ILLINOIS POLLUTION CONTROL BOARD
January 21,
1993
IN
THE
MATTER
OF:
)
)
RCRA UPDATE, USEPA REGULATIONS
)
R92-10
(1/1/92
—
6/30/92)
)
(Identical in Substance
)
Rules)
Ado~tedRule.
Final Order.
OPINION OF
THE
BOARD
(by
3.
Anderson):
By a separate Order, pursuant to Section 7.,2 and 22.4(a) of
the Environmental Protection Act
(Act), the Board is
a~nendingthe
RCRA hazardous waste regulations.
The aLendments involve 35 Iii.
Adin.
Code 702, 703,
720, 721, 724, 725, 726 and 728.
The Board
will not file the adopted rules until 30 days after
the date of
this order, to allow tune for post—adoption coaments,
particularly from the agencies involved in the authorization
process.
Section 22.4 of the Act governs adoption of regulations
establishing the RCRA program in Illinois.
Section 22.4(a)
provides for quick adoption of regulations which are “identical
in substance” to federal regulations; Section 22.4(a) provides
that Title VII of the Act and Section 5 of the Administrative
Procedure Act shall not apply.
Because this rulemaking is not
subject to Section 5 of the.Administrative Procedure Act, it is
not subject to first notice or to second notice review by the
Joint Committee on Administrative Rules (JCAR).
The
federal
RCRA
regulations are found at 40 CFR 260 through 270.
This
rulemaking
updates Illinois’ RCRA rules to correspond with federal
amendments during the period January 1 through June 30, 1992.
The USEPA actions during this period are as follows:
57
Fed.
Req.
Date
Su~mary
14
Jan.
2,
1992
Criteria for listing
toxic hazardous waste.
3486
Jan.
29,
1992
Leak detection system
(“LDS”)
rules for land
disposal units.
5862.
Feb.
18,
1992
Extension of stay for
coatings for wood
preserving drip pads.
7632
Mar.
3,
1992
Mixture and derived-from
rules, “sunset” rule.
8088
Mar.
6,
1992
Third-third corrections.
01381.0765
2
20770
May 15,
1992
General “capacity
variance” for “debris”
21534
May 20,
1992
Exclusion of used oil
filters
.
23063
June 1,
1992
Correction
to mixture and
derived-from rules.
27888
June 22, 1992
Exclusion of coke by-
product residues.
28632
June 26,
1992
National capacity
“variance’
for certain
reclaimed lead storage
batteries.
On July 1,
1992, at 57 Fed. Reg. 29220, USEPA also published
a correction to the May 20 used oil filter rule.
In addition, at
57 Fed. Reg.
30658, July 10,
1992, USEPA published corrections to
the toxicity characteristic leaching procedure
(TCLP) rules.
The
Board will address these corrections in this Docket, even though
the corrections are outside
the time frame of this batch period.
Most of the volume of this rulemaking comes
from the leak
detection system
(“LDS”) rules in the January 29,
1992,
Fed. Reg.
USEPA has provided
the
Board with an electronic copy.
Although
the Board has below noted
a.number of editorial errors with this
large rulemaking, these are of a type and frequency expected in
any large project.
The March 3 and June 1,
1992, Federal Registers added an
April 28,
1993,
“sunset” provision to the “mixture and derived
from” rules in 40 CFR 261.3(e)
(Sections 721.103(a) (2) (D) and
(C)
(2) (A)).
However, USEPA repealed the sunset provision at 57
Fed. Reg. 49278, October 30,
1992.
On November 19,
1992, the
Board entered
an order alerting possible commenters about the
repeal.
Section 7.2 of the Environmental Protection Act limits
identical in substance batch periods to no more than six months.
The
October 30,
1992, repeal of the sunset provision is outside
the batch period for R92-1O, which
began
on January 2,
1992.
However, the Board frequent:’ addresses USEPA corrections with
the origina~adoption of the equivalen.
rule, even if the
corrections tall outside the batch period.
The Board does
n~..t
construe section 7.2 as requiring it to adopt incorrect USEPA
rules pending the proper batch period.
If the Board were to delay proposing the repeal of the
sunset provision until the next update docket dealing with USEPA
actions between July 1 and December 31,
1992,
it would risk being
0~I38-0766
3
unable to take final action
until after
April
28,
1993.
This
could result in a temporary,
but major difference between the
USEPA and Board rules.
The Board will therefore not adopt
the
sunset provision.
USEPA also terminated the wood pr.serving stays
at
57
Fed.
Reg.
61492, December 24,
1992.
As is discussed
below
in
connection with Section 724.673 and 725.543, the Board is
extending
the stays
of the State rules
until
the Board is
able
to
address
the accompanying revisions to the
wood
preserving rules
in R93—4.
The
USEPA amendments include several site—specific
delistings.
As provided in 35 Ill.
Ads.
Code
720.122(p),
as
amended in 1(90-17, the
Board
will not consider adoption of site-
specific delistings as determined by the USEPA unless and
until
someone files a proposal before the Board showing that the waste
will be generated or managed in Illinois.
PUBLIC
The Board adopted a proposal for public comment on
October
16, 1992.
The proposed rules appeared on November 6, 1992, at 16
Ill. Reg. 16776.
The Board has received the following public
conunent:
PC 1
Department of
Commerce
and
Community
Affairs,
Regulatory Flexibility Unit (DCCA), November 12,
1992
PC 2
Administrative Code Division,
December
8, 1992
DCCA indicated that the proposed rules will not
significantly impact small business.
The Code Division noted a
number of minor editorial problems, which have been corrected.
The Board staff has received informal comment from USEPA by
telephone, and has acted on it as discussed below.
The
Board
expects to receive a written comment from USEPA shortly, but,
because of the time limitations discussed below, cannot postpone
this order.
The
Board
will handle this comment
as
post-adoption
comment, and will, if necessary, enter an order modifying this
opinion and order pursuant to the comment.
EXTENSION OF TIME
ORDERS
Section 7.2(b)
of the Act requires that identical in
substance rulemakings be completed within one year after the
first USEPA action in the batch period.
If the Board is unable
to do so it must enter an “extension of time” Order.
The
earliest USEPA action in the Docket was January 2,
1992.
On
December
17,
1992,
the Board entered an extension of time order,
0138-0767
4
indicating that January 21,
1993,
is the anticipated completion
date.
REGULATORY HISTORY
The complete history of
the
RcRA, UST and UIC rules appears
at the end of this opinion.
While a short form of reference to
the adopting opinions will be
used
in
the
body
of this opinion,
complete citations are included in the history.
AGENCY
OR
BOARD
ACTION?
The USEPA RcRA rules contain decisions
which,
as worded, are
to be made by the USEPA Regional Administrator.
These generally
pose a
question
as to who is supposed to make the decision at the
State level:
USEPA, the Board, the
Agency
or some other entity?
Section 7.2(a)(5)
of the Act requires the Board to specify which
decisions USEPA will retain.
In addition, the Board is
to
specify which State agency is to make decisions, based on the
general division of functions within the
Act
and other Illinois
statutes.
In effectuating this requirement, the Board has almost
always changed “Regional Administrator” to
“Agency”.
However, in
some situations “Regional Administrator” has,
been
changed to
“USEPA” or “Board”.
In situations in which the Board has determined that USEPA
will retain decision-making authority, the Board has replaced
“Regional Administrator” with “USEPA”, so as to avoid specifying
which office within USEPA is to make a decision.
In a few instances in identical in substance rules decisions
are not appropriate for Agency action pursuant to a
permit
application.
Among the considerations in determining the general
division of authority between the Agency and the
Board are the
following:
1.
Is the person making the decision applying a
Board
regulation, or taking action contrary to
(“waiving”) a Board regulation?
It generally
takes some form of Board action to “waive” a Board
regulation.
For example, the Agency clearly has
authority to apply a regulation which says “If A,
do X;
if not A, do y”.
On the other hand,
regul tions
which say “If not
A,
the state shall
waive
X’s are
abm.*
troubling.
2.
Is there a clear standard for action such that the
Board can give meaningful review
to an Agency
decision?
3.
Is there a right to appeal?
Agency actions are
generally appealable to the Board.
0138-0758
5
4.
Does this action concern a person who is required
to have a
permit anyway?
If
so there is a pre-
existing permit relationship which can easily be
used as a context for Agency decision.
If the
action concerns a person who does not have a
permit,
it is more difficult to place the decision
into a procedural context which would be within
the
Agency’s
jurisdiction.
Decisions
involving
interim status are often more ambiguous as to
whether
they
are
permit
actions.
5.
Does
the action result in exemption from the
permit
requirement
itself?
If
so,
Board
action
is
generally
required.
6.
Does the decision amount to “determining, defining
or implementing environmental control standards”
within the meaning of Section 5(b) of the Act?
If
so,
it must be made by the Board.
Once it is determined that a decision must be made by the
Board,
rather
than
the Agency, it is necessary to determine what
procedural
context
is
best
suited
for that decision.
There are
four common classes of Board decision:
variance, adjusted
standard,
site specific rulemaking and enforcement.
The first
three are methods by which a regulation can be temporarily
postponed (variance)
or adjusted to meet specific situations
(adjusted standard or site specific rulemaking).
Note that there
are differences in the nomenclature for these decisions between
the
USEPA and Board regulations.
These differences have caused
past misunderstandings with USEPA.
A
variance is initiated by the
operator
filing
a
petition
pursuant to Title IX of the Act and 35 Ill. Ads.
Code 104.
The
Agency files a recommendation as to what action the Board should
take.
The Board may conduct a public hearing,
and must do so if
there is an objection to the variance.
Board variances are:
temporary;
based on arbitrary or
unreasonable hardship;
and,
require a plan for eventual
compliance with the general regulation.
To the extent a USEPA
decision involves these factors, a Board variance is an
appropriate mechanism.
A
variance is not an appropriate mechanism for a decision
which is not based on arbitrary or unreasonable hardship, or
which grants permanent relief without eventual compliance.
To
grant permanent relief, the Board needs to grant a site specific
regulation or an adjusted standard pursuant to Sections 27 or
28.1 of the Act, and 35 Ill.
Ads. Code 102 or 106.
0138-0769
6
EDITORIAL
CONVENTIONS
As a final note,
the
rules have been edited to establish a
uniform usage with respect to “shall”, “must”,
“will”, and “may”.
“Shall” is used when the subject of a sentence has to do
something.
“Must” is used when someone has to do something, but
that someone is not
the
subject of the
sentence.
“Will” is used
when
the
Board
obliges itself to do something.
“May”
is
used
when a provision is optional.
Some of the USEPA
rules
appear to
say something other than what was intended.
Others
do not read
correctly when “Board” or “Agency” is
substituted into the
federal rule.
The
Board does not intend to sake
any
substantive
change
in the rules by way of these
edits.
Much of the text discussed below
exists
both
as
a Board and
USEPA rule.
When
discussing one rule set,
the
Board
has
provided
frequent
citations
to
the
other to aid in cross referencing.
These usually appear in brackets following a citation.
For
example,
“40
CFR
270.4
702.181)”
or “Section 702.181
(270.4”.
The first reference is the rule
set
primarily being discussed,
and the second (in brackets
is
the
equivalent (or comparable)
rule in the other set.
The second reference is usually just the
number, with the “40 CFR”, etc., understood.
The following discussion also includes
many
quotations from
the
Board
and USEPA
rule
sets.
Bold
type
is frequently used to
call attention to specific language within
the
quotes.
The
language
in
bold
is
usually.discussed
following
the
quotation.
PART
702:
RCRA AND
UIC
PERMITS
This
Part
includes
permit
rules
which
apply
to
both
the
RCRA
and UIC
program.
Section 702.181
This
Section
is
derived
from
40
CFR
270.4,
which
was
amended
at 57 Fed. Reg. 3486, January 29,
1992, in connection
with
the
new leak detection’ requirements.
As amended, the USEPA rule
reads as follows:
(a) Compliance with a
RCRA permit during
its
term
constitutes compliance, for purposes of enforcement,
with
subtitle
C
of
RCRA
except
for
those
requirements
not
inca
ided
in
the
permit
which:
1Tbe
USEPA
rules
affect
liners, leachate collection and
removal systems and leak detection systems.
For the sake of
brevity, in this opinion, we will refer to these as “leak
detection”
(or
“LDS”),
except where the discussion focuses on
differences among these.
Ui 38-0770
7
(1) Become effective by statute;
(2)
Are
promulgated under part 268 of this chapter
restricting the placement of hazardous wastes in or on
the
land;
or
(3)
Are
Dromulaated under
Dart
264
of
this
chaDter
reaardina leak detection systems for new and
reolacement surface
impoundment.
waste
pile,
and
landfill
units,
and
lateral
exDansions
of
surface
imnoundsent.
waste
pile,
and
landfill units.
The
leak
detection system r.auirementa
include double liners.
COA Droarams.
monitoring, action leakaae rates, and
resoonse
action
Dlans.
and
will
be
imolemented
throuah
the Drocedures of ~ 270.42 Class 1*
Dermit
modifications.
The Board
rule,
35 Ill. Ads. Code 702.181(a)
is quite
different:
The existence of a
RCRA
or UIC permit does not
constitute a defense to a violation of the
Environmental Protection Act or this Subtitle, except
for development, modification or operation without a
permit.
However,
a
permit
may
be modified, reissued or
revoked
during
its
term
for
cause
as
set
forth
in
35
Ill.
Ads.
Code
703.270
through 703.273
(RCRA)
and
35
Ill.
Ads.
Code
704.261
~through
704.263
(UIC)
and
Section
702.186.
The
Board
and
USEPA
rules
go
in opposite directions with
respect
to
the
effect
of
the
permit:
while
compliance
with
the
USEPA permit
is
deemed compliance with
the
federal
law,
the
State
permit affords no such protection.
In R81-32
(at p.
7)2,
the
Board
determined
that
this
was
required by Illinois law, citing
Landfill.
Inc..
v.
IPCB
(l978~. 74
Ill.
2d
541.
387
N.E.
2d
258.
The
USEPA
amendment
is setting additional limitations on the
extent
to
which the
RCRA
permit
is
an
enforcement
shield.
These
amendments
are
not
needed
in
the
Illinois
program,
since
the
entire
concept is reversed.
The final sentence of the USEPA
amendment
specifies
that
the
“leak detection system requirements include double liners,
CQA
programs,
monitoring, action leakage rates, and response action
plans, and will be implemented through the procedures of § 270.42
Class 1* permit modifications.”
This is unrelated to the “effect
of permit” subject matter of the remainder of the Section.
It is
2As discussed in the regulatory history below, R81—32
Was
the original adoption of the UIC program.
0138-0771
8
possible
that this language needs to
be
inserted
elsewhere.
The
Board
has not, however, done
so,
since
the
language
appears
to
be
merely a statement of intent.
As is
discussed
below,
USEPA
has
specified in the Appendix to Section 270.42 703.App
A
that
these
are
Class
1*
modifications.
Nothing
more
is
needed.
As
is
discussed
in
a
footnote
to
the
1993.
Edition
of
40
CYR
270
•
4(a),
USEPA
inadvertently
dropped
the
following
sentence
in
a
1988
amendment:
Howevir,
a
permit
may
be
modified,
reissued
or
revoked
c~uringits
term
for
cause
as set
forth
The
CFR
indicates
that
USEPA
would
add
the
sentence
back
in
a
future
correction.
USEPA
did
not
do
so
in
this
rulemaking.
The
Board
rule
still
contains
the
sentence,
and
the
Board
will
not
repeal
it at this time.
The Board has updated
the
Board note in this Section, and to
make other minor editorial changes.
However, the substance of
this Section remains the same.
PART
703:
RCRA
PERMITS
This Part
contains
rules
governing
RCRA
permits.
It
is
derived
from
40
CFR
270.
All
of
the
amendments are derived from
the
liner
and
leak detection system
(LDS) rules at 57 Fed. Reg.
3486, January 29,
1992.
Section 703.203
This Section is derived from 40
CFR
270.17, which specifies
the
contents
of
the
RCRA
Part
B
application
module
for
a
surface
impoundment.
The
amendments
(mainly
to
subsection
(b))
reflect
detailed
new
rules, discussed below in
Part
724,
concerning
liners,
leak
detection and removal, and
construction
quality
assurance
(CQA).
As is discussed below in connection with Section 724.321(b),
the
Board
is
utilizing
the
adjusted
standards
procedure
for
the
“alternative
design
and
operating
practices”
determination
for a
surface
impoundment.
At
the
USEPA
level,
40
CFR
270.17(b)
(1)
(703 .203 (b)
(1)
would
require
the
operator
to
submit
information
for
this
determination
with
the
Part
B
permit
application.
At
‘e
State
level,
the
information
would
be
submitted
purs~ant to
a
Part
106
adjusted
sta~dards petition,
as
provided
be...ow
in
Section
724.321(b).
USEPA has informally indicated that
the
adjusted
standards
procedure will be acceptable if it is equivalent to the USEPA
procedure for the “alternative design and operating practices”
0138~0772
9
determination.
At the USEPA level, this would
take
place
as
part
of
the
review
of
a
Part
B permit
application
(or
modification).
As
is
discussed
in
general
above,
under
Illinois
law,
certain decisions under the
RCRA
rules are not appropriate as
Agency decisions, but must be made by the Board.
Section
724.321(b)
falls into this category, since it allows a permittee
to
take
action
contrary
to
the
general
rule.
When
the Board
adopted Section 724.321(b), in R82—19, it
provided
that
this
decision was to be made by variance or site—specific rule.
The
variance mechanism would be of limited use for this
type
of
decision,
since
it
could
be
granted
for
no
more than five years.
Since that time, the
adjusted
standards
mechanism
has
been
added
as Section 28.1 of the Act.
This is a
simpler
and
more
appropriate
procedural
vehicle for this
type
of
Board
decision.
The “justification” for the adjusted standard,
set
forth
below
in
Section 724.321,
is identical to the criteria for grant of this
relief
under
40
CFR
264.221.
The procedures for granting an adjusted standard are set
forth in 35 Ill. Ads. Code 106.Subpart G.
They
provide for a
method of review and public participation which is similar to
that
used
by
USEPA
for
the grant of a Part B
RCRA
permit.
The
procedures were summarized in the R90-l7 opinion, at p.
5, which
discussion is repeated here.
The adjusted standard procedure may be initiated by a
petitioner acting alone, orwith the Agency as a co-petitioner.
(Section 106.703.)
The contents of the petition are specified in
Section 106.705.
If the Agency is not a co—petitioner, it is
required to file a response within 30 days after the filing of
the petition,
in which it must recommend a
grant
or denial of
the
petition, and supporting rationale.
(Section 106.714.)
Within 14 days after the filing of the petition, the
petitioner must publish a public notice of the filing of the
petition in a newspaper in the area likely to be affected.
(Section 106.711.)
The notice gives
members
of
the
public
21
days to request a public hearing.
(Section 106.713.)
The
Board
will schedule a hearing if one is requested,
or if it otherwise
determines that one is advisable.
(Section 106
•
801.)
Interested
persons are allowed to present testimony and exhibits.
(Section
106.806.)
A final comment period is allowed following the public
hearing.
(Section 106.807.)
It would be duplicative to require the information in the
permit application also.
All the Agency needs is a copy of
the
Board order on the adjusted standard.
The Board has therefore
amended Section 703.203(b) (1) as follows:
The liner system
(except for an existing portion of a
surface impoundment).
If an exemption from the
0138-0773
10
requirement
for a liner is sought as provided by 35
Ill. Ada. Code 724.321(b), submit detailed plane and
engineering
and
hydreqeolegio
reperts
an apprepriate,
desoribing alternate design and
eperating
pr*etiees
that
vill,
in
eonjunotien
with le.atien aepseta,
prevent
the
migration
of
-any hosard.uo
sonatituento
into
the
greund-uater
or
surf see
water at
-any
future
4i.e
a
CODV
of
the
Board
order
aranting
an
adjusted
standard
Dursuant
to
35
Ill.
Ada.
Code
724.321(bI
40
CFR
270.17(b)
(5)
requires
the
operator
to
include
a
proposed
“action
leakage
rate”
and
“response action
plan” with
the
application.
These
are
addressed
below
in
connection
with
Section
724.322
and
724.323.
However,
40
CFR
270.17
does
not
require
the
operator
to
include
the
“proposed
pump
operating
level”
addressed in 40
CFR
264.226(d)(3)
724.326(d)(3).
Since
this appears to be a parallel determination, the Board has added
it to Section 703.203(b) (5), so that the Board rule reads:
Proposed
action
leakage
rate,
with
rationale,
if
required under
35
Ill.
Ada.
Code
724.322,
response
action
plan,
if
required
under 35
Ill.
Ada.
Code
724.323,
and
a
proposed
pump operating~evel,
if
required
under
35
Ill.
Ada.
Code
724.326(d)
(3);
Section
703.204
This
Section
is
derived
from
40
CFR
270.18,
which
specifies
the
contents
of
the
RCRA
Part
B
permit
application
module
for
a
waste
pile.
Section
703.204(c)
(1)
(A)
(270.18(c)
(1)(i))
contains
the
permit
application
module
for
the
“alternate
designs”
demonstration
in
Section
724.351(b),
below.
For
the
reasons
discussed
above
with
Section
703.203(b)
(1),
the
Board
is
requiring
a
copy
of
the
Board
order
with
the
permit
application,
rather
than
a
repetition
of
the
information.
The
main
amendments
are
in
Section
703,204
(C)
(1)
(B)
—
(E).
There
are
no
major
problems
with
the
text.
The
language
concerning
the pump operating level is absent from the waste pile
application, as discussed below with Section 724.352.
Section 703.204(d)
(270.18(d)
rrrntains an erroneous cross
reference
which
the
Board
has correct~.d: “703.183(g,~)”.
Section
703.207
This Section is derived from 40
CFR
270.21,
which
specifies
the
contents
of
the
RCRA
Part
B
permit application module for a
landf i.
The
main
amendments
are
to
Section
703.207(b)
(1)
(B)
-
(E).
01 38-o77~
1.
Section
703.207(b)
(l)(A)
(270.21(b)(1)(ifl.contains
the
“alternative
designs”
application
module
related
to
Section
724
•
401 (b), below.
For
the
reasons
discussed
above
in
connection
with
Section
703.203(b)
(1)
(A),
the Board
is replacing the
detailed
information
request
in
the
application
with
a
requirement
to
include
the
Board
order
granting
the
adjusted
standard.
The
Board
has
added
a
“proposed
pump
operating
level”
to
this
Section
for
use
in
Section
724.403(c)
(3),
below,
for
reasons
similar
to
those
discussed
above.
The
text
of
Section
703.207(b)(1)(E)
is:
proposed action leakage rate, with rationale, if
required under 35 Ill. Ada.
Code 724.402,
and
response
action plan,
if required under 35 Ill. Ada. Code
724.404, and proposed pump operating level,
if required
under
35 Ill.
Ada.
Code
724.403;
The Federal Register for 40
CFR
270.21(b) (1) (v) contains an
erroneous cross reference to “264.303” for the response action
plan, which the Board has corrected
in
703.207(b) (1) (E)).
This
should read “264.304” (724.404.~
The
Fed. Reg. includes a revised text for section 270.21(c)
(703.207(c)):
(c) A description of how each landfill, including the
double liner system, leachate collection and removal
system,
leak detection system,
cover
system,
and
appurtenances for control of
run—on and
run—off, will
be
inspected
in
order
to
meet
the
requirements
of
~
264.303(a),
(b),
and
(c)
of
this
chapter.
This
information must be included in
the
inspection
plan
submitted
under
§
270.14(b)
(5);
The
existing
language
of
Section
270.21(c)
(703.207(c))
governs
the
permit
application
for
the
“exemption”
of
former
Section
264.302
(724.402),
which
was
repealed following HSWA
(RB6-1).
Retention
of
the
Section
was
an
error
in
both
the
USEPA
and
Board
rules.
The
new
language
governs
the
“inspection
plan”
associated
with
the
LDS
rules.
The
text
of
Section
703.207(c)
(270.21(c)
is:
3This is somewhat confusing, because the USEPA rule is
citing to the pump operating level instead of the response action
plan.
However,
as discussed above, the Board is modifying this
rule
to address both the pump operating level and the response
action plan.
Therefore Section 724.403 winds up also being
cited
in the Board rule.
0138-0775
12
A description of how each landfill, including the
double liner system, leachate collection and removal
system, leak detection system, cover system, and
appurtenances for control of run-on and run-off, will
be inspected in order to meet the requirements of 35
Ill. Ada. Code 724.403(a),
(b),
and
(c).
This
information must be included in the inspection plan
submitted under Section 703
•
183
(e);
This language in similar to Section 270.21(d)
(703.207(d)).
The Board solicited comment on the possibility that USEPA
intended to amend that Section,
rather than to replace subsection
(C).
Another possibility was that subsection
(d) continued to
govern landfills which are not subject to the LDS rules.
The
Board received no response, and has retained Section 703.207(d)
(270.21(d)):
A description
of how each landfill, including the
liner and cover systems, will be inspected in order to
meet
the
requirements
of
the
35
Ill.
Ada.
Code
724.403(a) and
(b).
This information cb.~4must be
included in the inspection plan submitted under Section
703.183(e);
Section 703.Appendix A
This Appendix is drawn
frOm
40
CFR 270.42, Appendix I.
It
specifies the
type
of
permit
modification
procedure
to be used
for various changes.
The amendments add items
(B) (7),
(H) (6) and
(7),. and
(J)
(7) and (8), dealing with changes to the construction
quality assurance (CQA)
plan, and modifications to meet the new
liner and leak detection and removal requirements.
The
procedures are specified in Section 703.280 ct seq.,
which
are
not
involved
in
this rulemaking.
The permittee may
make a Class 1 change followed by notification to
the
Agency.
The
permittee must notify the Agency in advance of a Class
2
change, and may make the change unless the Agency objects.
Class
3 modifications require prior approval.
Several of the new types of changes are “Class 1*”.
As
provided in Section 703.281(a) (2) and
(b), the Agency
must
give
prior written approval for a Class 1* change.
Public notice is
given following the Agency approval.
PART
720:
GENERAL
PROVISIONS
This
Part
specifies
definitions,
incorporations
by
reference
and other general provisions governing the hazardous waste
program.
It is
drawn
from 40
CFR
260.
The USEPA amendments are
drawn entirely from 57 Fed. Reg. 3486, January 29,
1992, the
amendments to the liner and leak detection requirements.
0138-0776
13
Section 720.110
Definitions
The proposed definition of “qualified groundwater scientist”
was adopted in R92-1, with revisions to the text.
Therefore, the
text has been revised to conform with R92-l,
and
the
underlining
has been removed.
The
Board
has
added
a
definition
of
“LDS”,
an
acronym
for
“leak detection system” which is used sporadically in the USEPA
rules.
The Board will use this acronym in this opinion, and in
the body of the rules.
The
Board
will
restate
the
definition
of
the
acronym at places to avoid confusion.
USEPA has added a new definition and amended a second:
“replacement unit” and “suap”.
The first definition poses
several
problems.
It reads as follows:
Replacement unit means a landfill, surface
impoundment, or waste pile unit
(1)
from which all or
substantially all of the waste is removed, and
(2)
that
is subsequently reused to treat, store, or dispose of
hazardous waste. “Replacement unit” does not apply to a
unit from which waste is removed during closure, if the
subsequent reuse solely involves the disposal of waste
from that unit and other closing units or corrective
action areas at the facility,
in
accordance
with an
approved
closure
plan
or
IPA or
Itate
approved
corrective action.
The structure of the definition violates
two
basic Code
Division format rules:
One cannot have numbered paragraphs in a
definition;
and, one cannot break a numbered
list
out in the
middle of a paragraph.
Retaining the list structure would
involve turning the definition inside out.
However, this appears
to be unnecessary, since the definition is understandable with
the numbers simply removed.
The
next
problem
is
the
“‘Replacement
unit’
does
not
apply
to...” language.
In a definition, this would be better stated as
“does not include”.
The final
problems
involve
the
exclusion
of
units which are
subsequently used solely for disposal of waste from that unit or
other closing units at the facility.
Such units would not be
“replacement units”, and hence would not be subject to the new
liner and leachate collection requirements.
For example, see
Section 724.351(c), below.
Non-replacement
units
are limited to those receiving waste
in accordance with “an approved closure plan or
ZPA or ltate
approved corrective action.”
For one thing,
it is not clear why
the corrective action must be approved specifically by USEPA or a
0138-0777
14
State, but not the closure plan.
The
Board suggests that this is
an editorial error, so that both must receive the same type of
approval.
The
main problem is whether the Illinois rule needs to
address the possibility of approval by other
states,
or by USEPA.
With respect to the approval by other states, the USEPA
definition appears to be limited to disposal of waste from units
at a single facility.
In other words, a unit receiving waste
from a f~ci1ityclosing in another state could not qualify as a
non-replacement unit.
The Board does not therefore have to allow
for approval by other states.
The next question is whether the Board should allow for
approval by USEPA.
Within Illinois, IISWA-driven USEPA amendments
become effective immediately upon federal adoption.
Sections 7
•
2
and 22.4(a) of
the
Act require the Board to adopt the federal
requirement, which then becomes a State requirement.
A dual
federal/State regulatory
scheme then exists
until USEPA
authorizes the Illinois rule, at which time the federal
requirement is no longer effective in Illinois.
(See 57 Fed.
Req.
3480, January 29,
1992)
There is therefore a possibility
that
a
portion of a closure or post—closure care plan would have
been primarily approved by USEPA.
It appears that the federal
intent of the limitation has been met so long as either USEPA or
the Agency has approved the closure or post—closure plan.
The
Board solicited comment as to whether approval by just the Agency
ought to control at the State level, but received no response.
The text of the definition is as follows:
“Replacement unit” means a landfill, surface
impoundment or waste pile unit from which all or
substantially all of the waste is removed, and which is
subsequently reused to treat, store or dispose of
hazardous waste.
“Replacement unit” does not include a
unit from which waste is removed during closure, if the
subsequent reuse solely involves the disposal of waste
from that unit and other closing units or corrective
action areas at the facility, in accordance with a
closure or corrective action plan approved by USEPA or
the
Agency.
USEPA has also amended the
definition
of
“sump”
..O
give it
~‘
special meaning in the context of the liner and leachate
collection rules.
The definition adopted by the Board is as
follows:
“Suap” means any pit or reservoir that meets the
definition of tank and those troughs or trenches
connected to
it that serve to
collect hazardous waste
for transport to hazardous waste storage, treatment or
0138-0779
15
disposal facilities: exceDt that. as used in the
landfill, surface imDoundment and waste ~i1e rules,
“sump” means any lined tit or reservoir
that
serves to
collect liquids drained from a leachate collection and
removal system or leak detection system for
subsequent
removal from the system.
PART
721:
DEFINITION OF
‘HAZARDOUS
WASTE’
This
part contains the definitions of “solid waste” and
hazardous waste”, together with the procedures for listing and
the listings themselves.
It is derived
from
40 CFR 261.
USEPA
has amended these rules in several isolated.ru.emakings,
which
will be identified with each Section.
Section 721.103
This Section is the definition of “hazardous waste”.
USEPA
amended it at 57 Fed. Reg. 7632, March 3,
1992, and corrected the
amendment at 57 Fed. Reg. 23063, June 1,
1992.
The amendments
concern the “mixture and derived-from”
rules.
Although USEPA has
reprinted the entire text of Section 261.3, the amendments appear
to be to only a small portion of the text.
In Section 721.103 (a) (2) (A), the
main
amendment
(in the
correction)
is that the reference to the EP toxicity test has
been changed to reference the toxicity characteristic, measured
by the TCLP test, which replaced the EP toxicity test for most
purposes.
The Board adopted the TCLP test in R90-1O.
Most of the language in Section 721.103(a)(2)(A) concerns
the “Bevill exclusion” for certain mining
wastes.
The
Board
adopted this language in R90-2.
The
Board noted and corrected
numerous minor editorial problems with the
USEPA rule.
These
have not been fixed, and account for most of the differences
between the Board and USEPA text.
The Board has not changed its
text.
USEPA has made several other minor changes in wording to
Section 721.103(a) (2) (B) et seq., which the
Board
has followed.
In section 261.3(a)(2)(jv)(E)
(721.103(a)(2)(D)(v)3 USEPA
has apparently added a comma to the second proviso, so it reads:
“provided the wastes, combined annualized average...”
This is
obviously wrong, and the Board has made no
change.4
40
CFR
261.3(c)(2)(ji)(C)
(721.103(c)(2)(B)(iii)
was added
in R91-13, based on the August 19, 1991 Federal Register.
The
addition was a correction concerning “high temperature metal
recovery wastes”, which the Board addressed with the underlying
41t is possible that USEPA intended this as a possessive:
“wastes”.
0138-0779
16
rule, sooner than in the normal batch
period.
Apparently the
subsection was inadvertently repealed with the March
3 Fed. Reg.,
and then restored with the June
1, 1992, correction.
This
USEPA
amendment has no effect on the
Board
rules.
When the Board adopted its version of 40 CPR
261.3(c)
(2) (ii)
(C)
(721.103(c)(2)(B)(iii),
it
noted
and
corrected
a
number
of
editorial
errors.
This
is
discussed
in
the
R91-13
Opinion,
at
p.
22
—
25.
USEPA has not corrected these
editorial errors in this correction.
The Board has
not been able
to
identify
any
substantive
changes in
the
USEPA correction with
respect to this subsection, and
has
made none.
The March 3,
1992, Fed. Req.
addressed
the “mixture and
derived-from” rules which are in 40 CPR 261
•
3(d).
One change
appears to have been the omission of the “however” clause from
section
261.3(d)
(1)
(721.103(d)
(1):
(However, wastes that exhibit a characteristic
at the
point of generation may
still
be subject to the
requirements of part 268,
even if they no longer
exhibit a characteristic at the point of land
disposal.)
However, this was added back in the
June
1 corrections.
The March 3 Fed. Reg. added
section 261.3(e)
(721.103(e):
(e)
Sunset provision.
Paragraphs
(a) (2) (iv) and
(C)
(2) (i) of this section shall remain
in effect only
until April 28,
1993.
40
CFR
261.3(a)(2)(iv)
(723..103(a)(2)(D)3 is a lengthy
elaboration on
the
mixture rule
with respect to various
types of
listed waste.
40
CFR
261.3(c)(2)(i)
(721.1O3(c)(2)(A).)
includes
solid wastes generated from the treatment of listed hazardous
waste.
As is discussed in the general
introduction to this
opinion, USEPA repealed the sunset provision at 57 Fed. Reg.
49278, October 30, 1992, which would normally be addressed in
R93-4.
However, based on this USEPA action, the Board will not
adopt the sunset provision in this Docket.
Section 721.104
This Section contains exclusions from the defi.~itionof
“hazardous waste”.
It was amended at 57 Fed. Reg. 21534, May 20,
1992 and at 57 Fed. Reg. 27888,
June
22, 1992 and at 57 Fed. Reg.
30658, July 10,
1992.
The last is a correction to the TCLP
rules, which the Board is addressing outside the normal batch
period.
Also,
the May 20 action was corrected at 57 Fed. Reg.
29220, July 1,
1992, which the Board is also addressing outside
the normal batch period.
0138-0780
17
40 CFR 261.4(a)
(721.104(a)
lists exclusions which are
neither hazardous waste nor “solid waste”.
USEPA amended 40 CTR
261.4(a) (10) at 57 Fed. Reg. 27888
June
22, 1992.
This modifies
the
exclusion
f
or
certain
recycled
coke/coal
tar
by—products.
The
amendment, as adopted by the Board, is as follows
(721.104 (a) (10)
)
When
used as a
fuel,
-eeke and seal tar
from
the
iron
and steel industry
that
eentain.
or
is
pr.dueed
from
deoanter tank tar sludge,
UEEFA
hamardeus
waste I~087.
The proeeaa —of
pzoduoinq
o.k.
end seal tar from
sush
deeanter
tank
tar sludge in a eske even
is
likeurise
and any wastes from the
coke
bv—mroducts
processes
which
are
hazardous
only
because
they
exhibit
the
toxicity characteristic specified in Section 721.124.
when. subsequent to generation.. these materials are
recycled to coke ovens. to the
tar
recovery process as
a feedstock to rroduce coal
tar
or are mixed with coal
tar prior to the tar’s sale or ref
inina.
This
exclusion is conditioned on there
being
no land
disDosal
of
the
wastes
from
the Doint they
are
generated to the point they are recycled to coke ovens
or
the
tar
refinina
Drocess.
40 CFR 261.4(b)
(721.104(b)
lists exclusions of “solid
wastes” which are hazardous wastes.
USEPA corrected 40 CFR
261.4(b)(6)(ii)
(721.104(b)(6)(B)
at
57
Fed.
Reg.
30658,
July
10,
1992,
to
replace
the
reference
to
the
EP
toxicity
characteristic with a reference to the toxicity characteristic
(measured by
TCLP).
The
Board
language
is as
follows
(721.104(b)
(6)
(B):
Specific wastes which meet the standard in subsections
(b)(6)(A)(i),
(ii).
and
(iii),
above,
(so
long
as
they
do not fail the test for the toxicity characteristic
for any other constituent of
EP
teuioity, and do not
4e44—4he—t.eet-4e~-~x~ijkjt,any
other characteristic)
are~
USEPA corrected 40
CFR
26l.4(b)(9)
(Section
721.104(b)
(9))
at 57 Fed. Reg. 30658, July 10,
1992, also in connection with the
TCLP corrections.
The Board language is:
Solid waste which consists of discarded arsenical-
treated
wood
or
wood
products
which
fails
the
test for
the toxicity characteristic solely for arGonie for
hazardous waste
codes
D004 throuah D017 and which is
not a hazardous waste for any other reason or roasona
if the waste is generated by persons who utilize the
arsenical-treated wood and wood products for these
materials’ intended end use.
0138-0781
18
USEPA added a new exclusion as
40
CFR 261.4(b) (15)
(721104(b) (15)
at 57 Fed. Reg. 21534,
Nay 20, 1992.
This was
corrected at
57 Fed. Req. 29220,
July 1, 1992.
This excludes
certain used oil filters which have been properly drained.
The
Board language is:
Non-terne plated used oil filters which are not mixed
with wastes listed in
Subøart
D. if these oil filters
have been aravitv
hot-drained
using
one of the
following
methods:
~j
p~’ncturina
the
filter anti-drain
back
valve
or
the
filter
dome
end and hot-draining
~
Hot-draining and crushina:
Dismantling
and
h~t—drainina; or.
~
Any
other eauivalent hot—draining
method
which
will remove used oil.
The
subsection
numbering
in
the
USEPA
and Board rule now
jumps from
(b)(3.2) to (15), with (13)
and
(14) missing.
The
Board
has
numbered
its
rule
in
parallel with
the
USEPA
numbering.
The
Board solicited comment as to whether something might be
missing, but received no response,
The
Code
Division noted the gap in
numbering.
(PC
2.)
The
Board cannot renumber
(b)
(15) to
(13), without reviewing the
enti~rerule set (Parts 702 through 728) for cross—references, and
setting
up a continuing program to keep track of
this anomaly in
perpetuity.
The Board has instead inserted “filler” sections
into
(b) (13)
and
(14).
Section 721.111
This Section is
drawn
from 40 CFR 261.11, which was amended
at 57 Fed. Req.
14, January 2,
1992.
These are the criteria used
by USEPA for listing hazardous waste.
Section 721.111 was
recently amended in R90—17, which revised the delisting rules to
better
accommodate
delegation
of
this
authority
by
USEPA.
The “bow to list a
waste”
rules
are different from most of
the rest of
the
USEPA
RCRA
ules
in
that,
rather
than
governing
hazardous
waste
operations,
they
gover
future
rulemaking
r’~t.~ns
to be taken by USEPA.
The Board did not initially adopt ~
equivalent rule, since a Board rule would seem to be a State rule
regulating USEPA, since USEPA was not going to delegate listing
authority, and since
the
Board would not be governed by the
regulatory language to
the
extent
it did exercise listing
authority.
The Board instead incorporated the USEPA rule by
reference.
Uowever, once- delisting authority .was delegated,
it
0138-0782
19
became apparent that the listing standards within 40
c~
261.11
were
critical
for
delisting.
In
R90-17,
the
Board
therefore
adopted most of the text of section 261.11,-but.worded it
as a
recitation of USEPA’s criteria for listing, rather than as a
rule
enforceable against USEPA.
There are, therefore, numerous
differences in wording between the Board
and
USEPA rules.
Apart
from
the
functional
differences
between
the
Board
and
USEPA
rules,
there
are
a
number
of editorial problems with the
USEPA rule,
which were discussed in
the
R90-17
Opinion.
In
particular, section 261.11(a) (3), the topic of the January
2,
1992,
amendment, includes a “hanging
paragraph”
in which the
text
returns to the original level of indentation after a list is
broken out.
The Code Division prohibits this format.
The
Board
therefore had to restructure this portion of the
rule
in R90-17.
The hanging paragraph became two Board
notes,
following
the
introduction to subsection
(a) (3)
and
subsection
(a) (3) (K).
USEPA made a minor, but important,
change
in wording to 40
CFR
261.11(a) (3) at 55 Fed. Reg. 18726, Kay
4,
1990.
The
Board
picked this up in R90-17. As discussed at 57 Fed. Reg.
13, USEPA
initially treated the change as a technical revision, which was
made without notice and opportunity for
comment.
However,
after
opposition arose, USEPA made a new proposal, which appeared at 55
Fed. Reg. 33238, July 19,
1991.
This resulted in the January 2,
1992, USEPA action, which is the subject of this Docket.
The
USEPA
amendment appears
to
require
only
a
minor
change
in wording to Section 72l.lll(a)(3)
(261.11(a)(3)):
Toxic waste.
It contains any of
the toxic constituents
listed in Appendix H and, after considering any of the
following factors, USEPA concludes that the waste is
capable of posing a substantial present or potential
hazard to human health or the environment when
improperly treated, stored, transported or disposed of,
or otherwise managed:...
Section 721.Appendix I, Table D (Not Amended)
This
Appendix is
a listing of delisting adjusted standards.
This currently lists only the Keystone delisting adopted in AS
91-1.
None have been adopted since.
-The Board has therefore
made no changes .to this Appendix, but will make changes at a
later date to list any additional adjusted standards.
PART
724:
STANDARDS FOR PERMI~DHWM FACILITIES
This
Part contains the standards for owners and operators of
hazardous waste management
(MW)!) facilities with
RCRA
permits.
Standards for interim status facilities are in Part 725,
below.
This Part is drawn from 40
CFR
264.
Most of the amendments come
-
0 138-0783
20
from the liner and leak detection system
(LDS) amendments at 57
Fed. Reg. 3486, January 29, 1992.
This includes the addition of
numerous Sections to this Part.
USEPA is reusing several section numbers which were used for
Sections which were repealed following the HSWA Act
(RB6-1 at the
State level).
Under the Administrative Code Division rules,
repealed Sections remain as a heading, with a “Repealed”
designation
(a “ghost”).
The
new Sections will therefore appear
at the State level as amendments replacing the “ghosts”.
Pursuant
to a request from the Administrative Code Division,
there are minor changes in the format for removing
the
“ghosts”
as between the proposed and final orders.
-
Section
724.113
General Waste Analysis
This Section is derived from 40 CFR 264.13, which was
amended at 57 Fed. Reg. 8088, March 6, 1992, in connection with
the “third third” corrections.
The “third third” land disposal
bans were the main topic of R90-11.
The last Board amendment to
this Section was in R90-11.
The
amendments are minor changes in
the
wording of 40
CFR
264.13(a)(1)
(724.113(a)(1)), which are
easier to set forth than describe.
The Board amendment is as
follows:
Before an owner or operator treats, stores
or
disposes
of any hazardous waste~.,or non-hazardous wastes if
applicable under Section 724.213(d), the owner or
operator shall obtain a detailed chemical and physical
analysis of a representative sample of the waste~. At
a minimum, this ~
analysis must contain all, the
information which must be
known
to treat, store or
dispose of the waste in accordance with 4~e
roquireaonts
of
this
Part
e*~
~
35 131. Adm. Code 728,-
or vith the senditiono
-f
-
mermit
ispued
under
3~Ill.
Adm.
Cede 703, 703 and 70g.
Section 724.115
General Inspection Requirements
This Section is derived from 40 CPR 264.15, which was
amended ~t 57 Fed. Reg.
3486, in connection with LDS rules.
This
Section deals with “inspections” which must be performed and
documented by the operator.
The amendments are mainly changes to
cross referenc.
•;
to reflect new rules discussed below.
The Board
amendment to Section 724
•
115(b) (4)
is:
The frequency of inspection may vary for the items on
the schedule.
However, it should be based on the rate
of poesible—deterjoratjon of the equipment and the
probability of an environmental or
human
health
incident if the deterioration, malfunction or any
operator error goes undetected between inspections.
0138-076k
21
Areas
subject to spills, such as loading and unloading
areas, must be inspected daily when in use.
At a
minimum, the inspection schedule must include the
terms
and frequencies called for in Sections 724.274,
324.394,
724.293
724.295.
724.326,
334.353,
724.354,
724.378. 724.403, 724.447,
724.702, 724.933, 724.952,
724.953 and 724.958, where applicable.
Section 724.119
Construction Quality Assurance
Program
This new Section is derived from 40 CFR 264.19, adopted at
57 Fed. Reg. 3486, in connection
with LDS rules.
This
requires
a
“Construction Quality Assurance Program”
.
(CQA
Program)
for
certain
surface
impoundments,
waste
piles
and
landfill
units.
Among
other
things,
the
CQA program has to
address
the
construction
of
soil liners, geomeabrane liners, leachate
collection and removal systems, and leak detection systems.
The
operator has to have a CQA plan and a
CQA
officer,
and has to
certify,
before
receiving
waste,
that
the CQA plan was
successfully carried out.
40
CFR
264.19(c) (2) requires
test
fills or other
measurements of hydraulic conductivity of recompacted liners.
The USEPA rule reads as follows:
The CQA program shall include test fills for compacted
soil liners, using the same compaction methods as in
the full scale unit, to ensure that the liners are
constructed to meet the hydraulic conductivity
requirements of S~264.221(c) (1) (i) (B),
264.251(c)
(1) (i) (B),
and
264
e301(c)
(1) (i)
(B)
in the
field. Compliance with the hydraulic conductivity
requirements must be verified by using in-situ testing
on the constructed test fill. The *.qional
Administrator
may
accept
an alternative demonstration,
in lieu of a test fill, where data are sufficient to
show that a constructed soil liner will meet the
hydraulic conductivity requirements of §~
264.221(c) (1) (i) (B), 264.251(c) (1) (i) (B), and-
264.301(c) (l)(i)
(B)
in
the field.
There
are
several
minor
problems
with
this
language.
The
first problem concerns the agency with authority to make this
decision at the State level.
A general discussion of how
the
Board decides this appears in the introduction to this Opinion.
The Board sees no indication that USEPA intends to retain this
authority.
The
choice
is
therefore
as
between
the
Board and
Agency.
This decision,
in Part 264 (724), concerns an operator
who either has a permit or is required to get one.
The general
rule requires a test fill, or an alternative demonstration “where
data are sufficient to show that a constructed soil liner will
meet the hydraulic conductivity requirements”.
Rather than a
0138-0785
22
“waiver” of
the
test fill requirement,
this is an alternative way
of showing the same thing.
This is a ~technicalshowing of a type
typically made by the Agency on a
permit
application.
The
tJSEPA rule provides that the Regional Administrator “may
accept” the alternative.
As
“may”
is defined in the general
introduction
above,
this
could
be construed
as
meaning
that
the
decision maker “may or
may
not”
accept the alternative,
regardless of whether
the
data was “sufficient” under the
standard.
The Board has therefore worded t.his as “the Agency
shall accept.
.
.where data are sufficient”.
The
Board solicited
comment as to whether there might be other
grounds
on which
the
-
Agency should be able to reject
the
alternative, but received no
response.
The ~SEPA rule also is
wQrded
so
as to require that the data
be
sufficient to show compliance with the impoundment, pile and
landfill rules.
The alternative data need to be sufficient only
to meet
the
requirements
for
the type of unit
in
question.
The text of Section 724.l19(c)(2)
264.19(c)(2),
as adopted
by the Board, is as follows:
The CQA program must include test fills for compacted
soil liners, using the same compaction methods as in
the full scale
unit,
to
ensure
that
the
liners
are
constructed to meet the hydraulic conductivity
requirements of Sections 724.321(c) (1) (A) (ii),
724.351(c) (1) (A) (ii)
or 724.401(c) (1) (A) (ii)
in the
field.
Compliance with the hydraulic conductivity
requirements must be verified by using in-situ testing
on the constructed test fill.
The
Agency
shall accept
an alternative demonstration, in lieu of a test fill,
where
data
are
sufficient
to
show
that
a
constructed
soil liner will meet the hydraulic conductivity
requirements of Sections 724.321(c) (1) (A) (ii),
724.351(c) (1) (A) (ii) or 724.401(c) (1) (A) (ii)
in
the
field.
40
CFR
264.19(d)
(724.119(d)) prohibits acceptance of waste
until
the
CQA
officer
certified
that
the CQA program has been
carried out and that the unit meets the requirements of this
Part,
and:
The pro -~durein ~ *70.30(1)’2)(ji) of this chapter has
been completec, ~
40
CFR
270.30(1)
(2) corresponds with Section 703.247;
270.30(1) (2) (ii)
is 703.247(b).
This prohibits receipt of waste
5The reference is to “1”, as in “eli”.
0138-0786
23
following notification to the State, until either the State
has
inspected the unit, or 15 days have lapsed without State action.
Section 724.173
Operating Record
This Section is drawn from 40
CFR
264.73,
which
was
also
amended in connection with LDS rules.
The amendments add cross
references to the new requirements.
40
CFR
264.73(b) (6) the operator to record the following:
Monitoring, testing or analytical
data,
and corrective
action where requ.ired by subpart F and SS 264.19,
264.191, 264.193,
264.195,
264.222, 264.223, 264.226,
264.252—264.254, 264.276, 264.278, 264.280, 264.302—
264.304,
264.309,
264.347,
264.602, 264.1034(c)—
264.1034(f),
264.1035,
264.1063(d)—264.1063(i),
and
264.1064.
As worded,
the
USEPA rule appears to require the .data to be
recorded only if required by all the listed Sections, some of
which are mutually exclusive.
The Board believes this is an
editorial error by USEPA, and has retained “or” in its equivalent
rule (724.173(b) (6)).
The Board also believes that the reference to “corrective
action” has an understood “data” after it.
The
Board has
inserted this word.
The text of Section 724.173(b) (6)
is as
follows:
Monitoring, testing or analytical data and corrective
action data where required by Subpart F or Sections
724.119.
724.291.
724.293
724.295k
724.322.
724.323.
724.326, 324.353, 724.353 throuah 724.354, 724.376,
724.378,
724.380,
724.403,
724.402
throuch
724.404.
724.409,
724.447, 724.702, 724.934(c) through (f),
724.935,
724.963(d) through
(i) or 724.964.
SUBPART
K:
SURFACE
IMPOUNDMENTS
This Subpart contains design and operating requirements for
surface impoundments.
The amendments specify the design and
°!38
0787
24
operating requirements for leak detection6 at new7 surface
impoundments.
Section 724.321
Design
and
operating requirements (surface
impoundments)
This Section is
drawn
from 40 CPR
264.221.
Section 724.321(b) allows for approval of alternate design
or operating practices.
As adopted by the
Bourd
(in R82-19),
this allowed alternative practices only pursuant to a variance or
site-specific rulemaking.
Since that time,
Section 28.1 has
been
added
to
the Act, authorizing
this
type
of decision by “adjusted
standard”.
The Board
has
modified
this
Section
to
allow
the
use
of adjusted standards for this approval.
Section 28.~b)allows the Board to specify the “level of
justification” at the time it adopts the rule authorizing an
adjusted standard procedure.
The USEPA
rule,
and
existing
Board
rule, contain language appropriate
as
the
level of justification.
The
language
appears below.
The Board has reworded the Section
to make it clear what
the
level of justification is.
At one time the Board adopted procedures which were specific
to
RCRA
adjusted
standards.
These
remain
in
the
rule
book
as
35
Ill.
Ada.
Code
106.Subpart
D,
for.use
with
the
rules
that
specifically
reference
them.:
The
Board
has since adopted general
adjusted standards
procedures
in 35 Ui.
Ada. Code
106.Subpart G.
The Board has referenced these, rather than the RCRA-specific
procedures.
These procedures are discussed in detail above,
in
connection with Section 703.203.
The USEPA rule includes at least six procedures involving
“alternative design (and)
(or
operating practices”.
While this
one uses “and”, USEPA has apparently changed subsection
(d) below
to read “or”.
Of
the
other four,
some say “and”, others “or” and
others both.
The
Board
suggests that “or” is more correct, and
has revised all these procedures to be consistent.
~The
USEPA rules affect liners, leachate collection and
removal systems and leak detection systems
(“LDSs”).
For the
sake of brevity, in the rest of
this
opinion, we will refer to
ther ~ as “leak detection” or
“ws”,
except where the discussion
focusses on differen es among these.
7me applicability of the requirements is stated in the
subsection quoted below in connection with Section 724.321(c),
which is repeated for each type of unit.
For
the
sake of
brevity,
in this opinion, we will refer to these as “new” units,
except where the discussion focusses on the different types.
0138-0788
25
The text of the Board’s rule
(724.321(b)) is as follows:
b)
The owner or operator will be exempted from the
requirements of subsection
(a) above if the Board
finds
based en a d.aen.tratien by
the
imer
Sr
epera~er,in a varianee aria/er
sits
spesu3.o
rulemaking, arants
an
adi
usted
standard
oursuant
to
35
Iii.
Ada.
Code
106.Subnart
G.
The
level
of
justification
is
a
demonstration
by
the
owner
or
gperator that alternate design eM ~
operating
practices, together with location characteristics,
will prevent the migration of any -hazardous
constituents
(see Section 724.193) into the
groundwater
or
surface
water
at
any
future
time.
In deciding whether to grant an ...eept4ee adiusted
standard, the Board will consider:
1)
The nature and quantity of the wastes;
2)
The proposed alternate design and operation;
3)
The hydrogeologic setting of the facility,
including the attenuative capacity and thickness
of the liners and soils present between the
impoundment and groundwater or surface water;
and
4)
All other factors which would influence the
quality
and
mobility
of
the
leachate
produced
and
the potential for it to migrate to groundwater or
surface
water.
The applicability of the new leak detection requirements is
governed by 40
CFR
264.221(c)
(724.321(c),
which reads as
follows:
The owner or operator of each new surface impoundment
unit on which construction commences after January
29,
1992, each lateral expansion of a surface impoundment
unit on which construction commences after July 29,
1992 and each replacement of an existing surface
impoundment
unit
that
is to commence reuse after July
29,
1992 must install two or more liners and a leachate
collection and removal system between such liners.
“Construction commences” is as defined in
S 260.10 of
this
chapter
under
“existing
facility”.
These dates have already passed.
This
raises a question as
to whether the Board ought to adopt the rule with a later State
effective date.
This depends in part on whether these are HSWA-
driven amendments, which are already effective as federal law in
Illinois.
The new leak detection (and other) requirements do
appear to be NSWA—driven rules
(57 Fed. Reg. 3462).
Since
0138-0789
26
Illinois facilities are already subject to these requirements,
there appears to be no problem with adopting the State rule with
a retroactive date.
40
CER
264.221(c) (l)(i)
(B) and (c)(2)(ii)
(724.321(c) (1) (A) (ii) and (c)(2)(B)) include three numerical
standards,
as
follows:
(A composite bottom liner ...)
The lower component
must be constructed of at
least
3 feet
(91 cm) of
compacted soil material with a hydraulic conductivity
of no
more
than 1X1O/7/c*/sec.
(LDS
.
.
.3
Constructed of granular drainage materials
with a hydraulic conductivity of 1X10/1/aa/sec or more
and a thickness of 12 inches (30.5 cm) or more; or
constructed of synthetic or geonet drainage materials
with a transaissivity of 3X10/’/m2sec or more;
There
are
several
editorial
problems
with
the
numerical
standards.
First, each exponent is surrounded by a “I
/“,
both
in the Fed. Reg. and in the USEPA electronic version.
The Board
assumes this is an artifacte of a change in word processing
systems at some point in the development of the rule,
and has
removed the characters.
The first two standards: are for hydraulic conductivity,
which is normally measured in units of cm/sec.
The third
standard, however, is for synthetic or geonet draina~ematerials
with a .transmissivity apparently expressed
as
“m2sec”~’.
Appropriate units for transmissivity would be “m2/sec”.
USEPPI has also amended 40 CFR 264.221(d)
(724.321(d)), which
allows for an alternative liner demonstration.
When the
Board
originally adopted this provision, it determined that this was an
appropriate decision for the Agency to make in the context of
RCRA permit
issuance.
The Board revised the wording of the USEPA
rule to make it clear that this was to be an Agency action
An alternative possibility is that, while
the
“,/“
in
advance of
the
exponent is an artifact, the
“/“
following the
exponent is a part of the
units,
i.e.
“1
x
iO~~
/cm/eec”.
This
would be equivalent to “1 x l0~sec/cm”, which would be the
reciprocal of the hydraulic conductivity units indicated in the
first tw~standards.
This would clearly be wrong for the first
two standards.
9The USEPA rule could be read as
“/in2sec”.
This would,
however, be inconsistent with the reading of the “I
I”
typographical error above, and would be incorrect units for
transmissivity.
0138-0790
27
pursuant to a permit application.
Iost of the differences
between the USEPA and Board rule result from this.
The current
USEPA amendments modify the standard to allow an alternative
demonstration with respect to leak detection.
As discussed above in connection with Section 724.321(b),
there is a question as to whether this subsection ought to read
“alternative design and” or “alternative design or operating
practices”.
The Board has followed the USEPA amendment and used
“or”.
The amendment to Section 724.321(d)
is as follows:
Subsection
(c) will not apply if the owner or operator
demonstrates to the Agency and the Agency finds
f
or
such surface impoundment, that alternative design end
~_operating practices, together with location
characteristics,
ijill
j..
jJ
Will prevent
the
migration
of
any
hazardous
constituent into the groundwater or surface
water at least as effectively
as
•uoh ~
liners and leachate collection and removal
systeae~-s~ecifiedin subsection (c~above
Afl~
~
Will allow detection of leaks of hazardous
constituents through the
toD
liner
at
least
as effectively.
USEPA
has
also
added
40
CTh
264.221(f)
(724.321(f)),
pushing
the existing subsection
(f),
et
seq.,
down
one
•
The new language
is as follows:
(f) The owner or operator of any replacement surface
impoundment unit is exempt from paragraph
(C)
of this
section
if:
(1) The existing unit was constructed in compliance
with the design standards of sections 3004
(0)
(1)
(A) (i)
and
(o)
(5)
of
the
Resource
Conservation
and
Recovery
Act; and
(2) There is no reason to believe that the liner is not
functioning as designed.
The direct reference to the
RCRA
Act poses an editorial
problem in that it might be necessary to handle this as an
incorporation by reference at the State level.
As was discussed
in R90-2, at p.
17 and 27, the APA is unclear as to whether this
type of reference is an incorporation by reference,
and as to
whether it is allowable.
Regardless, this type of reference is
OJ38~o791
28
functioning
as
an
incorporation
by
reference
of
design
standards
in the federal law, and should be avoided, to maintain clarity.
The
cited provisions are
HSWA
Act provisions which set
design standards for surface impoundments
that
were
effective
until USEPA promulgated new design requirements.
They read as
follows:
• .
At a minimum, such regulations shall require
(1)
(A)
For each new landfill or surface
impoundment,
for which an application for a final
determination regarding issuance of a
permit
under section 3005(c) is received after the
date of enactment of (HSWA3
(i)
the installation of two or more liners
and
a
leachate
collection
system
above
(in the case of a landfill) and between
such liners;
...
(3004
(0)
(1)
(A) (1).)
(5)
(A)
The Administrator shall promulgate
regulations or issue guidance,.documents
implementing
...
(1)
(A)
within
two
years
after (HSWA).
(B)
Until the effective date of such regulations
or
guidance
documents,
the
requirement
for
the installation of two or
more
liners
may
be
satisfied by
the
installation
of
a top liner
designed, operated, and constructed of
materials to prevent the migration of any
constituent into such liner during the
period
such facility remains in operation (including
any
post—closure
monitoring
period),
and
a
lower liner designed, operated, and
constructed to prevent the migration of any
constituent through such liner during such
period.
For
the
purpose of the preceding
sentence,
a
lower
liner
shall be deemed to
satisfy such requirement if it is constructed
of at least a
3-foot
thick
layer of
recompacted clay or other natural material
with a permeability of no more than
3. x 10~
(cm/eec).
(3004(0) (5)
.3
These requirements appear to represent Section 724.321(c)
through
(e), as they existed prior to the amendments in this
Docket.
That
Section
assumed its post-HSWA form in R861,
at 10
Ill. Reg.
14119, effective August 12, 1986.
The Board has
referenced that version of its rule, and added an explanatory
note.
The language is as follows (724.321(f)):
0138-0792
29
f)
The owner or operator of any replacement surface
impoundment unit is exempt from subsection
(C)
above
if:
1)
The existing unit was constructed in
compliance with the design standards of 35
Ill. Adm. Code 724.321(c),
Cd) and (e), as
amended in R86—1, at 10 Ill. Reg.
3.4119,
effective August 12,
3.986; and
BOARD
NOTE:
The cited subsections
implemented
the design standards of
sections 3004(o)(1)(A)(i) and (o)(5) of
the Resource Conservation and Recovery
Act
(42 U.S.C. 6901 et seq.).
2)
There is no reason to believe that the liner
is not functioning as designed.
Section 724.322
Action Leakage Rate
This Section is derived from 40 CFR 264.222, which USEPA
adopted with the new leak detection rules.
The
new USEPA section
replaces a “ghost” at the State level.
This Section governs the
“action leakage rate” for a “new”10 surface impoundment.
The
action leakage rate is the maximum design flow rate that the leak
detection system
(LDS) can remove without the fluid head on the
bottom liner exceeding 1 foot.
To determine if the action
leakage rate has been exceeded, the owner or operator
converts
the
weekly or monthly flow rate from the monitoring data to an
average daily
flow
rate
(gallons
per
acre
per
day)
for each sump.
Response action under the following Sections results if the
action leakage rate is exceeded.
The USEPA rule includes two decisions which are to be made
by
the
Regional Administrator.
A general discussion appears
above as to how the Board determines who will
make
these
decisions in the State program.
The Board believes that both
decisions are to be delegated.
The first decision (in 724.322(a)
is the approval of the
action leakage rate.
40
CFR
270.17(b)(5)
(703.203(b)(5))
requires the operator to file a proposed action leakage rate,
with rationale, with the
permit
application.
The approval of the
action leakage rate would thus come in the context of a permit
application.
This would be an engineering-type demonstration of
a type typically made by the Agency pursuant to a
permit
application, the question being whether the leakage rate would
10As noted above, the Board is using “new” as a shorthand
for the types of units subject to these requirements.
0138-0793
30
cause more than a one foot head on the liner, considering slope,
permeabilities, etc.
The second decision is in 40
CFR
264.222(b), which reads as
follows:
Unless the negional Administrator approves a
different
calculation,
the average daily flow rate for
each
sump
must be calculated weekly during the active life and
clo;ure period, and if the unit is closed in accordance
with ~ 264.228 (b), monthly during the post—closure care
period when monthly monitoring is
required
under ~
264.226(d).
Although this is worded in terms of a “different
calculation”, it does not appear to allow
a
different
formula
to
be used.
Rather, the rule is referring to the frequency with
which
the
leakage
rate
must be recalculated and, by implication,
the period over which the daily leakage is averaged.
It is
closely linked with section 264.226(d)
(724.326(d)), which
specifies monitoring frequency.
This subsection authorizes an alternative frequency, but
specifies no criteria for decision.
However, the criteria appear
to
be
in
40
CFR
264.226(d)(2)
(724.326(d)(2fl:
After the final cover is installed, the amount of
liquids removed from each leak detection system sump
must be recorded at least monthly. If the liquid level
in the sump stays below the pump operating level for
two
consecutive
months,
the
amount
of
liquids
in
the
sumps
must
be
recorded
at
least
quarterly.
If
the
liquid
level
in
the
sump
stays
below
the
pump
operating
level for two consecutive quarters, the amount of
liquids in the sumps must be recorded at least semi-
annually
Although there is
a
specific
variable
frequency
rule
applicable following closure, section 264.226(d) (1)
(724.326(d) (1)) is quite specific that weekly monitoring is
required up to the point of closure.
It thus appears that the
alternative frequency decision applies only after closure.
The Board has adopted the following 1anguag~(7~ 322 (b):
To determine if the action leakage rate
~asbeen
exceeded,
the
owner
or
operator
shall
convert
the
weekly or monthly flow rate from the monitoring data
obtained under Section 724.326(d) to an average daily
flow rate
(gallons
per
acre per day)
for each sump.
The average daily flow rate for each sump must be
calculated weekly during the active life and closure
0138-079k
31
period and, if the unit
is
closed
in accordance with
Section 724.328(b), monthly during the post—closure
care period, unless the Agency approves a different
frequency
pursuant to Section 724
•
326(d).
Section 724.323
Response Actions
This new Section is derived from 40 CFR 264.223, which USEPA
adopted with the leak detection rules.
It requires the operator
of a “new” impoundment to have an approved “response action
plan”.
If the action leakage rate is
exceeded,
the
operator
must
implement the response action plan.
This entails notification,
an assessment of the leak, a response
and
monthly
reports.
The operator is required to file a “response action plan”
with the Part B permit application under 40
CFR
270.17(b) (5)
(703
•
203(b) (5).
The plan is reviewed and approved by
the
Agency
pursuant to normal permit review procedures.
This Section has some minor editorial problems.
40
CFR
264.223(b)(6)
(724.323(b)(6)
includes a reference to the
“analyses” in subsections
(b) (3),
‘(4)
and
(5).
Those rules
are
all worded as directives to the operator to “determine”, for
example, the location of a leak.
USEPA refers to these rules as
“determinations” at other points.
The Board ~as therefore
replaced “analyses” with “determinations”.
40
CFR
264.223(c)
(724.323(c)
has a subsection
(1) with no
text.
This is prohibited by
the
Code Division.
The
Board
has
inserted
the
word
“either”
at
this
level,
since
the
subsection
appears to have the form
((A, B and C) or D).
In addition, this
subsection has an “and/or”, an expression to which the Code
Division sometimes objects.
As used by the Code Division,
“A
or
B” means “A or B or both”,
the
same
thing as “and/or”.
The text of Section 724.323(c)
adopted by the Board is as
follows:
c)
To make the leak or remediation determinations in
subsections
(b) (3),
(4)
and
(5) above, the
owner
or operator shall:
1)
Either:
A)
Assess the source of liquids and amounts
of liquids by source;
B)
Conduct a fingerprint, hazardous
constituent or other analyses of the
liquids in the
LDS
to identify the
source of liquids and possible location
0138-0795
32
of any leaks, and the hazard and
mobility of the liquid; and
C)
Assess the seriousness of any leaks in
terms of potential for escaping into the
environment; or
2)
Document why such assessments are not needed.
Section 724.326
Monitoring and Inspection
This Section is derived from 40 CPR 264.226, which USEPA
amended with the leak detection rules.
The amendment adds a new
subsection
(d).
This governs monitoring and inspection of liquid
levels in Bumps.
This deals with “inspection” which must be
performed and documented by the operator.
It is closely related
to Section 724.322, discussed above.
Subsection
(d) also is an
empty level.
The Board has inserted “Monitoring of
LDS”
as a
grouping heading.
This rule depends in part on the “pump operating level”.
The monitoring frequency is reduced to less than monthly if
liquids remain below
the
pump operating level for long periods of
time.
40
CFR
264.226(d) (3) provides that:
“Pump operating, level” is a liquid level proposed by
the owner or operator and approved by the Regional
Administrator based on pump activation level, sump
dimensions, and level that avoids
backup
into the
drainage layer and minimizes head in the
Bump.
The pump operating level is
potentially
a
very
important
determination, since monitoring frequencies depend in part on how
often liquids reach the pump operating level.. A high pump
operating level could lead to very infrequent monitoring.
This is a technical decision which is closely related to the
action leakage rate and response plan.
As is discussed above, 40
CFR 270
•
17(b) (5) requires a proposed action leakage rate and
response plan in the permit application, but omits the pump
operating level.
The Board has above included it in Section
703
•
203 (b) (5).
With the decision placed into the normal context
of a
permit
application, there is no need to create a special
procedure.
The text of Section 74.4.326(d) adopted by the Board is as
follows:
d)
Monitoring of
LDS.
1)
An
owner
or operator required to have a
LDS
under Section 724.321(c)
or
(d)
shall record
0138-0796
33
the
amount
of
liquids
removed from each
LDS
sump at least once each week during the
active life and closure period.
2)
After the final cover is installed, the
amount
of liquids removed from each
LDS
sump
must be recorded at least monthly.
If the
liquid level in the sump stays below the pump
operating level for two consecutive months,
the
amount
of liquids in
the
sumps must be
recorded at least quarterly.
If the liquid
level in the sump stays below the pump
operating level for two consecutive quarters,
the amount of liquids in the sumps must be
recorded at least semi—annually.
If at any
time during the post—closure care
period
the
pump operating level is exceeded at units on
quarterly or semi-annual recording schedules,
the owner or operator shall return to monthly
recording of amounts of liquids removed from
each sump until the liquid level again stays
below the pump operating level for two
consecutive months.
3)
“Pump
operating level” is a liquid level
proposed by the owner or operator pursuant to
35 Ill. Adm. Code 703.203(b) (5,) and approved
by the Agency based on pump activation level,
swap dimensions and level that avoids backup
into the drainage layer and minimizes head in
the Bump.
Section 724.328
Closure and Post—closure Care
This Section is
drawn
from
40
CFR
264.228.
The amendment
adds
section
264.228(b)(2)
(724.328(b)(2)),
which
requires
the
operator
to
maintain
and
monitor
the
LDS
during and after
closure.
SUBPART
L:
WASTE PILES
This
Subpart specifies design and operating requirements for
waste piles.
A waste pile is a type of storage unit.
A pile in
which waste is permanently placed would be a type of landfill.
These provisions were also amended with the LDS rules, at 57 Fed.
Reg.
3486, January 29,
1992.
These amendments largely repeat the
amendments to the surface impoundment rules, discussed above.
However, piles differ from surface impoundments in one major
respect:
while liquid is expected to be present on top of the
first liner in an impoundment, such liquid must be removed from
the top liner under a pile.
Moreover, USEPA has never adopted
rules implementing HSWA requirements with respect to piles.
0138-0797
34
Section 724.351
Design
and Operating Requirements for Waste
‘Piles
This Section is drawn from 40 CFR 264.251.
Section 724.351(a) contains the general liner requirement
for a waste pile:
a single liner which will prevent migration
through the liner during the active life of the pile.
The pile
must also have leachate collection and removal above the
liner.
Section 724.351(b) allows for approval of alternate desigr~
or operating practices.
As adopted by the Board
(in R82—l9),
this allowed alternative practices only pursuant to a variance or
site—specific rulemaking.
For the reasons discussed above in
connection with Section 744.321(b), the Board is replacing these
determinations with an adjusted standards procedure.
The text of the Board rule (724.351(b))
is as follows:
b)
The owner or operator will be exempted from the
requirements
of pe~ep~
subsection
(a)
above
if
the
Board
finds,
biiood
an
a dnnan.tration
by
the
e~mer
er
eperater,
in
a
varianee
a$/er
o•i••ie~•..•u•l
.rl.•..•..,i•
ki.•.’~~•••~••~,
~
.~
r~
i~’~’-
standard pursuant to 35 Ill. Adm. Code
106.SubDart
G.
The level of justification is a demonstration
by
the
owner
or
operator
that
alternate
design
eed
~
operating practices, together with location
characteristics, will prevent
the
migration of any
hazardous
constituents
(see
Section
724.193)
into
the groundwater or surface water at any future
time. In deciding whether to grant an
*eapt4ee
adiusted standard,
the
Board will consider:
1)
The nature and quantity of the wastes;
2)
The proposed alternate design and operation;
3)
The hydrogeologic setting of the facility,
including attenuative capacity and thickness of
the
liners
and
soils
present
between the pile and
groundwater or surface water; and
4)
All other fa. :ors which would influence the
quality and mobility of die leachate produc ~ and
the potential for it to migrate to groundwater or
surface water.
The USEPA amendments consist of the addition of 40 CFR
264.251(c)
—
(f)
(724.351(c)
—
(f)), and renumbering of existing
subsections.
The amendments are very similar to Section
724.321(c) et seq., discussed above.
The leak detection
0138-0798
35
requirements apply to new piles.11
The requirements are keyed to
January 29 and July 29,
1992, dates, which have already passed.
However, there appears to be no retroactivity problem with the
Board keying the State rules to these same dates, since operators
are already subject to these HSWA—driven requirements as federal
law.
As was discussed
above,
there were a
number
of editorial
problems with the numerical standards
in
the
surface
impoundment
rule.
The
comparable provisions differ for waste piles, in part
because of the fundamental difference between a pile and surface
impoundment:
while liquid is expected to exist
above
the top
liner in the impoundment, liquid
must
be removed from
under
the
pile.
The numerical standards for pile liners in 40 CFR
264.251(c)
(724.351(c)
are as follow:
The lower (liner
component must be constructed of
at least 3 feet
(91 cm) of compacted soil material with
a hydraulic conductivity of no more than 1X1O7 cm/sec.
(264.251(c) (1) (B))
The leachate collection and removal system
immediately above the top liner must be designed,
constructed,
operated,
and maintained to collect and
remove leachate from the waste pile during the active
life and post—closure care period. The Regional
Administrator will specify design and operating
conditions in the permit to
ensure
that the leachate
depth over the liner does not exceed 30 cm (one foot).
(264.251(c) (2)
The leachate collection and removal system between the
liners, and immediately above the bottom composite
liner in the case of multiple leachate collection and
removal systems,
is also a leak detection system.
(264.251(c) (3)
(The lower
LDS
must be
Constructed of granular
drainage materials with a hydraulic conductivity of
1X102 cm/sec or more and a thickness of 12 inches
(30.5 cm) or more; or constructed of synthetic or
geonet drainage materials with a transmissivity of
3X10’5 m2/sec or more:
(264.251(c)(3)(ii)
There appear to be no errors in the numerical standards of
the type discussed above for surface impoundments.
The
3 X 10~
11The applicability statement is actually quite complex, and
appears to be identical to that for surface impoundments, above.
As noted above, the Board is using the term “new” as a shorthand
description of these units.
ni
36
a2/sec transmissivity standard for the synthetic drainage
materials is equal to 0.3 cm2/sec, corresponding with the
transmissivity of 30.5 cm gravel layer with a conductivity of 1 X
10.2 cm/sec.
40 CFR 264.251(d)
(724.351(d)) provides for alternative
design or operating practices:
(d) The Regional Administrator
may approve
alternative
design or operating practices to those specified in
paragraph
(c) of this section if the owner or operator
demonstrates to the Regional Administrator that such
design and operating practices, together with location
characteristics:
(1)
Will
prevent
the migration of any hazardous
constituent into the ground water or surface water at
least as effectively as
the
liners
and
leachate
collection and removal systems specified in paragraph
(c) of this section; and
(2)
Will allow detection of leaks of hazardous
constituents through the top liner at least as
effectively.
This is quite similar to Section
724.321(d),
discussed
above.12
This is a technical showing which, rather than
exempting the operator from requirements, allows alternative
methods of accomplishing the same thing.
The Agency can make
this type of determination pursuant to a permit application.
The
Board has worded the introductory paragraph
(724
.
351(d))
as
follows:
The Agency shall approve alternative design or
operating practices to those specified in subsection
(C)
above if
the
owner or operator demonstrates to the
Agency, by way of
permit
or permit modification
application,
‘that
such design and operating practices,
together with location characteristics:...
40
CPR
264.251(f)
includes an exemption based on design
standards in the R~RAAct:
(f) The o~4!eror oper-ttor of any replacement waste pile
unit
is
exempt
from
paragraph
(c) of thit section if:
120ne difference is that, while the alternative showing for
a surface
impoundment
already exists, the language for piles
is
completely
new.
0138-0800
37
(1) The existing unit was constructed in compliance
with
the
design
standards
of
section
3004(o)(1)(A)(i)
and
(0)
(5)
of the Resource Conservation and Recovery
Act; and
(2) There is no reason to believe that the liner
is
not
functioning
as
designed.
This is comparable to Section 724.321(f), discussed
above.
There the Board determined that
the
cited Sections of
RCRA
(as
amended by HSWA) had been implemented in the subsections of
the
regulations which were amended.
The
Board
cited to the Illinois
Register publication of the repealed rules,
and
added an
explanatory note.
Here, however, the HSWA language was never
added to the regulations,
since there has been no post—HSWA
amendment to this Section.13
14
The Board has therefore added a
paraphrase of the RCRA/HSWA provisions in a Board Note
(724.351(f)
(1)
The
existing
unit
was
constructed
in
compliance
with
the design standards of section 3004(o) (1) (A) (i) and
(0)
(5)
of the Resource Conservation and Recovery Act
(42 Usc 6901 et seq.); and
BOARD
NOTE:
The cited provisions required the
installation of two or more liners
and
a leachate
collection system above
(in the case of a
landfill) and between such liners, including a top
liner designed, operated and constructed of
materials to prevent the migration of any
constituent into such liner during the period the
facility remained in operation (including any
post-closure monitoring period),
and
a
lower liner
to prevent the migration of any constituent
through
the
liner
during
such period.
The lower
liner was deemed to satisfy the requirement if it
was constructed of at least a 3—foot thick layer
of
recompacted
clay
or
other
natural
material
with
a permeability of no more than 1 x 1O’~cm/sec.
~The
CFR
carries a source note referencing 50 Fed. Reg.
4514, January 31,
1985.
This
was addressed in R85—22.
The cited
Fed. Reg. merely announced
0MB
approval
of
the July 26,
1982,
USEPA
amendments
to
this
Section.
141n
view
of
the
absence
of any post—HSWA amendments, one
might
question
whether
the
amendments
to
the
pile rules are HSWA-
driven.
However,
USEPA
has
unambiguously
stated
that
it
regards
the
new
pile
rules
as
HSWA-driven.
(57 Fed. Reg. 3480,
column
3.)
0138-0801
38
Section 724.352
Action Leakage
Rate
This Section is drawn from 40 CFR 264.252, which was adopted
with the leak detection rules.
The new Board Section replaces a
“ghost” section.
This Section governs the action leakage rate.
It is
comparable to Section 724.322, above.
The operator has to
propose an action leakage rate in the
permit
application pursuant
to
40
CFR
270.18(c)(1)(v)
(703.204(c)(1)(Efl.
40 CFR
264.252(b)
(724.352(b))
reads
as follows:
To
determine
if
the
action
leakage
rate
has
been
exceeded,
the
‘owner
or
operator
must
convert
the
weekly
flow rate from
the
monitoring
data
obtained
under
§
264.254(c), to an average daily flow rate (gallons per
acre per day)
for each Bump.
Unless
the
Regional
Administrator approves a different calculation,
the
average daily flow rate for each swap must be
calculated weekly during the active life
and
closure
period.
As discussed above in connection with Section 724
•
322 (b),
the Board construes this as referring to a different frequency of
calculation, rather than method of calculation.
However, with
this understanding, there are differences between this and the
comparable Section applicable to surface impoundments.
Differences appear to stem from the absence of post—closure care
rules for waste piles.15
While the other Section includes cross
references to post-closure care rules and a monitoring rule with
criteria for when the calculation frequency is to be reduced, the
Section on piles includes no such cross references.
Indeed, no
criteria are present in the pile rules for reducing
the
frequency.’6
The Board therefore suggests that the “unless”
clause is an editorial error, and has to omitted it.
The
language adopted by the Board (724.352(b)
is as follows:
To determine if the action
leakage
rate has been
exceeded, the owner or operator shall convert the
weekly or monthly flow rate from the monitoring data
obtained under Section 724.354(c) to an average daily
flow rate (gallons per acre
per
day)
for each swap.
15A waste pile is a temporary repository for waste, which
will
be
removed upon closure of the pile.
A “pile” in which
waste
will
remain
permanently
is
a
type
of
landfill.
~The
reduced
calculation frequency provisions for
impoundments depend on the pump activation level, which
provisions
are
also
missing
from
the waste pile provisions.
0138-0802
39
The average daily flow rate for each swap must be
calculated weekly during the active life and closure
period
Section 724.353
Response Actions
This Section is derived from 40
CFR
264.253,
which
was
also
added with the leak detection rules.
The new Section replaces a
“ghost”
Section.
This Section governs the response actions which the operator
must take if the action leakage rate is exceeded.
The operator
proposes a response action plan in the permit application
pursuant to 40
CFR
270.18(c)(l)(v)
(703.204(c)(l)(E)).
This
Section
is
comparable
to
Section
724.323
(264.223
above.
There appear to be no major problems with the text.
Section
724.354
Monitoring
and
Inspection
This Section is drawn from 40
CFR
264.254,
which
was
also
amended with the leak detection rules.
This Section governs
“inspection” of the unit by the operator.
The amendment adds subsection
(c), requiring weekly
monitoring
of
swaps:
An owner or operator required to have a
LDS
under
Section 724.351(c)
shall record the amount of liquids
removed from each
LDS
sump at least once each week
during the active life and closure period.
There
is
no
provision
for
monitoring
following closure,
because all
wastes
and
residues
must be removed from a pile on
closure.
SUBPART N:
LANDFILLS
This Subpart specifies design and operating requirements for
landfill units at permitted facilities.
It is derived from 40
CFR
264, Subpart N,
which
was
amended
with
respect
to
the
leak
detection rules, at
57
Fed.
Reg.
3486,
January
29,
1992.
These
amendments are comparable to the amendments discussed above with
respect
to
surface
impoundment
and waste pile
units.
Section
724.401
Design
and
Operating Requirements
This
Section
is
drawn
from
40
CFR
264.301.
Subsections
(c)
and
(d)
are
largely
replaced,
a
new
(f)
is added, and everything
below
is
moved
down.
0138-0803
40
Section 724.401(b)
allows for approval of alternative
practices as approved by site—specific rulemaking or variance.
The Board has replaced site—specific rulemaking with a reference
to the adjusted standards procedures, for the reasons discussed
above in connection with Section 724.321(b).
40
CFR 264.301(c)
(724.401(c)) controls
the
applicability
of
the new leak detection requirements.
This appears to be
identical to 40 CFR 264.221(c)
(724.321(c)), which is
set
out
above.
As noted there, the
Board
is using the term Nnew~~
as a
shorthand
description
for
the units to which
the
new requirements
are applicable, and is using
Uleak detection” or “LDS” to
describe
the
requirements,
which
also
include
liner
and
leachate
collection and removal requirements.
40 CFR 264.301(c)(1)(i)(B)
and
(c)(2)
(724.401(c)(1)(A)(ii)
and
(C)
(2)
include numerical standards for liner and drainage
layer hydraulic conductivity, etc.:
A composite bottom liner, consisting of at least two
components... The lower component
must be
constructed
of at least
3 feet
(91 cm) of compacted soil material
with a hydraulic conductivity of no
more
than 1XlO7
cm/sec.
(264.301(c)
(1) (i)
(B)
The leachate collection
and
removal
system between the
liners, and immediately: above
the
bottom
composite
liner.
..
Constructed of granular drainage materials
with
a
hydraulic
conductivity
of
1XIO2
cm/sec
or
more
and
a thickness of 12 inches (30.5 cm) or
more;
or
constructed of synthetic or geonet drainage materials.
with a transaissivity of 3X105 a2/sec or more;
(264.301(c) (2))•
The standards for conductivity and tranamissivity in the
drainage layer are approximately equivalent.
These rules differ
from the surface impoundment rules in that the drainage layers
can be up to ten times less permeable, apparently reflecting the
smaller liquid volumes expected under a landfill.
Indeed, the
standards are equal to
the
standards for a waste pile.
40
CFR
264.301(c)
(2) includes the following cross—reference:
The leachati collection and removal system must c’mply
with paragraphs
(3) (c)
(iii).
and
(iv)
of this sect...on.
This
is
probably
a reference to “(c) (3) (iii) and (iv)”.
The
Board
has
cited to the equivalent “(c) (3) (C) and
(D)”.
40 CFR 264.301(d)
(724.401(d)) allows for alternative design
or
operating
practices.
This
is
similar
to
Section 724.321(d),
above.
When
the Board adopted this
provision,
it
modified
the
01 38-080k
41
USEPA
language
to
make
it clear that this technical decision is
to be made pursuant to a permit application.
The language now
adopted by the Board is as follows:
Subsection
(c) will not apply if
the
owner or operator
demonstrates to
the
Agency,
and
the
Agency
finds
for
such
landfill, that alternative design aed g~operating
practices, together with location characteristics, vill
3J.
Will
t~revent
the migration of any hazardous
constituent into the groundwater
or
surface water
at least as effectively as such liners
and
leachate collection and removal systems. sDecified
in
subsection
(c)
above:
and
~
Will allow detection of leaks of hazardous
constituents throuah the toD liner at least as
effectively.
USEPA has also added 40
CFR
264.301(f)
(724.401(f)), which
includes an exemption for replacement units constructed in
compliance with section 3004(0) (1) (A) (i) and (o)(5) of the
Resource Conservation and Recovery Act.
This poses problems
which are similar to those discussed above with respect to
Section
724.321(f).
The
Board
has
handled this as above, by
referencing the repealed pro~~isions
which implemented the cited
RCRA
Act provisions.
The language is as follows:
f)
The owner or operator of any replacement landfill
unit is exempt from subsection
(c)
above if:
1)
The existing unit was constructed in
compliance with the design standards of 35
Ill. Adm. Code 724.401(c),
(d) and
(e), as
amended in R86-1, at 10 Ill. Reg. 14119,
effective August 12, 1986; and
BOARD
NOTE:
The cited subsections
implemented the design standards of
sections 3004(o) (1) (A)
Ii)
and (o)(5) of
the Resource Conservation and Recovery
Act
(42 U.S.C. 6901 et seq.).
2)
There
is no reason to believe that the liner
is not functioning as designed.
Existing Sections 724.401(f)
—
(j)
are promoted to
(g)
—
(k).
40 CFR 264.301(1)
is a site—specific rule applicable only
in
Alabama,
and
does
not
appear
in
the
Illinois
rules.
0138-0805
42
Section 724.402
Action Leakage Rate
This Section is drawn from 40 CFR 264.302, which was adopted
with the leak detection rules.
At the State level, the new
language replaces a “ghost” Section.
It specifies the “action
leakage rate”, which triggers response actions under the ensuing
Sections.
It is similar to Section 724.322, above.
40
CFR
264.302(a)
(724.402(a)) has an apparent editorial
error, which the Board has corrected.
The USEPA Section should
apply to “landfill units”, rather than “surface impoundments”.
40
CFR
264.302 (724.402) includes two decisions, which are
similar to those discussed above (in Section 724.322).
The
Regional Administrator approves the action leakage rate, and may
approve an alternative “calculation” of the rate.
The former is
clearly a part of the permit application under 40
CFR
270.21(b)(1)(v)
(703.207(b)(l)(E)).
The latter is a subsidiary
demonstration which is really addressing the frequency of
calculation, rather than the formula for the calculation.
The
standard for the alternative frequency is in 40 CFR 264.303(c) (2)
(724.403(c) (2)), below.
As is the case with the surface
impoundment rule, the alternative frequency is available only
following closure.
The Board has adopted
the
following
(724.402(b)):
To
determine
if
the
action
leakage
rate has been
exceeded,
the
owner
or
operator
shall
convert
the
weekly or monthly flow rate from the monitoring data
obtained under Section 724.403(c) to an average daily
flow
rate
(gallons
per
acre
per
day)
for each swap.
The average daily flow rate for each swap must be
calculated
weekly
during
the active life and closure
period,
and
monthly
during
the post—closure care
period, unless
the
Agency
approves
a different
frequency pursuant to Section 724.403(c) (2).
Section 724.403
Monitoring
and
Inspection’7
This Section is
drawn
from 40 CFR 264.303.
USEPA has added
a subsection
(C)
with
the
leak detection rules.
This provision
is comparable to 40 CFR 264.226(d)
(724.326(d)),
discussed above
in connection with surface impoundments.’8
17This Section deals with “inspection” which is to be
performed by the operator.
18The
order of the rules is different as between the surface
impoundment and landfill rules.
0138-0806
43
As is discussed in connection with the surface impoundments,
this Section depends in part on
the
“pump operating level”, which
the Regional Administrator is to approve pursuant to 40 CFR
264.403(d)(3).
This determination is similar to the action
leakage rate and response plan determinations discussed above and
below.
In
Section 703.207(b) (1) (E),
above, the Board has added a
component to the Part B application addressing the
pump
operating
level, alongside
the
action leakage rate and response plan.
This
brings the determination clearly into the permit application
process, avoiding any need for specialized procedures.
The pump
operating level language is as follows (724.403(c) (3)):
“Pump
operating level” is a liquid level proposed by
the owner or operator pursuant to 35 Ill. Ads. Code
703.207(b) (1) (E) and approved by the Agency based on
pump activation level,
swap dimensions and level that
avoids backup into the drainage layer and minimizes
head in the swap.
Section 724.404
Response Actions
This new Section is drawn from 40 CFR 264.304, which was
added with the leak detection rules.
It governs the response
actions the operator must take if the action leakage rate is
exceeded.
This section is comparable to Section 724.323,
discussed
above
in
connection
with surface impoundments.
The operator is required to file a “response action plan”
with the permit application pursuant to Section 703
•
207(b) (1) (E).
The Agency approves the plan pursuant to normal permit approval
procedures.
This Section governs
the
contents of the plan.
40
CFR
264.304 has three minor editorial problems which are
identical to those discussed above in connection with Section
724.323
(“analyses”,
“and/or”
and
“either”).
Section
724.410
Closure and Post-closure Care
This Section is
drawn
from
40
CFR
264.310,
which
was
amended
with the leak detection rules.
The amendments add a new
subsection
(b) (3)
(724.410(b) (3)), which requires the operator to
maintain and monitor the
LDS
during the post—closure care
period;
Existing subsections
(b) (3)
-
(5) are then renumbered.
SUBPART W:
DRIP PADS
This
Subpart
governs
“drip
pads”, a type of hazardous waste
management unit on which wood products are stored following
0138-0807
44
application’9 of wood preservatives.
Drip pads were a major
topic
in
R91-1
and
R9l-26.
USEPA has amended the rules at 57
Fed. Reg.
5861,
February
18,
1992.
Section 724.673
Design
and
Operating Requirements
This Section was drawn from 40
CPR
264.573.
It governs
design
and
operating
requirements
for
drip
pads
at
permitted
facilities.
OSEPA has amended this Section “by revising
paragraph
(a) (4) to read as follows:”
(Drip pads must:...)
Be impermeable, e.g., concrete pads must be sealed,
coated, or covered with an impermeable material
such
that. the entire surface where drippage occurs or may
run across is capable of containing such drippage and
mixtures of drippage and precipitation, materials, or
other wastes while being routed to an associated
collection system.
Note:
The requirement that existing drip pads be
impermeable, e.g., that drip pads be
sealed,
coated, or
covered,
with
an
impermeable material is
administratively stayed.
The stay will remain in
effect until October 30,
1992.
The drip pad administrative stays have a complex history,
which may be relevant to the current stay.
USEPA adopted the
drip pad rules on December 6, 1990, and published a stay on June
13,
1991.
This was coupled with a stay of the related P034 and
P035 listings in 40
CFR
261.31.
USEPA
also corrected the rules
on July
1,
1991.
The
Board
addressed all
of
these
when
it
adopted Section 724.673 in R91—1.
The stay situation is complicated by the HSWA status of
different
provisions.
As discussed above, USEPA amendments which
are required by the HSWA amendments to
the
RCRA
Act
become
effective immediately in authorized states, including Illinois.
The P032 listing of chlorophenolic preservatives was HSWA-driven.
On the other hand, the P034 and P035 listings were not HSWA-
driven,
and
hence, from the USEPA perspective, would not become
effective in states until authorized.
However, Sections 7.2 and
22.4(a) of the A”t required Illinois to adopt these rules on a
“fast—track”, regardless of HSWA status and USEPA’s authorization
schedule.
Thus, USEPA had to
write
different
stays
for
the
HSWA
‘91n
other
words,
following
“treatment”
of wood to produce
“treated
wood”.
However,
“treatment” and “treated” are important
terms
within
the
hazardous
waste
rules and have a very different
meaning.
0
I 38-0808
45
and non—HSWA portions, and was operating with an incorrect
perspective as to the effect of its actions in Illinois.
(See
Opinions in R91-1 and R91-26.)
The Board adopted the USEPA stays of the P032,
P034 and P035
listings, and of the coating requirement of Section 724.673 in
R9l-l.
However, the Board extended
some
of the notification
dates for the non-HSWA portions of the rules, so as
to
give
persons in Illinois more time to take actions to qualify for the
stay.
Following the adoption of R91-1,
the Board received calls
from wood preservers
who
stated
that
they
were
unable
to
meet
the
specified dates for application of coatings because of the onset
of winter, and that they had been misled by statements at the
national level that they would not have to comply with the non—
HSWA portions of the rule in authorized states.
The Board opened
R91-26 to further extend the dates associated with the stays for
the non-HSWA listings P034 and P035.
R91—26 was adopted just
prior
to
the
February
18,
1992,
USEPA
stay.
The R9l-l stay of
the
impermeable
coating
requirement
of
Section 724.673
(264.573) was embodied in a note following
subsection
(a) (4).
As worded by USEPA, it
read:
Note:
The requirement that new drip pads be
impermeable, e.g., that new drip pads be sealed,
coated, or covered with an impermeable material,
is
administratively stayed.
The
stay
will remain in
effect until further administrative action is taken.
(40
CFR
264.573(a) (4),
56 Fed. Reg.
27336, June 13,
1991.)
As was discussed in R9l-1, at p.
14, USEPA omitted the note
from the corrections which appeared two weeks later
(56 Fed. Reg.
30192,
July
1,
1991).
The Board construed this as an error by
USEPA,
and
retained
the
note
in
the
rules as adopted.
The note
does
not
appear
in
the
1991 Edition of the
CFR
(which,
anachronistically,
included
the
July 1 corrections).
The February
18, 1992, USEPA stay
makes
no mention of the
June 13,
1991,
stay.
It differs in that it applies to
“existing”, rather than “new” pads, and it terminates on a date
certain (October 30,
1992).
In the proposal, the Board was
uncertain
as
to
whether
the
June
13 stay was still in
0138-0809
46
existence.2° The Board proposed to retain the stay, but
solicited comment.
BOARD NOTE:
The requirement that new drip pads be
impermeable,
e.g., that new drip pads be sealed, coated
or covered with an
impermeable
material, is
administratively stayed.
The stay will remain in
effect
until
further
administrative action is taken.
The
requirement that existing driD Dads be
impermeable.
~
that
driD
Dads be sealed, coated or coverect with
an impermeable material, is administratively stayed.
The stay will remain in effect until
October
30. 1992.
USEPA informally alerted the Board that USEPA had terminated
the stays, and revised the regulations, at 57 Fed. Reg. 61492
December 24, 1992.
The background discussion at 57 Fed. Reg.
61493 makes it fairly clear that USEPA
regarded
the
June
13.
1991, stay as still in existence.
However, the December 24,
1992, action raises other problems.
One problem is that part of the stay
expired
on October 30,
1992.
Adopting it at this point might force Illinois wood
preservers to comply with rules that have a~readybeen modified
at the USEPA level.
Although the Board coula avoid this problem
by terminating the stay and adopting the
December
24,
1992,
modifications, this would be taking action on a USEPA rulemaking
outside the batch period required by Section 7.2 of the Act.
The December 24 action could be construed
as
a correction to
a matter already before the Board, and taken with this Docket, as
has been done with respect to other similar corrections discussed
in the general introduction to this opinion.
The Board, however,
declines to take such action at this late date.
For one thing,
this would require the Board to act on Sections which were not
included in the original proposal, and to act without affording
notice and the opportunity to comment.
Moreover, it would entail
at least a two-week delay in this rulemaking,
which
is subject to
an extension of time order already.
The Board has therefore
extended the stay until the time the Board
takes
further
regulatory action implementing the December 24,
1992, USEPA
amendments.
Part of the
USEPA
stay
is
“until
further
administrative
action is taken”.
At the State level, this means ac. ~onby the
Board to remove the note:
i.e., a final order in R93—4.
We
expect such action by July 10,
1993.
20USEPA may have intended to repeal the June 13 stay with
the July 1 corrections.
Or, the Board may have missed an
intervening USEPA action removing the stay.
Or, the newest stay
may have replaced the prior stay.
0138-0810
47
Some drip pads may be subject to HSWA-driven requirements
which are already effective at the federal level.
The extended
State stay will not be construed as excusing owners or operators
from complying with federal requirements already in effect in
Illinois.
The language adopted by the Board is as follows:
BOARD
NOTE:
The ràquiraaent that new drip
pads
be
impermeable,
e.g., that new drip pads be sealed, coated
or covered with an impermeable material, is
administratively
stayed.
The
stay will
remain in
effeet
until
further
adainietrativo aptien is taken.
The
reauirement
that existing
drib
Dads
be
imtermeable.
e.g.. that drib Dads be sealed, coated or covered with
an impermeable material,
is administratively staved.
The
stave will remain in effect until the
Board
removes
this note by further regulatory action imDlementing
USEPA amendments at 57 Fed.
flea. 61492. December 24.
1992. exøected in Docket R93—4.
The extended State
stay will not be
construed
as
excusing
owners
or
oberators from comblying with any federal reauirements
already In effect in Illinois.
PART 725:
INTERIM STATUS STANDARDS
This Part is drawn from. 40
CFR
265, which was amended mainly
in connection with the leak detection rules for certain new
units.2’
This Part contains the design and operating
requirements for hazardous waste management facilities with
“interim status”,
i.e., those who have filed a Part A permit
application under 40
CFR
270 (7033, but who have not received a
permit.
The
Part
265
(725)
rules are nearly identical to the Part
264
(724) rules, above, which apply to permitted facilities.
One
difference is that the interim status rules often need special
decision-making procedures to be used in the absence of a permit
system.
The new leak detection rules apply to “new” units.
Interim
status facilities are generally prohibited from building new
units
under
35
Ill.
Ads.
Code 703.155.
There are, however,
numerous exceptions, including units added to comply with
21As noted above,
in this opinion, the Board is using
“leak
detection” or
“LDS”
as a shorthand for rules which also include
new liner and leachate collection requirements.
The Board is
also
using
“new”
to
describe
the
applicability
of
the
new
requirements, which
is actually
quite
complex.
See Section
724.321,
above,
for the applicability.
0138-0811
48
enforcement orders.
It is therefore possible that an interim
status facility could be required to build a new unit outside the
permit system.
SUBPART B:
GENERAL FACILITY STANDARDS
This Subpart contains general rules governing all types of
interim status hazardous waste facilities.
Section 725.113
General Waste Analysis
This Section is drawn from 40 CFR 265.13, which was amended
at 57 Fed. Reg. 8088,
March 6,
1992, in connection with
the
“third third” corrections.
This involves minor changes in
wording to Section 725.113(a) (1):
Before an owner or operator treats, stores or disposes
of any hazardous wastes, or non—hazardous waste~if
applicable under Section 725.213(d), the owner or
operator shall obtain
a
detailed
chemical
end
physical
analysis of a representative
sample
of
the
wastes.
At
a
minimum, this ~
analysis must contain all the
information which must be
known
to treat, store or
dispose of the waste in accordance with
4I~e
requiroaonts ef this Part and 35 Ill. Ads. Code 728.
Section 725.115
General inspection Requirements
This Section is
drawn
from 40 CPR 265.15, which was amended
at 57 Fed. Reg. 3486,
in connection with the leak detection
.requireaents.
The Section governs “inspection” of the facility
to be performed by the operator.
The amendments mainly add, to
subsection
(b) (4), cross—references to the new rules discussed
below:
The frequency of inspection may vary for the
items
on
the schedule.
However, it should be based on the rate
Of peee4~edeterioration of the equipment and the
probability of an environmental or human health
incident
if
the
deterioration or malfunction
or
any
operator
error
goes
undetected
between
inspections.
Areas
subject
to
spills, such
as
loading
and
unloading
areas, must be inspected daily when in use.
At a
minimum,
the
inspection schedule a ~t include
the
items
and frequencies called for in Sections 725.274,
725.293,
725.295,
725.326,
725.360.
725.378.
725.404,
725.447, 725.477,
725.503, 725.933,
725.952, 725.953
and 725.958. Where abolicable.
0138-0812
49
Section 725.119
Construction Quality Assurance
(CQA) Program
This
new
Section is derived from 40 CFR 265.19, which
was
adopted with the
LDS
rules.
It is similar to Section 724.119,
above, except for problems caused by the absence of a procedural
context for decisions.
40 CFR 265.19 includes several references to design and
operating rules contained in 40 CFR 264 (724).
The Board has
generally followed these citations, which appear to reference
provisions not repeated in the interim status rules.
40
CFR
265.19(a)
includes the following sentence:
The (CQA
3
program
must
ensure
that
the
constructed
unit
meets or exceeds all design criteria and specifications
in the
permit.
USEPA has informally advised the Board that this appears to
be an editorial error in that interim status units will not have
permits.
The Board has cited to the Part, with the understanding
that some of the criteria and specifications are actually
referenced in
from Part 724 (264.
The adopted language
(725.119(a)
is:
The
(CQA) program must ensure that the constructed unit
meets
or
exceeds
all
design
criteria
and
specifications
in this Part.
The introductory sentence to 40
CFR
265.19(b)
(725.119(b))
is quite a bit different from the comparable language in
264.19(b)
(724.119(b):
Before
construction begins on a unit subject to the CQA
program
under
paragraph
(a) of this section, the owner
or operator must
develop a written
CQA plan.
For a permitted facility, the operator is required to
“develop and implement” the plan, with an unstated understanding
that this is to be prior to construction.
The Board has followed
the USEPA language in this Section on this.
The new language may
be setting up
the
differences between the permit and interim
status rules, which become more pronounced below.
40
CFR
265.19(c)(2)
(725.119(c)(2)j
requires
test
fills
for
compacted soil liners to confirm conductivity predictions.
As
discussed above with respect to Section 724.119(c) (2), this
provision contains two “and’s” which ought to be “or’s”.
40 CFR 265.19(c)(2)
(725.1l9(c)(2)
also contains the first
decision point in the rule.
This is comparable to 40 CFR
264.l9(c)(2)
724.l19(c)(2))
discussed above.
However, while for
0138-0813
50
a permitted facility the Regional Administrator “may accept” an
alternative demonstration of conductivity, the interim status
provision is worded as a self—implementing waiver:
The test fill requirement
is
vaiv.d where data are
sufficient to show that a constructed soil liner meets
the hydraulic conductivity requirements of
(part
2643
in the field.
(40 CFR 265.19(c) (2).)
The Board has left this as
a
self—implementing
waiver.
In
other words, the operator alone decides
whether
data are
“sufficient’ to
dispense
with the
test fill.
However, he does
so
at the risk that the Agency might disagree arid initiate
enforcement at a later date.
The alternative, which the Board is
not following, would be to create a
~priorapproval mechaniEm.
The Board solicited comment on this, but received no response.
The major differences between the permit and interim status
rules
lie
in
40
CP’R
265.19(d)
725.119(d).
For the permitted
facility,
the
CQA
officer merely delivers a certification to the
Agency,
initiating
procedures
for
initial
inspection
of
new units
under
the permit program.
For the interim
status
unit, a similar
procedure
is
created
within
the
rule
(265.19(d)):
Certification. The
owner
or operator of units subject
to § 265.19 must submit to the Regional Administrator
by certified mail or hand delivery, at least 30 days
prior to receiving waste, a certification signed by the
CQA officer that the
CQA
plan has been successfully
carried out and that the unit meets the requirements of
§S 265.221(a), 265.254, or 265.301(a). The owner or
operator may receive waste in the unit after 30 days
from, the Regional Administrator’s receipt of the CQA
certification unless the Regional Administrator
determines in writing that the
construction
is
not
acceptable, or extends the
review
period
for a maximum
of 30 more days, or seeks additional information from
the owner or operator during this period.
Documentation
supporting the CQA officer’s certification must be
furnished to the Regional Administrator upon request.
This clearly sets up a
permit-type
action which needs to be
subject to an appeal to the Board.
The Board has adopted the
following (725.119(d) and
(~..l:
d)
Certification.
The owner or operator of units
subject to this Section must submit to the Agency
by certified mail or hand delivery, at least 30
days
prior
to
receiving
waste,
a
certification
signed
by the CQA officer that the
CQA
plan has
been successfully carried out and that the
unit
meets the requirements of Sections 725.321(a),
51
725.354 or 725.401(a).
The owner or operator may
receive waste in the unit after 30 days from the
Agency’s receipt of the CQA certification unless
the Agency determines in writing that the
construction is not acceptable, or extends the
review period for a maximum of 30
more
days, or
seeks additional information from the owner or
operator during this period.
Documentation
supporting the CQA officer’s certification
must
be
furnished to the Agency upon request.
e)
Final Agency determinations pursuant to this
Section are deemed to be permit denials for
purposes of appeal to the Board pursuant to
Section 40 of the Environmental Protection Act.
The above subsection includes a “may”, which the Board has
left alone.
If the Agency fails to respond, the operator has an
option
as
to
whether
to
receive
waste
or
not.
SUBPART
E:
MANIFEST
SYSTEM,
RECORDKEEPING
AND
REPORTING
Section
725.173
Operating
Record
This Section is
drawn
from
40
CFR
265.73, which was amended
with the
LDS
rules.
The
amendments
to
Section
725
•
173 (b) (6)
add
cross references to the new rules discussed below, requiring the
recording of data required there.
As
is
discussed
above
in
Section
724.173,
this
Section has two “and’s” which need to be
“or’s”, since some of the referenced Sections are mutually
exclusive.
The text of Section 725.173(b)(6)
is as follows:
Monitoring, testing or analytical data
and
corrective
action
data
where
required
by
Subnart
F
or
Sections
725.190,
725.194,
725.291,
725.293,
725.295,
725.322.
725.323.
725.326.
725.355.
725.359. 725.360. 725.376,
725.378,
725.380(d)
(1),
725.402 throuah 725.404.
725.447,
725.477,
725.934(c) through
(f),
725.935,
725.963(d)
through
(i)
e~d~
725.964;
SUBPART
K:
SURFACE
IMPOUNDMENTS
This
Subpart
sets
design
and
operating
requirements
for
interim
status
surface
impoundment
units.
It
has
been
modified
by
the LDS
rules
at 57 Fed.
Reg.
3486, January 29,
1992.
Section 725.321
Design and Operating Requirements
This Section is drawn from 40
CFR
265.221, which was amended
with
the
LDS
rules.
It
contains
design
requirements
for
surface
impoundments.
This Section is closely related to 40 CFR 264.221
724.321),
which indeed is referenced.
0138-0815
52
The amendments add a new subsection
(a), which serves as
the
basic statement of what types of units are subject to the
LDS
requirements, and as to what the requirements are.
As adopted by
the Board, Section 725.321(a) reads:
The
owner
or
operator
of
each
new
surface
impoundment
unit on which construction commences after
January
29,
1992, each lateral expansion of a surface
impoundment
unit
on
which
construction
commences
after
July
29,
1992,
and each replacement of an existing surface
impoundment
unit
that
is
to
commence
reuse
after
July
29,
1992, shall install two or
more
liners and a
leachate collection and removal system between such
liners, and operate
the
leachate collection and removal
system,
in
accordance
with
35
IlL
Ada.
Code
724.321(c), unless exempted under 35 Zll. Ada. Code
724.321(d),
(e) or
(f).
“Construction commences” is as
defined in 35 Ill. Ads.
Code 720.110 under “existing
facility.”
These dates have already passed.
As discussed above, there
appears to be no retroactivity problem with adopting these dates
for HSWA-driven requirements which are alreaçly applicable as
federal
law.
Existing 40
CFR
265.221(c)
contains
the alternative design
and
operating practices demonstration which is discussed above in
connection with Section 724 .321(d).
This has apparently been
repealed and replaced with new language which is unrelated to the
alternative demonstration.
The Board has followed USEPA and
repealed this language.
The Board solicited comment as to
whether this might be an editorial error by USEPA, but received
no response.
On the one hand,
it is possible that USEPA intended
to instead replace subsection (b)~,which contains a
notification requirement which may be in conflict with
the
new
language in 40
CFR
265.19(d)
(725.119(d)
above.
On the other
hand,
it is possible that USEPA has determined that the
alternative should be available for permitted units only.
If
USEPA intended to retain the
language,
it
has
failed
to
make
amendments
which
would
be
necessary
to
accommodate
the
LDS
rules.
The new language of 40 CFR 265.221(c)
(725.321(c)) concerns
the exemption for surface impoundments which were designed to
meet standards set out ir the R~RAAct, “ed which are not
leaking.
This was discusbed above in
con,1ec+~on
with Section
724.321(f), in which the Board refer~cedthe regulatory version
of the
RCRA
standards, rather than the statute itself.
The Board
has followed the same course here.
However, in that the interim
~This notice requirement is, however, back—referenced in 40
CFR
265.222(a).
0138-0816
53
status
rules were apparently never amended to reflect the
statutory
requirements,
the
Board
has to cited Part 724
(264)
version.
The text of Section 725.321(c)
is as follows:
The owner or operator of any replacement surface
impoundment unit is exempt from subsection
(a)
above
if:
1)
The existing unit was constructed in
compliance with the design standards of 35
Ill. Ada. Code 724.321(c),
(d) and
Ce),
as
amended in R86—1, at.10 Ill. Reg. 14119,
effective August 12,
1986; and
BOARD NOTE:
The cited subsections
implemented the design standards of
sections
3004(0)
(1)
(A)
(i) and
(o)(5) of
the Resource Conservation and Recovery
Act (42 U.S.C. 6901 et seq.).
2)
There
is
no reason to believe that the liner
is
not
functioning
as
designed.
The
Board
has made minor editorial revisions to existing
Section
725.321(d),
as
follows:
The
double
linor
requiromont
A~encvshall
not
reanire
a
double liner as set forth in subsection
(a) may—be
uaived
by
the
Agency
for
any
monofill,
if:...
Pursuant
to
bullet
6
in
the Fed. Reg., Sections 725.322(a)
and
(b)
have been moved to become Sections 725.321(f)
and
(g).
This has to be shown as a repeal and new adoption of the language
under the Administrative Code.
A cross reference in former
Section 725.322(a)
265.222(a)
has to be changed from
“subsection (b)” to “subsection
(g)” to correspond with the new
numbering.
The existing Board rule has a subsection which is not
present in the CFR.
Section 725.321(f) authorizes appeal of
the
Agency determinations under this Section.
It will be renumbered
to 725.321(h).
Although one Agency determination is repealed
above, others remain.
Section 725.322
Action Leakage Rate
This Section is drawn from 40
CFR
265.222.
As discussed
above, USEPA has moved the existing text to the preceding
Section, and adopted new language in connection with the
LDS
rules.
This Section now specifies the action leakage rate, the
amount of liquid in the
LDS
which triggers a response action.
It
0138-0517
54
is
similar
to
Section
724.322 above, except for the complexities
introduced by the absence of a
permit
system.
40 CFR 265.222(a)
725.322(a))
sets up an approval procedure
for interim status leakage rates:
The owner
ox
operator of surface impoundment units
subject to
§
265.221(a) must submit a proposed action
leakage rate to the Regional Administrator when
submitting the notice required under 4 265
•
221 (b).
Within 60 days of receipt of the notification, the
Regional Administrator will: Establish an action
leakage rate, either
as
proposed by the owner or
operator or modified using the criteria in this
section; or extend
the
review
period
for
up
to
30
days.
If
no
action
is
taken
by
the
Regional
Administrator
before the original 60 or extended 90 day review
periods, the action leakage rate will be approved as
proposed by the owner or operator.
Section
725.322(a)
follows
this
language
closely,
subject
to
the appeal language in Section 725.322(d).
40
CFR
265.222(b)
(725.322(b)) contains the standard for the
action leakage rate determination.
This is very similar to
Section 724.322(a)~above.
40 CFR 265.222(c)
725:322(c))
specifies the
method
by which
the leakage rate is calculated.
This includes an alternative
“calculation”, which suffers from the
same
problems as discussed
‘above in Section 724.322(b):
the alternative applies to the
frequency of calculation,
and
relates only to the post-closure
care period.
The language adopted by the Board is as follows
(725.322(c)):
To determine if
the
action leakage rate has been
exceeded,
the owner or operator shall convert the
weekly or monthly flow rate from the monitoring data
obtained under Section 725.326(b)
to an average daily
flow rate (gallons
per
acre per day) for each aump.
The average daily flow rate for each sump must be
calculated weekly during the active life and closure
period
and,
if
the unit is closed in accordance with
Sectior 725
•
328(a) (2), monthly during the post—closure
care pe~.iod,unless the
ag.cy approves a
different
frequency pu~uantto Sectio~725.326(b).
~The standard gets pushed down in the rule because of the
greater complexity of the procedures for the interim status unit,
even at the federal level.
0138-0618
55
The Board has added language allowing appeals of Agency
determinations under this Section (725.322(d)):
Final Agency determinations pursuant to this Section
are
deemed
to
be
permit
denials
for
purposes
of
appeal
to
the
Board
pursuant
to
Section
40
of
the
Environmental Protection Act.
Section 725.323
Response Actions
This Section is drawn from 40
CFR
265.223.
There is a
fundamental ambiguity in the USEPA action on this Section, at 57
Fed.
Reg.
3486, January 29,
1992, with the
LDS
rules.
Bullet 7
in the Fed. Reg. instructs that Section 265.223 “is added”.
However, there is an existing, unrelated 40 CFR 265.223.
The
Board
suggests
that
USEPA
intended
to
insert the new Section
into
the “reserved” Section 265.224,
and to retain the existing
Section
265.223.
USEPA has informally advised the Board that this was an
error, but that it has not decided on which way to correct it.
The Board could correct this apparent error in two ways:
the
Board could either use
the
reserved number for the new Section,
or move the existing Section over to the new number.
The Board
has followed the latter course.
The pre-existing text
(a three—
line Section) will appear below,
as
Section 725.324.
This
alternative avoids the necessity of correcting numerous cross—
references into this Section.
The new text deals with response actions which are required
if the action leakage rate is exceeded.
It is similar to Section
724.323, above, except for the complexities introduced in
the
absence of a permit system.
40 CFR 265.223 (a)
(725.323 (a)) requires that the operator
submit a response action plan with the proposed action leakage
rate under the preceding Section.
That portion of the procedure
thus appears to be subsumed within that Section.
However, this
Section also has decision points following notification of any
exceeclence.
These potentially could be the subject of an appeal
to the Board.
The Board has therefore added Section 725
•
223(d),
authorizing appeals.
40
CFR
265.223(c)
(725.323(c)) has three minor editorial
problems, which are the same as those discussed above for
264.223:
“analyses”, “and/or” and “either”.
The complete text of Section 725.323 as adopted by the
Board
is as follows:
a)
The owner or operator of surface impoundment units
subject to Section 725.321(a)
shall submit a
0138-0819
56
response action plan to the Agency when submitting
the proposed action leakage rate under Section
725.322.
The response action plan must set forth
the actions to be taken if the action leakage rate
has been exceeded.
At a minimum, the response
action plan must describe the actions specified in
subsection
(b) below.
b)
If the flow rate into the
LDS
exceeds the action
leakage rate for any sump, the owner or operator
shall:
1)
Notify the Agency in writing of the
exceedence within 7 days of the
determination;
2)
Submit a preliminary written assessment to
the Agency within 14 days of
the
determination, as to the amount of liquids,
likely sources of liquids, possible location,
size and cause of any leaks, and short—term
actions taken and planned;
3)
Determine
to the extent practicable
the
location, size and cause of any leak;
4)
Determine whether waste receipt should cease
or be curtailed, whether any waste should be
removed from
the
unit for inspection, repairs
or controls, and whether or not the unit
should be closed;
5)
Determine any other short-term and longer-
term actions to be taken to mitigate or stop
any leaks; and
6)
Within 30 days after the notification that
the action leakage rate has been exceeded,
submit to the Agency the results of the
determinations specified in subsections
(b)(3),
(4) and
(5)
above, the results of
actions taken, and actions planned.
Monthly
thereafter, as long as the flow rate in the
LDS
exceeds
the
action leakage rate,
the
owner
or operator shall submit to the Agency
a resort summarizing the results of any
remedial actions taken and actions planned.
C)
To make the leak or remediation determinations in
subsections
(b) (3),
(4) and
(5) above, the owner
or operator shall:
0138-0820
57
1)
Either:
A)
Assess
the
source
of
liquids
and
amounts
of liquids by source;
B)
Conduct a fingerprint, hazardous
constituent or other
analyses
of
the
liquids in the
LDS
to identify the
source of liquids and possible location
of any leaks, and the hazard and
mobility
of
the
liquid;
and
C)
Assess the seriousness of any leaks in
terms
of
potential
for
escaping
into the
environment; or
2)
Document
why
such assessments are not needed.
d)
Final Agency determinations pursuant to this
Section are deemed to be permit denials for
purposes
of
appeal
to
the Board pursuant to
Section 40 of the Environmental Protection Act.
Section
725.324
Containment
System
As
discussed
above,
USEPA appears to have inadvertently
repealed the text of 40
CFR
265.223.
The
Board
has retained
the
text under this new Section~number. This may require revision to
conform with USEPA’s forthcoming correction.
Section 725.326
Monitoring and Inspection
This Section is drawn from 40
CFR
265.226, which was amended
in connection with the LDS.
It deals with monitoring and
inspection to be performed by the operator.
This Section is
comparable to Section 724.326 above.
The prior federal Section violated Code Division subsection
lettering requirements, requiring rearrangement when this Section
was adopted in 1982.
The amendment accidently brings the USEPA
text into compliance, so that the Board can rearrange its Section
to conform with the USEPA language.
The USEPA amendments add subsections
(b) (1)
—
(3).
The
Board has added a grouping heading to comply with Code Division
requirements
This Section includes the pump operating level
determination, which winds up being a quasi—permit action in this
Part.
The operator is required to file a proposed pump operating
level with the proposed action leakage rate in Section 265.222 (a)
(725.322(a))
above.
Arguably the procedures specified above
0138-0821
58
would suffice.
However, the
Board
has added procedural language
here as Section 725.326(c).
Section
725.328
Closure
and
Post—closure
Care
This Section is drawn from 40
CFR
265.228.
Subsection
(b) (2) was added with the
LDS
rules, to require maintenance and
monitoring of the
LDS
after closure.
As adopted by the Board,
Section 725.328(b) (2)
reads:
Maintain and monitor the
LDS
in accordance with 35 Ill.
Adm. Code 724.321(c) (2) (D) and (c)(3) and 725.326(b)
and comply with all other applicable
LDS
requirements
of this Part;
The USEPA amendment includes a typographical error which
the
Board has fixed.
40 CFR 265.228(b)(2)
(725.328(b)(2)) references
Section “265.221(c) (2) (iv) and
(c) (3)”.
However, no such
Sections exist.
USEPA apparently intended to reference to the
design standards in Part 264
(724),
which
are referenced into
Part 265
(725).
The
comparable
USEPA landfill rule discussed
below as Section 725
•
410(b) (2) contains the correct citation,
which the Board is following.
SUBPART L:
WASTE
PILES
This Subpart governs design and operating requirements for
interim status waste piles.~USEPA amended these rules in
connection with the leak detection system
(LDS)
rules
at
57
Fed.
Reg.
3486, January 29, 1992.
These rules are comparable to the
rules for permitted waste piles in Section 724.352., et seq.,
above, and to the rules for interim status surface impoundments
immediately above.
The rules differ from the Part 724 rules in
that a procedural context for decisions generally needs to be
created in the absence of a formal permit system.
The rules
differ from the surface impoundment
(and landfill) rules in that
piles are storage units from which wastes will be removed on
closure.24
Section 725.354
Design
and Operating Requirements
This Section is drawn from 40 CFR 265.254, which was
completely revised with the
LDS
rules.
This contains the
statement of applicability to “new” piles,
and references the
desigr standards of Section 724.351, above.
The applicability is
identical to that stated above with respect to surface
impoundments.
24A “pile” in which waste is to remain after closure is a
type of landfill.
0138-0622
59
40
CFR
265.255 (725.355), discussed
below,
references “the
notice required under” this Section.
However, the notice
requirement appears to have been omitted from the Federal
Register (265.254).
The Board has adopted the following
language, which is drawn from 40
CFR
265.221(b)
(725.321(b),
the
comparable
language
for
interim
status
surface
impoundments
discussed
above:
The owner or operator of
each
unit referred to in this
Section shall notify the Agency at least sixty days
prior to receiving waste. The owner or operator of each
facility submitting notice shall file a Part B
application within six months of the receipt of such
notice.
This has been added as sentences to this Section, which
lacks a subsection structure.
When USEPA corrects this,
it will
probably make this into a subsection
(b).
The Board has not done
so at this time, to preserve correspondence with the current
USEPA subsection lettering.
Section 725.355
Action Leakage Rates
This Section is drawn from 40 CFR 265.255, which was added
with the
LDS
rules.
This Section governs the action leakage
rate, the amount of liquid in the
LDS
which triggers a response
below.
It
iB
comparable to Section 724.352 for permitted piles,
and to 725.322 for interim status surface impoundments,
above.
The operator proposes an action leakage rate, which is
subject to approval (or default approval)
as discussed above for
Section 725.322.
The Board has added Section 725.355(d) to
establish an appeal mechanism.
40 CFR 265.255(c)
(725.355(c))
includes a reference to
approval of a “different calculation” of the leakage rate.
This
raises issues similar to those discussed above with respect to
Section 724.352.
The rule is actually referring to the frequency,
rather than
the
method of calculation.
However, the standards
for the alternative frequency appear to be absent from the waste
pile rules, which lack post—closure care provisions.
For the
reasons discussed above, the Board suggests that the inclusion of
the “different calculation” language is an editorial error.
The
Board has omitted this clause.
Section 725.359
Response Actions
This new Section is drawn from 40
CFR
265.259, which was
added with the
LDS
rules.
This specifies the response actions
which must be taken if the action leakage rate is exceeded.
This
Section is comparable to Section 724.353 for permitted piles, and
to 725.323 for interim status surface impoundments.
The language
0138-0823
60
is very similar to Section 725.323.
There appear to be no major
problems with the text (other than the “analyses”, “either” and
“and/or” discussed above).
The
Board
has added a subsection
(d)
to authorize appeals of Agency determinations.
Section 725.360
Monitoring and Inspection
This new Section is drawn from 40 CFR 265.260, which was
added with the
LDS
rules.
It reads as follows:
An owner or operator required to have a
LDS
under
Section 725.354 shall record the amount of liquids
removed from each
LDS
aump at least once
each week
during the active life and closure period.
SUBPART N:
LANDFILLS
This Subpart governs interim status landfill units.
It was
also amended mainly with the LDS rules at 57 Fed. Reg.
3486,
January 29,
1992.
The amendments to this
Subpart
are similar to
the amendments for permitted landfills in Section 724.401 et
seq., above, and for interim status surface impoundments Section
725.321 et seq., above.
Section 725.401
Design
and Operating Requirements
This
Section
was
amended
both
with
the
LDS
rules,
and
with
the “third third” corrections.
This Section contains the design
and operating requirements for interim status landfills.
It is
comparable to Sections 724.401 and 725.321.
40
CFR
265.301(a)
contains the applicability statement for
“new”~landfill units which must install LDS.
The Section
references the design standards in Section 724.401, above.
The
retroactive dates should pose no problem for these HSWA
requirements.
USEPA has informally confirmed that there is a typographical
error in the applicability statement in 40 CFR 265.301(a)
(725.401(a)) as set forth in the Federal Register.
A
line has
been dropped from the language as let
forth
at five other places
in the Federal Register.
The Board has added the line, which is
indicated in bold below 725.401(a)):
O)perate
the leachate collection and removal systems,
in accordance with 35 Ill. Mm. Code 724.401(0),
Unless
sxempt.d by 35 111. Ads. Cod. 724.401(d),
(e) or
(f).
~The Board is using “new” to describe this complex
applicability statement, which is identical to that set forth
above for Section 725.321.
0 138-O82~
61
40 CFR 265.301(c) apparently replaces
the
“alternative
design and operating practices” determination.
As is discussed
in connection with Section 725.321(c),
the Board has followed
this repeal, which raised questions discussed above.
New Section 265.301(c)
(725.401(c)) contains new language
referencing design standards in the
RCRA
Act.
These standards
are apparently contained in Section 724.401, as it existed prior
to these amendments.
The Board has used the same language
discussed above in connection with that Section.
The language is
(725.401(c):
The owner or operator of any replacement landfill unit
is exempt from subsection
(a) above if:
1)
The existing unit was constructed in compliance
with the design standards of 35 Ill. Adm.
Code
724.401(c),
(d) and
(e), as amended in R86-l, at
10 Ill. Reg.
14119, effective August 12,
1986; and
BOARD NOTE:
The cited subsections
implemented the design standards of sections
3004(o)
(1)
(A) (i)
and
(o)(5)
of
the
Resource
Conservation
and
Recovery
Act
(42
U.S.C.
6901
et seq.).
2)
There is no reason. to believe that the liner is
not functioning as designed.
40
CFR
265.301(d)(1)
(725.401(d)(l)
was
amended
in
connection
with
the
“third
third” corrections.
The amendments
change a reference to the EP toxicity characteristic to toxicity
characteristic, limited to D004 through D017.
In addition, the
Board has modified language to eliminate the term “waived”
(725.401(d) (1):
The double liner requirement Aaencv shall not require a
double liner as set forth in subsection
(a) may bc
iaivcd by tho Agcnoy for any monofill,
if:
1)
The monofill contains only hazardous wastes from
foundry furnace emission controls or
metal
casting
molding sand, and such weetee-de
v~ste~
4Qe~
not
contain constituents which vou1~render the wastes
hazardous for reasons other the ~
toxicity
ehareeterieties in 38 Ill.
Ads.
Cede 7Z~1.1~4
toxicity characteristic in 35 Ill.
Adm. Code
721.124. with hazardous waste number D004 through
D017;
The text of 40 CFR 265.302 has been moved into this Section,
where it will now appear as Section 265.301(f)
—
(i)
(725.401(f)
0138-0825
62
—
(i)).
Existing Section 725.401(f), which deals with appeals
and has no federal counterpart, has been moved down to
(j).
Section 725.402
Action Leakage Rate
This Section was drawn from 40 CFR 265.302.
With the
LDS
rules, USEPA has moved
the
existing text to the
preceding
Section, and has adopted new text dealing with the action leakage
rate, the quantity of liquid in the
LDS
which triggers a
response.
This Section is
comparable
to Section 724.402, and to
Section
725.322,
above.
40 CFR 265.302(b)
(725.402(b)) contains the same
typographical error as 40 CFR 264.302(a)
(724.402(a)).
The
Section applies to “landfills” rather than “Eurface
impoundments”.
40
CFR
265.302(c)
contains
the
alternative
“calculation”
which is discussed above in connection with Section 724.402 and
725.322.
The Board has followed the language set out above.
The
text of Section 725.402(c)
is as follows:
To determine if
the
action leakage rate has been
exceeded, the owner or operator shall convert the
weekly or monthly flow rate from the monitoring data
obtained under Section 725.404 to an average daily flow
rate
(gallons per acre
per
day)
for each sump.
The
average daily flow rate for each sump
must
be
calculated weekly during the active life and closure
period, and monthly during the post—closure care period
unless the Agency approves a different period under
Section 725.404(b).
The Board has added Section 725.402(d), allowing appeals of
Agency determinations pursuant to the interim status rules:
Final Agency determinations pursuant to this Section
are deemed to be
permit
denials for purposes of appeal
to the Board pursuant to Section 40 of the
Environmental Protection Act.
Section 725.403
Response Actions
This new Section is drawn from 40 CFR 265 ~03,
hich was
added with the LDS rules.
It governs response actions which must
be taken if liquids enter the
LDS
in excess ~f the action leakage
rate.
It is similar to Section 724.404~and 725.323 above.
~The interim status landfill rules are in a different
order.
0J38-0826
63
This Section contains three minor editorial problems which
are the same as discussed above (“analyses”, “and/or” and
“either”).
The Board has added subsection
(d), authorizing
appeals of the interim status determinations.
Section 725.404
Monitoring and
Inspection
This new Section is drawn from 40
CFR
265.304, which was
added with the
LDS
rules.
It governs “monitoring and inspection”
which is to be performed by the operator of a landfill unit.
It
is similar to Section 724.403, for permitted landfills, and
725.326,
for interim status surface
impoundments.
This Section includes the standard for reduction in sump
monitoring frequency, and the standard for determination of
the
“pump operating level”.
The Board has added a subsection
(d),
authorizing appeals of these interim status determinations.
Section 725.410
Closure and Post—Closure Care
This Section is drawn from 40 CFR 265.310, which was amended
with the
LDS
rules.
A
new subsection
(b) (2) is added, requiring
the operator to maintain and monitor the
LDS
during the post—
closure care period.
This Section cites to requirements for
permitted landfills in Part 724 264.
SUBPART W:
DRIP PADS
This Subpart governs interim status “drip pads”, a type of
hazardous waste management unit on which wood products are stored
following application21 of wood preservatives.
Drip pads were a
major topic in R9l-1 and R91-26.
USEPA has amended the rules at
57 Fed. Reg. 5861, February 18, 1992.
The rules are quite
similar to the rules above for permitted facilities.
The interim
status rules may be of greater practical importance,
since there
are probably many new interim status facilities which were
recently brought into the program by the regulation of this new
type of hazardous waste management unit, and who are required to
undertake new construction to come into compliance~
Section 725.543
Design
and Operating Requirements
This Section is drawn from 40 CFR 265.443, which was amended
at 57 Fed. Reg.
5861.
The amendment adds to Section 725.543 a
stay
for
existing
drip
pads
at interim status facilities.
This
Section
is
similar
to
Section
724.673 above.
The extensive
2TIn other words, following “treatment” of wood to produce
“treated wood”.
However, “treatment” and “treated” are important
terms within the hazardous waste rules and have a very different
meaning.
0138-0827
64
discussion above as to whether the existing stay for new
facilities remains is inapplicable,
since
the
Fed. Reg.
is clear
that the existing stay continues for the interim status units.
As is also discussed above, USEPA terminated these stays,
and amended the drip pad rules, at 57 Fed. Reg. 61492, December
24, 1992.
For the reasons discussed above, the Board
cannot
act
on these amendments in this
Docket,
but will address them in R93-
4.
The Board has therefore added language extending the stay
until the completion of that Docket.
The adopted text of Section 725.543(a) (4)
is as follows:
Be impermeable,
e
•
g., concrete pads must be sealed,
coated or covered with an
impermeable
material such
that the entire surface where drippage occurs or may
run
across is capable of containing such drippage and
mixtures of drippage and precipitation, aaterials or
other wastes while being routed to an associated
collection system; and
BOARD
NOTE:
The reauirement that existina
driD
pads be
imoermeable. e.g.. that drio oads be sealed. coated
or
covered with an
imDermeable
material, is
administratively staved.
The requirement that new drip
pads be impermeable, e.g., that new
drip
pads be
sealed, coated or covered with an impermeable material,
is administratively stayed.
The
stays will remain in
effect until further administrative sotion io
taken_the
Board
removes
this note by further regulatory action
imolementinu USEPA amendments at 57 Fed. Rep. 61492
December 24. 1992, exoected in Docket R93—4.
The
extended State stay will not be construed as excusing
owners or ooerators from comolvii1a with any federal
requirements already in effect in Illinois..
PART
726:
STANDARDS
FOR THE
MANAGEMENT
OF SPECIFIC WASTE
AND
SPECIFIC
TYPES
OF FACILITIES
SUBPART H:
HAZARDOUS
WASTE
BURNED
IN
BOILERS
AND INDUSTRIAL FURNACES
This
Subpart
regulates boilers and industrial furnaces
(“BIPs”) which
burn
hazardous wastes
as
fuel.
The BIF rules were
adopted in R91-13.
Section
726.200
Ap~iicability
This Section is drawn from 40 CFR 266.100, which was amended
at 57 Fed. Reg. 27888, June 22,
1992,
in connection with the
exclusion of coke by—product residues.
The amendment removes
(from subsection
(a)) a stay of the BIF rules with respect to
coke residues.
0138-0828
65
The stay was added in the
September
5,
1991, Federal
Register.
The
Board
added the stay in R91—l3 when it adopted
the
BIF rules, even though it was outside the normal batch period.
The lifting of the stay is coupled with the revision of Section
721
•
104 (a) (10) above, which clarifies the exemption for this
type
of recycling.
PART 728:
LAND
DISPOSAL RESTRICTIONS
This Part is derived from 40
CFR
268, which contains
the
USEPA land disposal restrictions.
It was amended in several
USEPA actions, mainly the “third third” corrections at 57
Fed.
Reg. 8088, March 6,
1992, the latest correction of the third
third land disposal rules adopted by the Board in R90-11.
Section 728.103
Dilution Prohibited
This Section is derived from 40
CFR
268.3, which was
amended
at 57 Fed.
Reg. 8088, March 6,
1992, the third third corrections.
The amendment authorizes dilution as a treatment for a D003
reactive cyanide wastewater or nonwastewater.
The text of
Section 728.103(b)
is as follows:
Dilution of wastes that are hazardous only because they
exhibit a characteristic in a treatment system which
treats wastes subsequently discharged to a water of the
State pursuant to an
NPDES
permit
issued under 35 Ill.
Adm. Code 309 or which ‘treats wastes for purposes of
pretreatment requirements under 35 Ill. Adm.
Code 310
is not impermissible dilution for purposes of this
Section unless a method has been specified as the
treatment standard in Section 728.142. or unless the
waste is a D003 cyanide reactive wastewater or
nonwastewater.
40
CFR
268.3 was the subject of a recent federal court
decision in Chemical Waste Manaaement et al.
V.
TJSEPA.
976 Fed.
2d 2. decided September 25.
1992.
in the U.S. Court of Aopea.s
for the District of Columbia.
This case mainly concerns the
related dilution rule for the UIC program in 40
CFR
148.3.
In a
comment received in R92-l3, USEPA indicated
that,
although a
motion for reconsideration is pending,
it expects that the UIC
rule will have to be modified in response to the litigation.
Chemical
Waste Management appears to have limited,
if any, impact
on the
RCRA
rule.
(976 Fed. 2d 24.)
Section 728.135
Third Third Prohibitions
This Section is drawn from 40
CFR
268.35, which was amended
at 57 Fed. Reg.
20770, May 15,
1992 and 57 Fed.
Reg. 28632,
June
26,
1992.
0138-0529
66
It is difficult to compare the USEPA and Board texts of this
Section.
The USEPA Section has several sentences with multi—page
lists in the middle.
To meet Code Division requirements,
these
had to be rearranged to put
the
lists at the end.
The Board
therefore broke several portions of
the
rule into subsections
which, although much easier to read, don’t
look
much like the
USEPA rules.
The Board subsections referenced below are tiny
specks
in
the
midst
of
large
paragraphs
in the USEPA rule.
The text of Section 728.135(c) (6) has a minor typographical
error which apparently
occurred
during
Board
adoption.
The
specific citation to 40
CFR
268.2(g) in the USEPA rule is
equivalent to Section 728.102 at
the Board
level.
This is
referring to an alphabetical definition list which does not have
subsections at the State level,
in accordance with Code Division
requirements.
The text of Section 728.135(c) (6)
is:
Inorganic solids debris as defined in 35 Ill.
Adm. Code
728.102 (which also applies to chromium refractory
bricks carrying the EPA Hazardous Waste Numbers
KO48—KO52)~ and
The June 26, 1992, amendment adds a “national capacity
variance” for certain reclaimed lead storage batteries which are
hazardous by reason of
the
characteristic for lead (D008).
The
amendments involve Sections 728.135(c) (5) and
(k).
The amendment
removes the D008 lead battery prohibition from subsection
(c) (5),
and adds a detailed rule as’subsection
(kJ, with a delayed
effective date.
The text of Section 728.135(k)
is as follows:
Effective May 8,
1993, D008 lead materials stored
before secondary smelting are prohibited from land
disposal.
On or before March 1,
1993, the owner or
operator of each secondary lead smelting facility shall
submit
to the Agency the following:
A binding
contractual commitment to construct or otherwise
provide capacity for storing such D008 wastes prior to
smelting which complies with all applicable storage
standards;
documentation that the capacity to be
provided will be sufficient to manage the entire
quantity of such D008 wastes;
and, a detailed schedule
for providing such capacity.
Failure by a facility to
submit
such documentation will render such D008 managed
by that facility proh~itedtror land disposal
ef~ctiveMarch
1, 1993.
In addition, no later than
July 27, 1992,
the
owner or operator of each faciliL
shall place in the facility record documentation of the
manner and location in which such wastes will be
managed pending completion of such capacity,
demonstrating that such management capacity will be
adequate
and
complies
with all applicable requirements
of
35 ‘Ill.
Adm.
Code
720
through
728.
0138-0830
67
There are some minor problems with the USEPA language,
which
the
Board
has
addressed
in
its
rule.
First,
to
qualify
for
the
“variance”, the operator had to document the management methods
by July 27, 1992, a date which has already passed.
The
Board
has
retained this date in the State rule.
Operators
were
required to
meet this HSWA-driven date as a matter of federal law,
so
there
is no problem with adopting a retroactive State date.
Second, the USEPA rule contains a reference to “subtitle C
requirements” in the last line.
The Board takes this to mean
subtitle C of the
RCRA
Act, the statutory basis for
the
federal
hazardous waste program.
The
Board has referenced 35 Ill. Adm.
Code 720 through 728 as State equivalents.
The May 15,
1992, amendment adds a “general capacity
variance” until May 8, 1993, for debris which is contaminated
with certain hazardous waste.
The text of Section 728.135(e) is
as
follows:
~
-u,
~
..c
wastoa specified in
thi
£5Ot1~n
wJn~
~
treatment
.taneare
n
sithpart
en inoineratien, moreury retertin~,vitrifisatien, said
leaching fellousd ~y ehemisal precipitatien
er
thermal
ranovory of aetalø and vhioh pro gontaminntod
ee~rio,are proni.ui~uutrom
~anu
asposal.
~g~tj~
May 8
1993. debris that is contaminated with wastes
listed in Sections 728.110. 728.111 or 728.112.
and
debris that is contaminated with any characteristic
waste for which treatment standards are established in
SubDart D. are prohibited from land disDosal.
The new language apparently replaces an unrelated “capacity
variance” involving thermal recovery of metals.
That variance
expired on May 8,
1992.
The USEPA text makes reference to 40
CFR
268.10, 268.11
and
268.12.
At the USEPA level, these are HSWA-required rules which
set up the schedule by which USEPA adopted the land disposal
bans.
The Board originally avoided adopting these, since the
verbatim text would appear to be a State
rule
enforceable
against
USEPA.
However, in R9l-13, the Board noted that these rules also
define the first, second and third thirds, and are sometimes used
for this purpose in
the
rules.
Between them they include all
-
hazardous waste, except newly listed wastes.
The Board therefore
incorporated the rules by reference, setting up dummy Sections.
The Board has referenced the
dummy
Sections.
The USEPA rule grants a variance for debris contaminated
with wastes listed in all, three Sections.
Since the lists are
mutually exclusive, this would be the null set.
The Board has
changed the “and’ to an “or”.
0138-0831
68
Section 728.141
CCWE
Treatment Standards
This Section is drawn from 40 CFR 268.41, which was amended
at 57 Fed. Reg. 8088, March 6,
1992, the third third corrections.
The Section establishes treatment standards expressed as
constituent concentrations in the waste extract
(CCWE),
one of
the three types of treatment
standards
in
this
part.
The amendments contain a large number of
minor
changes ‘to
the text of Section 728.141(a).
The Board language is as
follows:
Table
A identifies the restricted wastes and the
concentrations of their associated heee*4et*e
constituents which
may
not be
exceeded by
the
extract
of a waste or waste treatment residunl developed using
the test method in Appendix A for
the
allowabl,
land
disposal of such wastes, with the exception of wastes
D004, DOOB, Z033, K084, R101, K102, P030,
P011, P012,
P036, r030 and U136.
Table A identifies
the
restricted
wastes D004,
DOOS,
K031,
1t084, ElOl, E303,
i’oio,
roll,
I’91~,F036, T~038and
0136
and the concentrations of
their associated constituents which shall not be
exceeded by the extract of a waste or waste treatment
residual developed using the test method in 35 Ill.
Adm. Code 72l.Appendix
A
or B for
the
allowable land
disposal of such wastes..
(Appendix B
9f,,tMi, ia~t
provides guidance on treatment methods that have been
shown
to achieve the Table
A
levels for the respective
wastes.
Appendix B of this Part is not a regulatory
requirement but is provided to assist generators and
owners or operators in their selection of appropriate
treatment methods.)
Compliance
with these
concentrations is required based upon grab samples.
unless
otherwise
noted
in
Table A.
There are several possible USEPA editorial errors, some of
which have been corrected in the above language.
The language in
question is shown in bold above.
First, the
Fed.
Req. has
changed
the
first sentence to read:
“...
of this
part
of the
allowable.
•.“
The
CFR
and Board
rule
both
read “for”, which
seems to make more sense.
This appears to be a typographical
error, which the Board has corrected.
Second, the USEPA
ruje
changes the
W1(011..”
entry
to
“D031”.
USEPA has informally confirmed that this was a typographical
error in the Federal Register.
The Board has left it ~S “K03l”.
The existing USEPA rule includes the
listing
of
waste
numbers two times.
In the amendment, the second list has
apparently
been
dropped.
This
may
be a deliberate editorial
change
to
the
Section,
or
it
may
be
a
typographical
error.
The
0138-0832
69
Board has followed the USEPA text and deleted the second
list,
since
the
meaning
seems
unchanged.
The main change to this Section, the one discussed in
the
preamble,
is the final “unless” clause, which allows sampling
other than by grab samples,
as specified in the Table.
However,
USEPA
has
cited
to
“Table
CCW”
(Table
B.
This Section
governs
Table
CCWE
(Table
A)~.
The
Board
has corrected this error.
USEPA has also changed the references to Appendices in thi~
Section.
The
Board noted in prior opinions that these appeared
to be wrong, but followed the USEPA language in the absence of
clear cut resolution.
The issue has been confused by the
references to Appendix II
(B) in two different Parts.
The Board
has
followed
the
USEPA
clarification.
Table
D
Technology-based
Standards
This
Table
is
drawn
from
40
CFR
268.42,
Table
2,
which
was
amended at 57 Fed. Reg. 8088, March 6,
1992, the third third
corrections.
The
amendment
correlates
with
the exclusion of
cyanide
characteristic
wastes
from
the
no
dilution
rule
above.
D003 Sulfide reactive wastes may not be diluted as a substitute
for
treatment.
HISTORY
OF
RCRA,
UST and UIC
ADOPTION
The Illinois
RCRA,
UST’ (Underground Storage Tanks) and
UIC
(Underground Injection Control) regulations, together with more
stringent
State regulations particularly applicable to
hazardous
waste,
include
the
following:
702
RCRA
and UIC Permit
Programs
703
RCRA
Permit
Program
704
UIC
Permit
Program
705
Procedures for Permit Issuance
709
Wastestream
Authorizations
720
General
721
Identification
and
Listing
722
Generator Standards
723
Transporter
Standards
724
Final
TSD
Standards
725
Interim Status TSD Standards
726
Specific
Wastes
and
Management
Facilities
728
USEPA Land Disposal Restrictions
729
Landfills:
Prohibited
Wastes
~The
Administrative
Code
format
requirements
forced
the
Board to separate the very large
CCWE
and
CCW
tables
into
“Tables”, which float at the end of the Part, like Appendices.
CCWE
corresponds with A, and
CCW
with Table
B.
0138-0833
70
730
UIC Operating Requirements
731
Underground Storage
Tanks
738
Injection Restrictions
Special procedures for
RCRA
cases
are included in Parts 102,
103, 104 and 106.
Adoption
of
these
regulations
has
proceeded
in
several
stages.
The Phase
I
RCRA
regulations were adopted
and
amended
as
follows:
R8l—22
45
PCB
317,
February
4,
1982,
6
Ill.
Reg.
4828,
April
23,
1982.
R82-18
51 PCB 31, January 13,
1983, 7 Ill. Reg. 2518,
March 4,
1983.
Illinois
received
Phase
I
interim
authorization
on
May
17,
1982
(47 Fed. Reg. 21043).
The UIC regulations were adopted as follows:
R81—32
47 PCB 93, May 13,
1982;
October 15,
1982,
6 Ill.
Reg.
12479.
The UIC regulations were amended in R82-18, which is
referenced above.
The UIC regulations were also amended in R83-
39:
R83—39
55 PCB 319,
December
15,
1983;
7 111. Reg.
17338,
December
20,
1983.
Illinois received UIC authorization
February
1,
1984.
The
Board has updated the UIC regulations:
R85—23
70
PCB
311, June 20,
1986; 10 Ill. Reg. 13274,
August
8,
1986.
R86-27
Dismissed at 77 PCB 234, April 16, 1987
(No USEPA
amendments through 12/31/86).
R87—29
January 21, 1988; 12 Ill. Reg.
6673, April
8,
1988;
(1/1/87 through 6/30/87).
R88—2
June
16,
1988;
1’
Ill.
Reg.
13700,
August
26,
198~.
(7/1/87
through
12/31/87).
R88—17
December 15,
1988;
13 Ill. Reg.
478,
effective
December
30,
1988.
(1/1/88
through
6/30/88).
R89-2
January25,
1990;
14 111. Reg.
3059, effective
February
20,
1990
(7/1/88
through
12/31/88).
0138-08314
71
R89-11
May
24,
1990;
14
Ill.
Req.
11948,
July
20,
1990,
effective July 9,
1990.
(1/1/89 through
11/30/89).
R90—5
Dismissed March 22,
1990 (12/1/89
through
12/31/89)
R90—14
Adopted May 23, 1991;
35
Ill. Reg. 13425,
effective July 24, 1991
(1/1/90
through
6/30/90)
R9l—4
Dismissed February 28,
1991
(7/1
through
12/31/90)
R91-16
Dismissed December 6,
1991
(1/1 through 6/30/91)
R92—4
Dismissed April
9,
1992 (7/1/91 through 12/31/91)
R92-13
Proposed 10/16/92
(1/1/92
through
6/30/92)
R93-6
Next
UIC
Docket
(7/1/92
through
12/31/92)
The Phase II
RCRA
regulations included adoption of Parts 703
and 724, which established the permit
program
and final TSD
standards.
The Phase II regulations were adopted and amended as
follows:
R82—19
53 PCB 131, July 26,
1983, 7 Ill. Req.
13999,
October 28,
1983.
R83—24
55 PCB 31,
December
15,
1983,
8 Ill. Reg.
200,
January
6,
1984.
On
September
6,
1984, the Third District Appellate Court
upheld
the
Board’s
actions
in
adopting
R82-19
and
R83—24.
(Commonwealth Edison et p1.
v. IPCB,
127 Ill. App. 3d 446;
468 WE
2d
1339
(Third
Dist.
1984).)
The Board updated the
RCRA
regulations to correspond with
USEPA
amendments
in
several
dockets.
The
period
of the USEPA
regulations
covered
by the update is indicated in parentheses:
R84—9
64 PCB 427,
June
13,
1985;
9 Ill. Req. 11964,
effective July 24,
1985.
(through
4/24/84)
R85—22
67
PCB
175,
479,
December
20,
1985 and January 9,
1986;
10 Ill.
Reg. 968, effective January 2,
1986.
(4/25/84
——
6/30/85)
R86—l
71 PCB 110, July 11,
1986;
10 Ill. Req. 13998,
August 22,
1986.
(7/1/85
——
1/31/86)
U
138-083.5
72
R86—19
73 PCB 467, October 23, 1986;
10 Ill. Req. 20630,
December
12,
1986.
(2/1/86
——
3/31/86)
R86—28
75
PCB
306,
February
5,
1987;
and 76 PCB 195,
March
5, 1987;
11 Ill. Reg. 6017, April 3,
1987.
Correction
at
77
PCB
235, April 16, 1987; 11 Ill.
Reg. 8684, May 1, 1987.
(4/1/86
——
6/30/86)
R86—46
July 16, 1987; August
14,
1987;
11 Ill. Reg.
13435.
(7/1/86 ——9/30/86)
R87—5
October 15,
1987;
11 Ill.
Reg.
19280, November
30,
1987.
(10/1/86
——
12/31/86)
R87—26
December 3,
1987;
12 Ill. Req. 2450, January 29,
1988.
(1/1/87
——
6/30/87)
R87-32
Correction
to
R86-1;
September
4,
1987;
11
Ill.
Reg.
16698,
October
16,
1987.
R87—39
Adopted
June
14,
1988;
12
Ill.
Reg.
12999,
August 12,
1988.
(7/1/87
——
12/31/87)
R88—16
November 17,
1988;
13 Ill. Reg.
447, effective
December 28,
1988
(1/1/88
——
7/31/88)
R89-1
September 13, October 18 and November 16,
1989;
13
Ill.
Reg.
•18278,
effective
November
13,
1989
(8/1/88
——
12/31/88)
R89—9
March
8,
1990;
14
Ill.
Reg.
6225,
effective
April
16,
1990
(1/1/89
through
6/30/89)
R90—2
July
3
and
August
9,
1990;
14
Ill. Req. 14401,
effective
August
22,
1990
(7/1/89
through
12/31/89)
R90-10
August
30
and
September
13,
1990;
14
Ill.
Reg.
16450, effective September 25, 1990
(TCLP
Test)
(1/1/90 through 3/31/90)
R90—11
April 11,
May
23, 1991;
15 Ill. Reg. 9323,
effective June 17, 1991
(Third Third)
(4/1/90
through 6/30/90);
Corrected August 8,
1991;
Uncorrected August 22, 1991.
R90-17
Delisting Procedures
(See below)
R91—1
August 8, 1991; 15 Ill. Reg. 14446, effective
September 30,
1991
(Wood Preserving)
(7/1/90
through 12/30/90)
0I38-0835
73
R91—13
April
9,
1992;
16
Ill.
Reg.
9489,
effective
June
9,
1992;
Boilers
and
Industrial
Furnaces
(BIPs):
(1/1/91 through 6/30/91)
R91-26
Wood
Preserving Compliance Dates; January 9, 1992;
16
Ill. Req. 2600, effective
February
3,
1992.
R92—1
September 17,
1992, 16 Ill. Rag.
17636, effective
November 6,
1992 (7/1/91 through 12/31/91)
R92-l0
This Docket (1/1/92 through 6/30/92)
R93-4
Next
RCRA
Docket (7/1/92
through
12/31/92)
Illinois
received
final
authorization
for
the
RCRA program
effective January 31,
1986.
The
Underground
Storage
Tank
rules were adopted in R86-1
and
R86-28, which were
RCRA
update Dockets discussed above.
They are
currently being handled in their
own
Dockets:
R88—27
April 27, 1989;
13
Ill. Rag. 9519, effective
June
12,
1989
(Technical
standards, September 23,
1989)
R89—4
July
27,
1989;
13
Ill.
Reg.
35010,
effective
September 12, 1989 (Financial assurance, October
26,
1989)
R89-l0
February
22,
1990;
14
Ill.
Reg.
5797,
effective
April 10,
1990 (Initial update, through 6/30/89)
R89—l9
April
26, 1990;
14 Ill. Reg. 9454,
effective June
4,
1990
(UST State
Fund)
R90—3
June
7,
1990;
(7/1/89
—
12/31/89)
R90—l2
February
28,
1991
(1/1/90
—
6/30/90)
R91-2
July 25,
1991
(7/1 through 12/31/90)
R91—l4
April
9,
1992
(1/1/91
through
6/30/91)
R92—2
Dismissed
June
4,
1992
(7/1/91
through
12/31/91)
R92-l2.
Dismissed
August
13,
1992
(1/1/92
through
6/30/92)
R93-5
Next
UST
Docket
(7/1/92
through
12/31/92)
The Board added to the federal listings of hazardous waste
by listing dioxins pursuant to Section 22.4(d)
of
the Act:
0138-0837
74
R84—34
61 PCB 247, November 21, 1984;
8 Ill.
Reg. 24562,
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 S.B.
1834.
The
Board has adopted
USEPA
delistings
at
the
request
of
Amoco, Envirite and USX:
R85—2
69
PCB
314,
April
24,
1986;
J.0
Ill.
Reg.
8112,
effective
May
2,
1986.
R87—30
June
30,
1988;
12
Ill.
Reg.
12070,
effective
July
12,
1988.
R91-12
December 19,
1991;
16 Ill. Reg. 2155, Effective
January
27,
1992
(USX)
The
Board
has
modified
the
delisting
procedures
to
allow
the
use of adjusted
standards
in
lieu
of
site-specific
rulemakings:
R90—17
February
28,
1991;
15
Ill.
Reg. 7934, effective
May 9,
1991
The Board has granted a delisting by way of adjusted
standard:
AS91-1
Keystone, February 6,
1992
The Board has procedures to be followed in cases before it
involving the
RCRA
regulations:
R84—10
62
PCB
87,
349,
December
20,
1984
and
January
10,
1985;
9
Ill.
Reg.
1383,
effective
January
16,
1985.
The Board also adopted in Part 106 øpecia.
procedures to be
followed in certain determinations.
Part 106 was adopted in R85-
22
and
amended
in
R86-46,
listed
above.
The Board has also adopted requirements limiting and
restricting the landfilling of liquid hazardous waste, hazardous
wastes containing halogenated compounds and hazardous wastes
generally:
R81—25
60 PCB 381, October 25, 1984;
8
Il..
Req. 24124,
December 4,
1984;
R83—28
February 26,
1986;
10 Ill. Reg.
4875, effective
March
7,
1986.
D
138-0838
75
R86—9
Emergency
regulations
adopted
at
73
PCB 427,
October
23,
1986;
10
Ill.
Reg.
19787,
effective
November
5,
1986.
The
Board’s
action
in
adopting
emergency
regulations
in
R86—
9
was
reversed
(CBE
and
IEPA
V.
IPCB
et
p1.,
First
District,
January
26,
1987).
CONCLUSION
This opinion supports the Board’s order of this
same
date.
The Board will not file the adopted rules until 30 days after
the
date of this order, to allow time for post—adoption comments,
particularly from the agencies involved in the authorization
process.
IT IS SO ORDERED.
I,
Dorothy
N.
Gunn,
Clerk
of
the
Illinois
Pollution
Control
Board, hereby ce
fy that the above opinion was adopted on
the
~‘/“-~
day of
_____________,
1993, by a vote of
~
7
I
0138~0839
I
Control
Board