in the closed position
whenever the internal pressure of the container is within the internal
pressure operating range determined by the owner or operator based
on container manufacturer recommendations, applicable regulations, fire
protection and prevention codes, standard engineering codes and
practices, or other requirements for the safe handling of flammable,
ignitable, explosive, reactive, or hazardous materials. Examples of
normal operating conditions that may require these devices to open are
during those times when the internal pressure of the container exceeds
the internal pressure operating range for the container as a result of
loading operations or diurnal ambient temperature fluctuations.
E)
Opening of a safety device, as defined in Section 725.981, is allowed at
any time conditions require doing so to avoid an unsafe condition.
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4)
The owner or operator of containers using Container Level 1 controls must
inspect the containers and their covers and closure devices as follows:
A)
In the case when a hazardous waste already is in the container at the
time the owner or operator first accepts possession of the container at
the facility and the container is not emptied within 24 hours after the
container is accepted at the facility (i.e., it does not meet the conditions
for an empty container as specified in 35 Ill. Adm. Code 721.107(b)),
the owner or operator shall visually inspect the container and its cover
and closure devices to check for visible cracks, holes, gaps, or other
open spaces into the interior of the container when the cover and
closure devices are secured in the closed position. The container visual
inspection must be conducted on or before the date on which the
container is accepted at the facility (i.e., the date when the container
becomes subject to the Subpart CC container standards). For the
purposes of this requirement, the date of acceptance is the date of
signature that the facility owner or operator enters on Item 20 of the
Uniform Hazardous Waste Manifest incorporated by reference in 35 Ill.
Adm. Code 722.Appendix A (USEPA Forms 8700-22 and 8700-
22A), as required under Section 725.171. If a defect is detected, the
owner or operator shall repair the defect in accordance with the
requirements of subsection (c)(4)(C) of this Section.
B)
In the case when a container used for managing hazardous waste
remains at the facility for a period of one year or more, the owner or
operator shall visually inspect the container and its cover and closure
devices initially and thereafter, at least once every 12 months, to check
for visible cracks, holes, gaps, or other open spaces into the interior of
the container when the cover and closure devices are secured in the
closed position. If a defect is detected, the owner or operator shall
repair the defect in accordance with the requirements of subsection
(c)(4)(C) of this Section.
C)
When a defect is detected for the container, cover, or closure devices,
the owner or operator shall make first efforts at repair of the defect no
later than 24 hours after detection, and repair must be completed as
soon as possible but no later than five calendar days after detection. If
repair of a defect cannot be completed within five calendar days, then
the hazardous waste must be removed from the container and the
container must not be used to manage hazardous waste until the defect
is repaired.
5)
The owner or operator shall maintain at the facility a copy of the procedure
146
used to determine that containers with capacity of 0.46 m
3
(120 gal) or greater,
which do not meet applicable USDOT regulations as specified in subsection (f)
of this Section, are not managing hazardous waste in light material service.
d)
Container Level 2 standards.
1)
A container using Container Level 2 controls is one of the following:
A)
A container that meets the applicable U.S. Department of
Transportation (USDOT) regulations on packaging hazardous materials
for transportation as specified in subsection (f) of this Section.
B)
A container that operates with no detectable organic emissions, as
defined in Section 725.981, and determined in accordance with the
procedure specified in subsection (g) of this Section.
C)
A container that has been demonstrated within the preceding 12 months
to be vapor-tight by using 40 CFR 60, appendix A, Method 27,
incorporated by reference in 35 Ill. Adm. Code 720.111, in
accordance with the procedure specified in subsection (h) of this
Section.
2)
Transfer of hazardous waste in or out of a container using Container Level 2
controls must be conducted in such a manner as to minimize exposure of the
hazardous waste to the atmosphere, to the extent practical, considering the
physical properties of the hazardous waste and good engineering and safety
practices for handling flammable, ignitable, explosive, reactive or other
hazardous materials. Examples of container loading procedures that the
USEPA considers to meet the requirements of this subsection (d)(2) include
using any one of the following: a submerged-fill pipe or other submerged-fill
method to load liquids into the container; a vapor-balancing system or a vapor-
recovery system to collect and control the vapors displaced from the container
during filling operations; or a fitted opening in the top of a container through
which the hazardous waste is filled and subsequently purging the transfer line
before removing it from the container opening.
3)
Whenever a hazardous waste is in a container using Container Level 2 controls,
the owner or operator shall install all covers and closure devices for the
container, and secure and maintain each closure device in the closed position,
except as follows:
A)
Opening of a closure device or cover is allowed for the purpose of
adding hazardous waste or other material to the container as follows:
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i)
In the case when the container is filled to the intended final level
in one continuous operation, the owner or operator shall
promptly secure the closure devices in the closed position and
install the covers, as applicable to the container, upon
conclusion of the filling operation.
ii)
In the case when discrete quantities or batches of material
intermittently are added to the container over a period of time,
the owner or operator shall promptly secure the closure devices
in the closed position and install covers, as applicable to the
container, upon either the container being filled to the intended
final level; the completion of a batch loading after which no
additional material will be added to the container within 15
minutes; the person performing the loading operation leaving the
immediate vicinity of the container; or the shutdown of the
process generating the material being added to the container,
whichever condition occurs first.
B)
Opening of a closure device or cover is allowed for the purpose of
removing hazardous waste from the container as follows:
i)
For the purpose of meeting the requirements of this Section, an
empty container as defined in 35 Ill. Adm. Code 721.107(b)
may be open to the atmosphere at any time (i.e., covers and
closure devices are not required to be secured in the closed
position on an empty container).
ii)
In the case when discrete quantities or batches of material are
removed from the container but the container does not meet the
conditions to be an empty container as defined in 35 Ill. Adm.
Code 721.107(b), the owner or operator shall promptly secure
the closure devices in the closed position and install covers, as
applicable to the container, upon the completion of a batch
removal after which no additional material will be removed from
the container within 15 minutes or the person performing the
unloading operation leaves the immediate vicinity of the
container, whichever condition occurs first.
C)
Opening of a closure device or cover is allowed when access inside the
container is needed to perform routine activities other than transfer of
hazardous waste. Examples of such activities include those times when
a worker needs to open a port to measure the depth of or sample the
148
material in the container, or when a worker needs to open a manhole
hatch to access equipment inside the container. Following completion
of the activity, the owner or operator shall promptly secure the closure
device in the closed position or reinstall the cover, as applicable to the
container.
D)
Opening of a spring-loaded, pressure-vacuum relief valve, conservation
vent, or similar type of pressure relief device which that vents to the
atmosphere is allowed during normal operations for the purpose of
maintaining the internal pressure of the container in accordance with the
container design specifications. The device must be designed to
operate with no detectable organic emission when the device is secured
in the closed position. The settings at which the device opens must be
established such so that the device remains in the closed position
whenever the internal pressure of the container is within the internal
pressure operating range determined by the owner or operator based
on container manufacturer recommendations, applicable regulations, fire
protection and prevention codes, standard engineering codes and
practices, or other requirements for the safe handling of flammable,
ignitable, explosive, reactive, or hazardous materials. Examples of
normal operating conditions that may require these devices to open are
during those times when the internal pressure of the container exceeds
the internal pressure operating range for the container as a result of
loading operations or diurnal ambient temperature fluctuations.
E)
Opening of a safety device, as defined in Section 725.981, is allowed at
any time conditions require doing so to avoid an unsafe condition.
4)
The owner or operator of containers using Container Level 2 controls shall
inspect the containers and their covers and closure devices as follows:
A)
In the case when a hazardous waste already is in the container at the
time the owner or operator first accepts possession of the container at
the facility and the container is not emptied within 24 hours after the
container is accepted at the facility (i.e., it does not meet the conditions
for an empty container as specified in 35 Ill. Adm. Code 721.107(b)),
the owner or operator shall visually inspect the container and its cover
and closure devices to check for visible cracks, holes, gaps, or other
open spaces into the interior of the container when the cover and
closure devices are secured in the closed position. The container visual
inspection must be conducted on or before the date on which the
container is accepted at the facility (i.e., the date when the container
becomes subject to the Subpart CC container standards). For the
149
purposes of this requirement, the date of acceptance is the date of
signature that the facility owner or operator enters on Item 20 of the
Uniform Hazardous Waste Manifest incorporated by reference in 35 Ill.
Adm. Code 722.Appendix A (USEPA Forms 8700-22 and 8700-
22A), as required under Section 725.171. If a defect is detected, the
owner or operator shall repair the defect in accordance with the
requirements of subsection (d)(4)(C) of this Section.
B)
In the case when a container used for managing hazardous waste
remains at the facility for a period of one year or more, the owner or
operator shall visually inspect the container and its cover and closure
devices initially and thereafter, at least once every 12 months, to check
for visible cracks, holes, gaps, or other open spaces into the interior of
the container when the cover and closure devices are secured in the
closed position. If a defect is detected, the owner or operator shall
repair the defect in accordance with the requirements of subsection
(d)(4)(C) of this Section.
C)
When a defect is detected for the container, cover, or closure devices,
the owner or operator shall make first efforts at repair of the defect no
later than 24 hours after detection, and repair must be completed as
soon as possible but no later than five calendar days after detection. If
repair of a defect cannot be completed within five calendar days, then
the hazardous waste must be removed from the container and the
container must not be used to manage hazardous waste until the defect
is repaired.
e)
Container Level 3 standards.
1)
A container using Container Level 3 controls is one of the following:
A)
A container that is vented directly through a closed-vent system to a
control device in accordance with the requirements of subsection
(e)(2)(B) of this Section.
B)
A container that is vented inside an enclosure which is exhausted
through a closed-vent system to a control device in accordance with the
requirements of subsections (e)(2)(A) and (e)(2)(B) of this Section.
2)
The owner or operator shall meet the following requirements, as applicable to
the type of air emission control equipment selected by the owner or operator:
A)
The container enclosure must be designed and operated in accordance
150
with the criteria for a permanent total enclosure as specified in
“Procedure T--Criteria for and Verification of a Permanent or
Temporary Total Enclosure” under 40 CFR 52.741, appendix B,
incorporated by reference in 35 Ill. Adm. Code 720.111. The
enclosure may have permanent or temporary openings to allow worker
access; passage of containers through the enclosure by conveyor or
other mechanical means; entry of permanent mechanical or electrical
equipment; or direct airflow into the enclosure. The owner or operator
shall perform the verification procedure for the enclosure as specified in
Section 5.0 to “Procedure T--Criteria for and Verification of a
Permanent or Temporary Total Enclosure” initially when the enclosure is
first installed and, thereafter, annually.
B)
The closed-vent system and control device must be designed and
operated in accordance with the requirements of Section 725.988.
3)
Safety devices, as defined in Section 725.981, may be installed and operated as
necessary on any container, enclosure, closed-vent system, or control device
used to comply with the requirements of subsection (e)(1) of this Section.
4)
Owners and operators using Container Level 3 controls in accordance with the
provisions of this Subpart shall inspect and monitor the closed-vent systems and
control devices, as specified in Section 725.988.
5)
Owners and operators that use Container Level 3 controls in accordance with
the provisions of this Subpart shall prepare and maintain the records specified in
Section 725.990(d).
6) The transfer of hazardous waste into or out of a container using Container Level
3 controls must be conducted in such a manner as to minimize exposure of the
hazardous waste to the atmosphere, to the extent practical considering the
physical properties of the hazardous waste and good engineering and safety
practices for handling flammable, ignitable, explosive, reactive, or other
hazardous materials. Examples of container loading procedures that USEPA
considers to meet the requirements of this subsection (e)(6) include using any
one of the following: the use of a submerged-fill pipe or other submerged-fill
method to load liquids into the container; the use of a vapor-balancing system or
a vapor-recovery system to collect and control the vapors displaced from the
container during filling operations; or the use of a fitted opening in the top of a
container through which the hazardous waste is filled and subsequently purging
the transfer line before removing it from the container opening.
f)
For the purpose of compliance with subsection (c)(1)(A) or (d)(1)(A) of this Section,
151
containers must be used that meet the applicable U.S. Department of Transportation
(USDOT) regulations on packaging hazardous materials for transportation as follows:
1)
The container meets the applicable requirements specified in 49 CFR 178,
“Specifications for Packaging”, or 49 CFR 179, “Specifications for Tank
Cars”, both incorporated by reference in 35 Ill. Adm. Code 720.111.
2)
Hazardous waste is managed in the container in accordance with the applicable
requirements specified in 49 CFR 107, subpart B, “Exemptions”; 49 CFR 172,
“Hazardous Materials Table, Special Provisions, Hazardous Materials
Communications, Emergency Response Information, and Training
Requirements”; 49 CFR 173, “Shippers--General Requirements for Shipments
and Packages”; and 49 CFR 180, “Continuing Qualification and Maintenance
of Packagings”, each incorporated by reference in 35 Ill. Adm. Code 720.111.
3)
For the purpose of complying with this Subpart, no exceptions to the 49 CFR
178 or 179 regulations are allowed, except as provided for in subsection (f)(4)
of this Section.
4)
For a lab pack that is managed in accordance with the requirements of 49 CFR
178 for the purpose of complying with this Subpart, an owner or operator may
comply with the exceptions for combination packagings specified in 49 CFR
173.12(b), incorporated by reference in 35 Ill. Adm. Code 720.111.
g)
To determine compliance with the no detectable organic emissions requirements of
subsection (d)(1)(B) of this Section, the procedure specified in Section 725.984(d)
must be used.
1)
Each potential leak interface (i.e., a location where organic vapor leakage could
occur) on the container, its cover, and associated closure devices, as applicable
to the container, must be checked. Potential leak interfaces that are associated
with containers include, but are not limited to: the interface of the cover rim and
the container wall; the periphery of any opening on the container or container
cover and its associated closure device; and the sealing seat interface on a
spring-loaded pressure-relief valve.
2)
The test must be performed when the container is filled with a material having a
volatile organic concentration representative of the range of volatile organic
concentrations for the hazardous wastes expected to be managed in this type of
container. During the test, the container cover and closure devices must be
secured in the closed position.
h)
Procedure The procedure for determining a container to be vapor-tight using Method
152
27 of 40 CFR 60, appendix A for the purpose of complying with subsection (d)(1)(C)
of this Section. is as follows:
1)
The test must be performed in accordance with Method 27 of 40 CFR 60,
appendix A, incorporated by reference in 35 Ill. Adm. Code 720.111.
2)
A pressure measurement device must be used that has a precision of ±2.5 mm
(0.10 inch) water and that is capable of measuring above the pressure at which
the container is to be tested for vapor tightness.
3)
If the test results determined by Method 27 indicate that the container sustains a
pressure change less than or equal to 750 Pascals (0.11 psig) within five
minutes after it is pressurized to a minimum of 4,500 Pascals (0.65 psig), then
the container is determined to be vapor-tight.
(Source: Amended at 24 Ill. Reg. ________, effective ______________________)