ILLINOIS POLLUTION CONTROL BOARD
October 16,
1992
IN THE HATTER OF:
)
)
RCRA UPDATE, USEPA REGULATIONS
)
R92-l0
(1/1/92
—
6/30/92)
)
(Identical in Substance
Rules)
ProDosal for Public Comment.
PROPOSED
ORDER
OF THE BOARD
(by J. Anderson):
Pursuant to Section 7.2 and 22.4(a)
of the Environmental
Protection Act (Act), the Board is proposing to amend the RCRA
hazardous waste regulations.
The amendments involve 35
Ill.
Adin.
Code 702,
703,
720,
721,
724, 725,
726 and 728.
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.
This proposed order is supported by a proposed opinion of
this same date.
The complete text of the proposed rules is
attached to this order and will appear in the Illinois Register,
but will not appear in the Opinion volumes.
The Board will
receive written public comment for 45 days after the date of
publication of the proposed rules in the Illinois Register.
IT IS SO ORDERED.
I, Dorothy H. Gunn,
Clerk of the Illinois Pollution Control
Board, hereby certify tha
th
above proposed order was adopted
on the
/i~t1~
day of
_____________,
1992, by a vote of
/‘~
Dorothy N. ,4~inn, Clerk
Illinois P~1lutionControl Board
0136-0533
2
TITLE 35:
ENVIRONMENTAL
PROTECTION
SUBTITLE G:
WASTE DISPOSAL
CHAPTER
I:
POLLUTION
CONTROL
BOARD
SUBCHAPTER
b:
PERMITS
PART
702
RCRA
AND
UIC
PERMIT
PROGRAMS
SUBPART A:
GENERAL
PROVISIONS
Section
702.
101
Applicability
702.102
Purpose and Scope
702
.
103
Confidentiality
702
•
104
References
702.105
Rulemaking
702.106
Agency Criteria
702.107
Permit Appeals
702.108
Variances
702
.
109
Enforcement
702.110
Definitions
SUBPART B:
PERMIT APPLICATIONS
Section
702.120
Permit Application
702.121
Who
Applies
702.122
Completeness
702.123
Information Requirements
702.124
Recordlceeping
702.125
Continuation of Expiring Permits
702.126
signatories to Permit Applications and Reports
SUBPART
C:
PERMIT
CONDITIONS
Section
702.140
Conditions
Applicable
to all Permits
702.141
Duty
to
Comply
702.142
Duty
to
Reapply
702.143
Need
to
Halt
or
Reduce
Activity Not a Defense
702.144
Duty
to
Mitigate
702.145
Proper
Operation
and
Maintenance
702.146
Permit Actions
702.147
Property Rights
702.148
Duty to Provide Information
702.149
Inspection and Entry
702.150
Monitoring and Records
702.151
Signatory Requirements
702.152
Reporting Requirements
702.160
Establishing Permit Conditions
702.161
Duration of Permits
702.162
Schedules of Compliance
01 36-O53t~
3
702.163
Alternative Schedules of Compliance
702.164
Recording and Reporting
SUBPART D:
ISSUED PERMITS
Section
-
702 .181
Effect
of
a
Permit
702.182
Transfer
702.183
Modification
702.184
Causes for Modification
702.185
Facility Siting
702
.
186
Revocation
702.187
Minor Modifications
AUTHORITY:
Implementing Section 13 and 22.4 and authorized by
Section 27 of the Environmental Protection Act
(Ill.
Rev. Stat.
1991,
ch.
111 1/2, pars.
1013, 1022.4 and 1027).
SOURCE:
Adopted in R81-32, 47 PCB 93, at 6 Ill. Reg.
12479,
effective as noted in 35 Ill. Adm. Code 700.106; amended in
R82—19, at 53 PCB 131,
7
Ill. Reg.
14352, effective as noted in
35 Ill. Adm. Code 700.106; amended in R84—9 at
9 Ill.
Reg. 11926,
effective July 24,
1985; amended in R85—23 at 10 Ill. Reg.
13274,
effective July 29,
1986; amended in R86-1 at 10 Ill.
14083,
effective August 12,
1986; amended in R86—28 at 11 Ill.
Reg.
6131, effective March 24,
1987; amended in R87—5 at 11111.
Reg.
19376,
effective November 12,
1987; amended in R87—26 at 12
Ill.
Reg.
2579, effective January 15,
1988; amended in R87-29 at
12
Ill. Reg.
6673, effective March 28,
1988; amended in R87—39 at 12
13083, effective July 29,
1988; amended in R89—1 at 13 Ill.
Reg.
18452, effective November 13,
1989; amended in R89—2 at 14 Ill.
Reg.
3089, effective February 20,
1990; amended in R89-9 at 14
Ill. Reg. 6273,
effective April 16,
1990;
amended in R92-10 at
16 Ill. Reg.
effective
SUBPART D:
ISSUED PERMITS
Section 702.181
Effect of a Permit
a)
The existence of a
RCRA
or UIC permit ahall 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. Adm. Code 703.270 through 703.273
(RCRA)
and 35
Ill. Adm. Code 704.261 through 704.263
(UIC)
and
Section 702.186.
b)
The issuance of a permit does not convey any property
rights of any sort, or any exclusive privilege.
0 136-0535
4
c)
The issuance of a permit does not authorize any injury
to persons or property or invasion of other private
rights,
or any infringement of State or local law or
regulations, except as noted in subsection
(a).
BOARD NOTE:
Derived
from
40
CFR
144.35
.(1~C8)
(1991~ and 40
CFR
270.4
(1~OB),
no
amondcd
at
53
Fed.
flag.
37~)34,Ccptcaber 38,
1~J88 (1991).
as
amended at 57 Fed. Rep.
3486. January 29.
1992.
(Source:
Amended at 16 Ill. Reg.
,
effective
)
0136-0536
5
TITLE 35:
ENVIRONMENTAL
PROTECTION
SUBTITLE G:
WASTE DISPOSAL
CHAPTER
I:
POLLUTION CONTROL BOARD
SUBCHAPTER
b:
PERMITS
PABT~
703
RCRA
PERMIT
PROGRAM
SUBPART
A:
GENERAL
PROVISIONS
Scope
and
Relation
to
Other
Parts
Purpose
References
SUBPART
B:
PROHIBITIONS
Prohibitions in General
RCRA Permits
Specific Inclusions in Permit Program
Specific Exclusions from Permit Program
Discharges of Hazardous Waste
Reapplications
Initial Applications
Federal Permits
(Repealed)
SUBPART C:
AUTHORIZATION BY RULE
AND
INTERIM STATUS
Section
703.140
703.141
703
•
150
703
.
151
703
.
152
703. 153
703.154
703
.
155
703
.
156
703.157
703.158
703.159
703. 160
Section
703.180
703.181
703. 182
703. 183
703.184
703 .185
703. 186
703.187
Purpose and Scope
Permits
by
Rule
Application
by
Existing
HWM
Facilities
and
Interim
Status Qualifications
Application by New HWM Facilities
Amended Part A Application
Qualifying for Interim Status
Prohibitions During Interim Status
Changes During Interim Status
Interim Status Standards
Grounds for Termination of Interim Status
Permits for Less Than an Entire Facility
Closure by Removal
Procedures for Closure Determination
SUBPART D:
APPLICATIONS
Applications in General
Contents of Part A
Contents of Part B
General Information
Facility Location Information
Groundwater Protection Information
Exposure Information
Solid Waste Management Units
0t360537
Section
703.
100
703
•
101
703. 110
Section
703
•
120
703.121
703 .122
703
.
123
703
•
124
703.125
703.126
703.127
6
703
•
188
703.200
703.201
703.202
703.203
703.204
703.205
703.206
703. 207
703.208
703.209
703.210
703.211
703.212
Section
703.221
703.222
703.
223
703. 224
703 .225
703
•
230
703.231
703.232
Section
703
•
240
703.241
703. 242
703.243
703
.
244
703.245
703
•
246
703. 247
Section
703. 260
703. 270
703.271
703.272
703.273
703
•
280
703. 281
703.282
703.283
Appendix A
Other Information
Specific Information
Containers
Tank Systems
Surface Impoundments
Waste Piles
Incinerators
Land
Treatment
Landfills
Specific Part B Information Requirements for Boilers
and Industrial Furnaces
Miscellaneous Units
Process Vents
Equipment
Drip
Pads
SUBPART
E:
SHORT
TERM
AND
PHASED
PERMITS
Emergency
Permits
Incinerator
Conditions
Prior
to
Trial
Burn
Incinerator
Conditions
During
Trial
Burn
Incinerator Conditions After Trial Burn
Trial Burns for Existing Incinerators
Land Treatment Demonstration
Research, Development and Demonstration Permits
Permits for Boilers and Industrial Furnaces Burning
Hazardous Waste
SUBPART
F:
PERMIT
CONDITIONS
OR
DENIAL
Permit
Denial
Establishing Permit Conditions
Noncompliance Pursuant to Emergency Permit
Monitoring
Notice of Planned Changes
Twenty-four Hour Reporting
Reporting Requirements
Anticipated Noncompliance
SUBPART
G:
CHANGES
TO
PERMITS
Transfer
Modification
Causes for Modification
Causes for Modification or Reissuance
Facility Siting
Permit Modification at the Request of the Perinittee
Class
1 Modifications
Class
2 Modifications
Class
3 Modifications
Classification of Permit Modifications
0136-0538
7
AUTHORITY:
Implementing Section 22.4 and authorized by Section
27 of the Environmental Protection Act
(Ill. Rev.
Stat.
1991,
ch.
111½, pars. 1022.4 and 1027).
SOURCE:
Adopted in R82—19,
53 PCB 131,
at 7 Ill. Reg.
14289,
effective October 12
,~
1983; amended in~R83-24 at
B~X1L.Beg.
20k,
effective December 27,
1983; amended in R84-9 at
9 Ill. Reg.
11899, effective July 24, 1985;
amended in R85—22 at 10 Ill. Reg.
1110, effective January 2,
1987; amended in R85—23 at 10 Ill.
Reg.
13284, effective July 28,
1986; amended in R86—1 at 10 Ill.
Reg.
14093, effective August 12,
1986; amended in R86—19 at 10
Ill.
Reg. 20702, effective December 2,
1986; amended in R86—28 at
11 Ill.
Reg.
6121, effective March 24,
1987; amended in R86—46 at
11
Ii..
Reg.
13543, effective August 4,
1987; amended in R87—5 at
11 Ill.
Reg.
19383, effective November 12,
1987; amended in R87—
26 at 12 Ill. Reg.
2584,
effective January 15,
1988; amended in
R87—39 at 12 Ill.
Reg.
13069, effective July 29,
1988;
amended in
R88—16 at 13
Ill. Reg.
447, effective December 27,
1988; amended
in R89—1 at
13
Ill. Reg.
18477,
effective November 13,
1989;
amended in R89-9 at 14
Ill. Reg.
6278, effective April 16,
1990;
amended in R90-2 at 14
Ill. Reg.
14492, effective August 22,
1990; amended in R90-11 at 15 Ill. Reg.
9616, effective June 17,
1991; amended in R91—1 at 15 Ill.
Reg.
14554, effective September
30,
1991;
amended in R91-13 at 16 Ill Reg.
9767, effective June
9,
1992;
amended in R92-10 at 16 Ill Reg.
,
effective
SUBPART D:
APPLICATIONS
Section 703.203
Surface Impoundments
For facilities that store, treat or dispose of hazardous waste in
surface impoundments, except as otherwise provided in 35 Ill.
Adin. Code 724.101, the Part B application must include:
a)
A list of the hazardous wastes placed or to be placed
in each surface impoundment;
b)
Detailed plans and an engineering report describing how
the surface impoundment is desicmed and is or will be
dcaigncd, constructed, operated and maintained to meet
the requirements of 35 Ill. Adm. Code 724.119. 724.321~
724.322 and 724.323.
.
Thin submiaoion aunt addrooo the
JuiJ.uwiny
iioma an opooificd in that Ceotion addressing
the following items:
1)
The liner system (except for an existing portion
of a surface impoundment).
If an exemption from
the requirement for a liner is sought as provided
by 35 Ill.
Adm. Code 724.321(b), submit dctailcd
piano and
tnriiiwri-inri
and
hydroqoologio rcpnrti~
rn~
c, acocriDina
‘_
0 136-0539
8
operating prac~ioeothat will,
in oonjunotion with
location anpeot-
rcvcnt thc migration of any
z1~ardouoconstituonto into thc ground-watcr or
surfacc water at any futuro time a co~~
of the
Board order
grant
ma
an adjusted standard pursuant
t9
~1~d*cQ4eJ2L~a2~Lbi;
21
The double liner and leak (leachate)
detection,
collection and removal system. if the surface
impoundment must meet
the
requirements of 35 Ill.
Ada. Code 724.321(c)
•
If an exemption from the
requirements for double liners and a leak
detection,
collection and removal system or
alternative design
j6
sought as orovided by 35
Ill. Adm. Code 724.321(d).
(e) or
(f). submit
popropriate information
fl
If the leak detection system
is located in a
saturated zone.
submit detailed plans and an
engineering report exDlaining the leak detection
system desian and operation,
and the location of
the saturated zone in relation to
the
leak
detection system
4j
The construction qualitY assurance
(COA)
plan if
required under 35 Ill. Ada. Code 724.119
.~j
Prooosed action leakage rate, with rationale,
if
reauired under 35 Iii. Ada, Code 724.322. response
action olan,
if required under 35 Ill. Ada. Code
724.323. and a oropo8ed oump ooerating level,
if
renuired under 35
Ill. Ada. Code 724.326(d) (3)
3
~)
Prevention of overtopping; and
3
2)
Structural integrity of dikes;
C)
A description of how each surface impoundment,
including
the
double liner system, leak detection
system. cover system
and
oover
syotomo and
appurtenances
for
control of overtopping, will be
inspected
in
order
to
meet
the
requirements
of
35
Ill.
Ada.
Code
724.326(a).
a~4(b) and
(d)’. This information
nhoud
must
be
included
in
the
inspection
plan
submitted under Section 703.183(e);
d)
A certification by a qualified engineer which attests
to the structural integrity of each dike,
as required
under 35 Ill. Ada. Code 724.326(c).’ For new units, the
owner or operator aunt shall submit a statement by a
qualified engineer that the engineer will provide such
a certification upon completion of construction in
OI36-05~0
9
accordance
with
the
plans
and
specifications;
e)
A description of the procedure to be used for removing
a surface impoundment from service,
as required under
35 Ill. Ada. Code 724.327(b) and
(c).
This information
ohould must be included in the contingency plan
submitted
‘under
Section 703.183(g);
f)
A description of how hazardous waste residues and
contaminated materials will be removed from the unit at
closure, as required under 35
Ill. Ada. Code
724.328(a) (1). For any wastes not to be removed from
the unit upon closure, the owner or operator aunt shall
submit detailed plans and an engineering report
describing how 35 Ill. Ada. Code 724.328(a) (2) and
(b)
will be complied with.
This information ohould must be
included in the closure plan and, where applicable,
the
post-closure plan submitted under Section 703.183(m);
g)
If ignitable or reactive wastes are to be placed in a
surface impoundment, an explanation of how 35 Ill. Ada.
Code 724.329 will be complied with;
h)
If incompatible wastes, or incompatible wastes and
materials,
will be placed in a surface impoundment, an
explanation of how 35
Ill. Ada. Code 724.330 will be
complied with,-
;
and.
i)
A waste management plan for hazardous waste numbers
F020,
F02l, F022,
F023, F026 and F027 describing how
the surface impoundment is or will be designed,
constructed, operated and maintained to meet the
requirements of 35 Ill. Ada. Code 724.331. This
submission must address the following items as
specified in that Section:
1)
The volume, physical and chemical characteristics
of the wastes, including their potential to
migrate through soil or to volatilize or escape
into the atmosphere;
2)
The attenuative properties of underlying and
surrounding soils or other materials;
3)
The mobilizing properties of other materials
co—disposed with these wastes; and
4)
The effectiveness of additional treatment, design
or monitoring techniques.
BOARD NOTE:
Ccc 40
CFR
270.17 Derived from
40 CFR 270.17
(1991).
as amended at
57 Fed.
013605’41
10
Reg.
3486. January 29,
1992.
(Source:
Amended at 16
Ill. Reg.
,
effective
Section 703.204
Waste Piles
For facilities that store or treat hazardous waste in waste
piles,
except as otherwise provided in 35 Ill. Ada. Code 724.101,
the Part B application must include:
a)
A list of hazardous wastes placed or to be placed in
each waste pile;
b)
If an exemption is sought to 35 Ill. Ada Code 724.351
and 724.Subpart F as provided by 35 Ill. Ada. Code
724.350(c) or 724.190(b) (2),
an explanation of how the
requirements of 35 Ill. Ada. Code 724.350(c) will be
complied with or detailed plans and an engineering
report describing how the requirements of 35 Ill. Ada.
Code 724.190(b) (2) will be met;
c)
Detailed plans and an engineering report describing how
the pile is designed and is or will be dcoigncd,
constructed, operated and maintained to meet the
requirements of 35 Ill. Ada. Code 724.119.
724.351,..
724.352 and 724.353. addressing the following items:
-~
Thin subainnion aunt addreea the following itomo as
BPCOaa.
p~
~
,..Aat
~COta.,.n..
1)
Liner,
leak detection and removal system.
~j
The liner system
(except for an existing
portion of a waste pile),
if the waste pile
must meet the requirements of
35
Ill. Ada.
Code 724
.
351 (a).
If an exemption from the
requirement for a liner is sought,
as
provided by 35 Ill. Ada. Code 724.351(b), the
owner or operator
aunt
nubait detailed piano
and engineering and hydro~eologioroporto no
appropriate, deseribing alternate -deaiqn~and
operatin~practices that will,
in eonjunotion
with location anpoots, prevent the migration
of any haiiardoua constituents into the
~round-uatcr
or
surf
ace
water
at
any
future
time shall submit a
coov
of
the
Board
order
granting
p~
adjusted standard oursua~tto 35
Ill. Ada. Code 724.351(b)
~j.
The double liner and leak (leachate)
detection, collection and removal system.
if
the waste pile must meet the requirements of
0 I36~05’~2
11
35 1)1. Ada. Code 724.351(c).
If an
exemotion from the requirements for double
liners and a leak detection, collection and
removal system or alternative design is
souaht as provided by 35 Ill.
Ada. Code
724.351(d).
(e) or (f). submit,aooropriate
information
Q).
If the leak detection system is located in a
saturated zone,
submit detailed olans and an
engineering report explaining the leak
detection system desi~and operation.
and
the location of the saturated zone in
relation to the leak detection system
21
The COA olan
if
required under 35
Ill.
Ada.
Code 724.119
.~I
Proposed action leakage rate, with rationale.
if required under
35
Ill. Ada. Code 724.352,
and resoonse action plan.
if required under
35 Iii. Ada. Code 724.353
2)
Control of run-on;
3)
Control of run-off;
4)
Management of collection and holding units
associated with run—on and run—off control
systems;
and
5)
Control of wind dispersal of particulate matter,
where applicable;
d)
A description of how each waste pile,
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 724.354(a),
ei’~d(b) and
(c).
This
information should must be included in the inspection
plan submitted under Section 703.183(q
~).
e)
If the treatment is carried out on or in the pile,
details of the process and equipment used, and the
nature and quality of the residuals;
f)
If ignitable or reactive wastes are to be placed in a
waste pile, an explanation of how the requirements of
35 Ill.
Ada. Code 724.356 will be complied with;
g)
If incompatible wastes, or incompatible wastes and
0 I36-Q5L~3
12
materials, will be placed in a waste pile,
an
explanation of how 35 Ill. Ada. Code 724.357 will be
complied with;
h)
A description of how hazardous waste residues and
contaminated materials will be removed from the waste
pile at closure, as required under 35 I.?.
Ada. Code
724.358(a).
For any waste not to be removed from the
waste pile upon closure, the owner or operator aunt
shall submit detailed plans and an engineering report
describing how 35 Ill. Ada. Code 724.410(a)
and
(b)
will be complied with.
This information ohould must be
included in the closure plan and, where applicable, the
post-closure plan submitted under Section 703.183(m)~j
and,
i)
A waste management plan for hazardous waste numbers
F020,
F021, F022,
F023, F026 and F027 describing how
the surface impoundment is or will be designed,
constructed, operated and maintained to meet the
requirements of 35 Ill.
Ada. Code 724.359.
This
submission must address the following items as
specified in that Section:
1)
The volume, physical and chemical characteristics
of the wastes, including their potential to
migrate through soil or to volatilize or escape
into the atmosphere;
2)
The attenuative properties of underlying and
surrounding soils or other materials;
3)
The mobilizing properties of other materials
co—disposed with these wastes; and
4)
The effectiveness of additional treatment, design
or monitoring techniques.
BOARD NOTE:
Ccc 40
CFR
270.18Derived from 40
CFR
270.18
(1991). as amended at 57 Fed.
Reg.
3486, January 29. 1992.
(Source:
Amended at 16 Ill. Reg.
,
effective
)
Section 703.207
Landfills
For facilities that dispose of hazardous waste in landfills,
except as otherwise provided in 35 Ill. Ada. Code 724.101, the
Part B application must include:
a)
A list of the hazardous wastes placed or to be placed
Ot36-Q5’~’4
13
in each landfill or landfill cell;
b)
Detailed plans and an engineering report describing how
the landfill is designed and is or will be designed,
constructed, operated and maintained to comply with
meet the requirements of 35 Ill. Adm~ç~4e_,
724,119.
724.401.
724.402 and 724.403. addressina the following
items:.
Thin submission aunt addrooo the following
items an specified in that Ceotioni
1)
Liner,
leak detection.
collection and removal
systems.
~j
The liner system and lcaohatc oollcotion and
rcmoval system (except for an existing
portion of a landfill).
if the landfill must
meet the requirements of 35 Ill. Ada. Code
724.401(a).
If an exemption from the
requiremente for a liner and a lcaohatc
aoiication
an~rcmovai. system is sought as
provided by 35 Ill. Ada. Code 724.401(b),
submit detailed plans engineering and
hydrogoologic reports an appropriate,
describing alternate
design
and operating
practices that will,
in conjunction with
location aspects, prevent the migration of
any haeardoua constituent into the
r’-oundwatcr or surface water at any future
tiac a copy of the Board order granting an
adjusted standard oursuant to 35 Ill. Ada.
Code 724.401(b)
~j
The double liner and leak (leachate)
detection, collection and removal system,
if
the landfill must meet the requirements of 35
Ill. Ada. Code 724.401(c).
If an exemotion
from the requirements for double
liners
and
a
leak detection, collection and removal system
or alternative design is sought as provided
by 35 Ill.
Ada. Code 724.401(d).
(e) or
(f).
submit aporooriate information:
~j
If the leak detection system is located in a
saturated zone. submit detailed olans and an
engineering reoort explainina the leak
detection system desian and operation. and
the location of the saturated zone in
relation to the leak detection system
Qj
The CQA olan if required under 35 Ill. Ada.
Code 724.119
01 36-05~5
14
£1
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 ~rooosed pump
operating level,
if required under 35 Ill.
Ada. Code 724.4O3:~
2)
Control of run-on;
3)
Control
of
run-off;
4)
Management of collection and holding facilities
associated with run—on and run—off control
systems; and
5)
Control of wind dispersal of particulate matter,
where
applicable;
c)
If an exemption from 35 Ill. Ada. Code 724.Cubpart F is
nought,
no
provided
by
35
Ill.
Ada.
Code
724.402(n),
the owner or operator aunt oubmit detailed
plans
and
an
engineering report explaining the
location
of the
saturated ~onc in relation to the landfill, the design
of a double-liner system that incorporates a leak
detection system between the lincré and a loachato
collection and removal nystca above the liners 7 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)
;
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 should must be
included in the inspection plan submitted under Section
703.183(e);
e)
Detailed plans and an engineering report describing the
final cover which will be applied to each landfill or
landfill cell at closure in accordance with 35 Ill.
Ada. Code 724.410(a), and a description of how each
landfill will be maintained and monitored after closure
in accordance with 35 Ill. Ada. Code 724.410(b).
This
information should must be included in the closure and
post—closure plans submitted under Section 703.183(m);
f)
If ignitable or reactive wastes will be landfilled,
an
0136-05146
15
explanation of how the requirements of 35
Ill. Ada.
Code 724.412 will be complied with;
g)
If incompatible wastes,
or incompatible wastes and
materials,
will
be
landfilled,
an explanation of how 35
Ill. Ada. Code 724.413 will be complied with;
h)
If bulk or non-containerized liquid waste or waste
containing free liquids is to be landfilled, an
explanation of how the requirements of 35 Ill. Ada.
Code 724.414 will be complied with;
i)
If containers of hazardous waste are to be landfilled,
an explanation of how the requirements of 35 Ill. Ada.
Code 724.415 or 724.416, as applicable, will be
complied with,-
:
and,
j)
A waste management plan for hazardous waste numbers
F020, F021, F022,
F023, F026 and F027 describing how a
landfill is or will be designed, constructed, operated
and maintained to meet the requirements of 35 Ill. Ada.
Code 724.417.
This submission must address the
following items as specified in that Section:
1)
The
volume,
physical
and
chemical characteristics
of the wastes, including their potential to
migrate through soil or to volatilize or escape
into the atmosphere;
2)
The attenuative properties of underlying and
surrounding soils or other materials;
3)
The mobilizing properties of other materials
co—disposed with these wastes; and
4)
The
effectiveness
of
additional treatment, design
or monitoring techniques.
BOARD NOTE: Ccc 40
CFR
270.2lDerived from 40
CFR
270.21 (1991). as amended at
57
Fed.
Rep.
3486. January 29.
1992.
(Source:
Amended at 16 Ill. Reg.
,
effective
)
Section 703.Appendix A
Classification of Permit Modifications
Class
Modifications
A.
General Permit Provisions
1.
Administrative and informational changes.
O136-05~7
16
1
2.
Correction
of
typographical
errors.
1
3.
Equipment replacement or upgrading with
functionally equivalent components
(e.g., pipes,
valves, pumps,
conveyors, controls).
4.
Changésin the frequency of or procedures for
monitoring,
reporting,
sampling or maintenance
activities by the permittee:
1
a.
To provide for more frequent monitoring,
reporting or maintenance.
2
b.
Other changes.
5.
Schedule of compliance:
1*
a.
Changes in interim compliance dates,
with
prior approval of the Agency.
BOARD NOTE:
~
indicates that prior Agency
approval is required.
3
b.
Extension of final compliance date.
1*
6.
Changes in expiration date of permit to allow
earlier permit termination, with prior approval of
the Agency.
1*
7.
Changes in ownership or operational control of a
facility,
provided
the procedures of Section
703.260(b)
are followed.
B.
General Facility Standards
1.
Changes to waste sampling or analysis methods:
1
a.
To conform with Agency guidance or Board
regulations.
1
b.
To incorporate changes associated with F039
(multi—source leachate) sampling or analysis
methods.
2
c.
Other changes.
2.
Changes to analytical quality assurance/control
plan:
1
a.
To conform with agency guidance or
regulations.
013605148
17
2
b.
Other changes.
1
3.
Changes
in
procedures
for
maintaining
the
operating record.
2
4.
Changes in frequency or content of inspection
schedules.
5.
Changes in the training plan:
2
a.
That affect the type or decrease the amount
of training given to employees.
1
b.
Other changes.
6.
Contingency plan:
2
a.
Changes in emergency procedures
(i.e.,
spill
or release response procedures).
1
b.
Replacement
with
functionally
equivalent
equipment, upgrade or relocate emergency
equipment listed.
2
c.
Removal of equipment from emergency equipment
list.
1
d.
Changes in name,
address or phone number of
coordinators or other persons or agencies
identified in the plan.
Note:
When a permit modification (such as
introduction of a new unit) requires a change
in facility plans or other general facility
standards,
that change must be reviewed under
the same procedures as the permit
modification.
L~.
COA
olan:
~
Changes that the CQA officer certifies in the
operatina record will orovide equivalent or
better certainty that the unit comoonents
meet the desian specifications.
z
~
Other changes.
C.
Groundwater Protection
1.
Changes to wells:
2
a.
Changes in the number,
location, depth or
0136-05149
18
design of upgradient or downgradient wells of
permitted groundwater monitoring system.
1
b.
Replacement of an existing well that has been
damaged or rendered inoperable, without
change to location, design or depth, of the
well.
1*
2.
Changes in groundwater sampling or analysis
procedures or monitoring schedule, with prior
approval of the Agency.
1*
3.
Changes in statistical procedure for determining
whether a statistically significant change in
groundwater quality between upgradiertt and
downgradient
wells
has
occurred,
with
prior
approval of the Agency.
2*
4.
Changes in point of compliance.
5.
Changes in indicator parameters,
hazardous
constituents or concentration limits (including
ACL5 (Alternate Concentration Limits)):
3
a.
As specified in the groundwater protection
standard.
2
b.
As specified in the detection monitoring
program.
2
6.
Changes to a detection monitoring program as
required by 35 Ill. Ada. Code 724.198(j),
unless
otherwise specified in this Appendix.
7.
Compliance monitoring program:
3
a.
Addition of compliance monitoring program as
required by 35 Ill. Ada. Code 724.198(h) (4)
and 724.199.
2
b.
Changes to a compliance monitoring program as
required by 35 Ill. Ada. Code 724.199(k),
unless otherwise specified in this Appendix.
8.
Corrective action program:
3
a.
Addition of a corrective action program as
required by 35 Ill. Ada. Code 724.199(i) (2)
and 724.200.
2
b.
Changes to a corrective action program as
required by 35 Ill. Ada. Code 724.200(h),
0136-0550
19
unless otherwise specified in this Appendix.
D.
Closure
1.
Changes to the closure plan:
1*
a.
Changes in estimate of maximum extent of
operations or maximum inventory of waste on—
site at any time during the active life of
the facility, with prior approval of the
Agency.
1*
b.
Changes in the closure schedule for any unit,
changes in the final closure schedule for the
facility or extension of the closure period,
with prior approval of the Agency.
1*
c.
Changes in the expected year of final
closure, where other permit conditions are
not changed, with prior approval of the
Agency.
1*
d.
Changes in procedures for decontamination of
facility equipment or structures, with prior
approval of the Agency.
2
e.
Changes in approved closure plan resulting
from unexpected events occurring during
partial or final closure, unless otherwise
specified in this Appendix.
2
f.
Extension of the closure period to allow a
landfill, surface impoundment or land
treatment unit to receive non—hazardous
wastes after final receipt of hazardous
wastes under 35 Ill. Ada. Code 724.213(d)
or
(e).
3
2.
Creation of a new landfill unit as part of
closure.
3.
Addition of the following new units to be used
temporarily for closure activities:
3
a.
Surface impoundments.
3
b.
Incinerators.
3
c.
Waste piles that do not comply with 35 Ill.
Ada. Code 724.350(c).
2
d.
Waste piles that comply with 35 Ill. Ada.
0 136-0551
20
Code 724.350(c).
2
e.
Tanks or containers
(other than specified
below).
1
*
f
Tanks
used for
neutralization,
dewatering,
phase separation or component separation,
with prior approval of the Agency.
E.
Post-Closure
1.
Changes in name, address or phone number of
contact in post—closure plan.
2
2.
Extension of post-closure care period.
3
3.
Reduction in the post-closure care period.
4.
Changes to the expected year of final closure,
where other permit conditions are not changed.
2
5.
Changes in post—closure plan necessitated by
events occurring during the active life of the
facility,
including partial and final closure.
F.
Containers
1.
Modification or addition of container units:
3
a.
Resulting in greater than 25
increase in the
facility’s container storage capacity, except
as provided in F(1)(c) and F(4)(a).
2
b.
Resulting in up to 25
increase in the
facility’s container storage capacity, except
as provided in F(1) (c) and F(4) (a).
c.
Or treatment processes necessary to treat
wastes that are restricted from land disposal
to meet some or all of the applicable
treatment standards or to treat wastes to
satisfy (in whole or in part) the standard of
“use of practically available technology that
yields the greatest environmental benefit”
contained in 40 CFR 268.8(a) (2) (ii),
incorporated by reference in 35 Ill. Ada.
Code 728.108, with prior approval of the
Agency.
This modification may also involve
the addition of new waste codes or narrative
description of wastes.
It is not applicable
to dioxin—containing wastes
(F020, F021,
F022,
F023, F026,
F027 and F028).
0136-0552
21
2.
2
a.
Modification of a container unit without
increasing the capacity of the
unit.
b.
Addition of a roof to a container unit
without alteration of the containment system.
3.
Storage of different wastes in containers,
except
as provided in F(4):
3
a.
That require additional or different
management practices from those authorized in
the permit.
2
b.
That do not require additional or different
management practices from those authorized in
the permit.
Note:
See Section 703.280(g)
for
modification procedures to be used for the
management of newly listed or identified
wastes.
4.
Storage or treatment of different wastes in
containers:
2
a.
That require addition of units or change in
treatment process or management standards,
provided that the wastes are restricted from
land disposal and are to be treated to meet
some or all of the applicable treatment
standards, or are to be treated to satisfy
(in whole or in part)
the standard of “use of
practically available technology that yields
the greatest environmental benefit” contained
in 40
CFR
268.8(a) (2) (ii),
incorporated by
reference in 35
Ill. Ada. Code 728.108.
It
is not applicable to dioxin-containing wastes
(F020,
P021, F022,
F023,
P026, P027 and
P028).
b.
That do not require the addition of units or
a change in the treatment process or
management standards, and provided that the
units have previously received wastes of the
same type (e.g.,
incinerator scrubber water).
This modification is not applicable to
dioxin-containing wastes
(F020, F021,
F022,
F023,
F026, F027 and F028).
G.
Tanks
0
I 36-0553
22
1.
3
a.
Modification or addition of tank units
resulting in greater than 25
increase in the
facility’s tank capacity, except as provided
in paragraphs G(1)~(c),.G.(.1).(d) ..,.and~.(1).4e.)
2
b.
Modification or addition of tank units
resulting in up to 25
increase in the
facility’s tank capacity, except as provided
in paragraphs G(1) (d) and G(1) (e).
2
c.
Addition of a new tank that will operate for
more than 90 days using any of the following
physical or chemical treatment technologies:
neutralization,
dewatering, phase separation
or component separation.
1*
d.
After prior approval of the Agency, addition
of a new tank that will operate for up to 90
days using any of the following physical or
chemical treatment technologies:
neutralization,
dewatering,
phase
separation
or component separation.
e.
Modification or addition of tank units or
treatment processes that are necessary to
treat wastes that are restricted from land
disposal to meet some or all of the
applicable treatment standards or to treat
wastes to satisfy
(in whole or in part)
the
standard of “use of practically available
technology that yields the greatest
environmental benefit” contained in 40 CFR
268.8(a)
(2)
(ii), ‘incorporated by reference in
35
Ill.
Ada.
Code
728.108,
with
prior
approval of the Agency.
This modification
may also involve the addition of new waste
codes.
It is not applicable to dioxin-
containing wastes
(P020, P021,
P022,
F023,
P026, P027 and F028).
2
2.
Modification of a tank unit or secondary
containment system without increasing the capacity
of the unit.
3.
Replacement of a tank with a ‘tank that meets the
same design standards and has a capacity within
+/-
10
of the replaced tank provided:
a.
The capacity difference is no more than 1500
gallons,
0136-05514
23
b.
The facility’s permitted tank capacity is not
increased and
c.
The replacement tank meets the same
conditions in the permit.
2
4.
Modification of a tank management practice.
5.
Management of different wastes in tanks:
3
a.
That require additional or different
management practices, tank design, different
fire protection specifications or
significantly different tank treatment
process from that authorized in the permit,
except as provided in paragraph G(5)
(C).
2
b.
That do not require additional or different
management practices, tank design, different
fire protection specification or
significantly different tank treatment
process than authorized in the permit, except
as provided in paragraph G(5) (d).
Note:
See Section 703.280(g)
for
modification procedures to be used for the
management of newly listed or identified
wastes.
c.
That require addition of units or change in
treatment processes or management standards,
provided that the wastes are restricted from
land disposal and are to be treated to meet
some or all of the applicable treatment
standards, or that are to be treated to
satisfy (in whole or in part) the standard of
“use of practically available technology that
yields the greatest environmental benefit”
contained in 40
CPR
268.8(a) (2)
(ii),
incorporated by reference in 35 Ill. Ada.
Code 728.108.
The modification is not
applicable to dioxin—containing wastes
(P020,
P021,
P022, P023,
P026, P027 and P028).
d.
That do not require the addition of units or
a change in the treatment process or
management standards, and provided that the
units have previously received wastes of the
same type
(e.g., incinerator scrubber water).
This modification is not applicable to
dioxin-containing wastes
(F020,
P021, P022,
F023, F026,
P027 and P028).
0136-0555
24
H.
Surface
Impoundments
3
1.
Modification or addition of surface impoundment
units that result in increasing the facility’s
surface impoundment storage or treatment capacity.
3
2.
Replacement of a surface impoundment unit.
2
3.
Modification of a surface impoundment unit without
increasing the facility’s surface impoundment
storage or treatment capacity and without
modifying the unit’s liner,
leak detection system
or leachate collection system.
2
4.
Modification of a surface impoundment management
practice.
5.
Treatment,
storage
or
disposal
of
different
wastes
in
surface
impoundments:
3
a.
That require additional or different
management practices or different design of
the
liner
or leak detection system than
authorized in the permit.
2
b.
That do not require additional or different
management practices or different design of
the liner or leak detection system than
authorized in the permit.
Note:
See Section 703.280(g)
for
modification procedures to be used for the
management of newly listed or identified
wastes.
c.
That are wastes restricted from land disposal
that meet the applicable treatment standards
or that are treated to satisfy the standard
of “use of practically available technology
that
yields
the
greatest
environmental
benefit” contained in 40
CFR
268.8(a) (2) (ii),
incorporated by reference in 35 Ill. Ada.
Code 728.108, and provided that the unit
meets the minimum technological requirements
stated in 40
CFR
268.5(h) (2), incorporated by
reference in 35 Ill. Ada. Code 728.105.
This
modification is not applicable to dioxin-
containing wastes
(P020, P021,
F022,
P023,
F026,
F027 and F028).
d.
That are residues from wastewater treatment
or
incineration,
provided
the disposal occurs
0136-0556
25
in a unit that meets the minimum
technological requirements stated in 40 CFR
268
•
5(h) (2), incorporated by reference in 35
Ill. Ada. Code 728.105, and provided further
that the surface
impoundment
has previously
received wastes of the~sametype ~1,or.
example,
incinerator scrubber water).
This
modification is not applicable to dioxin-
containing wastes
(P020,
P021,
P022, P023,
P026, P027 and P028).
~
Modifications of unconstructed units to comoly
with
35
Ill.
Ada.
Code
724.321(c).
724.322,
724.323 and 724.326(d).
~
Changes
in resoonse action plan:
3
~
Increase in action leakaae rate.
3
—
~
Chance in a soecific resoonse reducing its
frequency or effectiveness.
2
—
ç~
Other changes.
I.
Enclosed Waste Piles.
For all waste piles,
except
those complying with 35 Ill.
Ada. Code 724.350(c),
modifications are treated the same as for a landfill.
The following modifications are applicable only to
waste piles complying with 35 Ill. Ada. Code
724.350(c).
1.
Modification or addition of waste pile units:
3
a.
Resulting in greater than 25
increase in the
facility’s waste pile storage or treatment
capacity.
2
b.
Resulting in up to 25
increase in the
facility’s waste pile storage or treatment
capacity.
2
2.
Modification of waste pile unit without increasing
the capacity of the unit.
3.
Replacement of a waste pile unit with another
waste pile unit of the same design and capacity
and meeting all waste pile conditions in the
permit.
2
4.
Modification of a waste pile management practice.
5.
Storage or treatment of different wastes in waste
0 136-0557
26
piles:
3
a.
That require additional or different
management practices or different design of
the
unit.
2
b.
That
do
not
require
additional or different
management practices or different design of
the
unit.
Note:
See Section 703.280(g)
for
modification procedures to
be
used
for
the
management of newly listed or identified
wastes.
J.
Landfills and Unenclosed Waste Piles
3
1.
Modification or addition of landfill units that
result in increasing the facility’s disposal
capacity.
3
2.
Replacement of a landfill.
3
3.
Addition or modification of a liner,
leachate
collection system, leachate detection system, run—
off control or final cover system.
2
4.
Modification of a landfill unit without changing a
liner,
leachate collection
system,
leachate
detection system, run—off control or final cover
system.
2
5.
Modification of a landfill management practice.
6.
Landfill different wastes:
3
a.
That require additional or different
management practices, different design of the
liner, leachate collection system or leachate
detection system.
2
b.
That do not.require additional or different
management practices, different design of the
liner,
leachate collection system or leachate
detection system.
Note:
See Section 703.280(g)
for
modification
procedures
to
be used for the
management of newly listed or identified
wastes.
c.
That are wastes restricted from land disposal
0136-0558
27
that meet the applicable treatment standards
or that are treated to satisfy the standard
of “use of practically available technology
that
yields
the
greatest
environmental
benefit” contained in 40
CPR
268.8(a) (2) (ii),
incorporated by referencE...in~
..3,.5
Ii..
Ada.
Code 728.108, and provided that the landfill
unit meets the minimum technological
requirements stated in 40 CFR 268.5(h) (2),
incorporated by reference in 35 Ill. Ada.
Code 728.105.
This modification
is
not
applicable to dioxin-containing wastes
(P020,
P021,
P022,
P023, P026,
P027 and P028).
d.
That are residues from wastewater treatment
or incineration, provided the disposal occurs
in a landfill unit that meets the minimum
technological requirements stated in 40 CFR
268.5(h) (2), incorporated by reference in 35
Ill.
Ada. Code 728.105, and provided further
that the landfill has previously received
wastes of the same type (for example,
incinerator ash).
This modification is not
applicable to dioxin—containing wastes
(F020,
F021, P022,
F023,
F026,
P027 and F028).
1*
7.
Modification of unconstructed units to comply with
35
Ill.
Ada. Code 724.351(c).
724.352,
724.353.
724.354(c).
724.401(c)
724.402.
724.403(c)
and
724.404.
~
Changes in response action olan:
a~
Increase in action leakaae rate.
3
—
~
Chanae in a specific response reducing its
frequency or effectiveness.
2.
—
~
Other chanaes.
K.
Land Treatment
3
1.
Lateral expansion of or other modification of a
land
treatment
unit
to
increase
area
extent.
2
2.
Modification
of
run—on
control system.
3
3.
Modify
run-off
control
system.
2
4.
Other modification of land treatment unit
component specifications or standards required in
permit.
0136- 0559
28
5.
Management of different wastes in land treatment
units:
3
a.
That
require
a
change
in
permit
operating
conditions or unit design specifications.
2
b.
That do not require a change in permit
operating conditions or unit design
specifications.
Note:
See Section 703.280(g)
for
modification procedures to be used for the
management of newly listed or identified
wastes.
6.
Modification of a land treatment unit management
practice to:
3
a.
Increase rate or change method of waste
application.
b.
Decrease
rate
of
waste
application.
2
7.
Modification
of
a
land
treatment
unit
management
practice to change measures of pH or moisture
content or to enhance microbial or chemical
reactions.
3
.
8.
Modification of a land treatment unit
management
practice to grow food chain crops, to add to or
replace existing permitted crops with different
food chain crops or to modify operating plans for
distribution of animal feeds resulting from such
crops.
3
9.
Modification of operating practice due to
detection of releases from the land treatment unit
pursuant
to
35
Ill.
Ada.
Code
724.378(g)
(2).
3
10.
Changes in the unsaturated zone monitoring system
resulting in a change to the location, depth,
number of sampling points or replace unsaturated
zone monitoring devices or components of devices
with devices or components that have
specifications
different
from
permit
requirements.
2
11.
Changes
in
the
unsaturated
zone
monitoring
system
that do not result in a change to the location,
depth,
number
of sampling points, or that replace
unsaturated zone monitoring devices or components
of devices with devices or components having
specifications different from permit requirements.
0136-0560
29
2
12.
Changes in background values for hazardous
constituents
in
soil
and
soil—pore
liquid.
2
13.
Changes in sampling, analysis or statistical
procedure.
2
14.
Changes in land treatment demonstration program
prior
to
or
during
the
demonstration.
1*
15.
Changes
in
any
condition
specified
in
the
permit
for
a
land
treatment
unit to reflect results of
the
land
treatment
demonstration,
provided
performance standards are met, and the Agency’s
prior approval has been received.
1*
16.
Changes to allow a second land treatment
demonstration to be conducted when the results of
the
first
demonstration
have
not
shown
the
conditions under which the wastes can be treated
completely, provided the conditions for the second
demonstration
are
substantially
the
same
as
the
conditions
for
the
first
demonstration
and
have
received the prior approval of the Agency.
3
17.
Changes to allow a second land treatment
demonstration to be conducted when the results of
the
first demonstration have not shown the
conditions
under
which
the
wastes
can
be
treated
completely, where the conditions for the second
demonstration
are
not
substantially
the
same
as
the
conditions
for
the
first
demonstration.
2
18.
Changes in vegetative cover requirements for
closure.
L.
Incinerators, Boilers and Industrial Furnaces
3
1.
Changes to increase by more than 25
any of the
following limits authorized in the permit: A
thermal feed rate limit,
a feedstream feed rate
limit,
a chlorine/chloride feed rate limit,
a
metal feed rate limit or an ash feed rate limit.
The Agency shall require a new trial burn to
substantiate compliance with the regulatory
performance
standards
unless
this
demonstration
can
be
made
through
other
means.
2
2.
Changes to increase by up to 25
any of
the
following limits authorized in the permit:
A
thermal feed rate limit, a feedetream feed rate
limit,
a chlorine/chloride feed rate limit,
a
metal
feed
rate
limit
or
an
ash feed rate limit.
0136-056
1
30
The Agency shall require a new trial burn to
substantiate compliance with the regulatory
performance standards unless this demonstration
can be made through other means.
3
3.
Modification of an. incinerator, ~boi1er.~.or
industrial furnace unit by changing the internal
size or geometry of the primary or secondary
combustion units, by adding a primary or secondary
combustion unit, by substantially changing the
design of any component used to remove HC1/Cl2,
metals or particulate from the combustion gases or
by changing other features of the incinerator,
boiler or industrial furnace that could affect its
capability to meet the regulatory performance
standards.
The
Agency
shall require a new trial
burn
to
substantiate
compliance
with
the
regulatory performance standards, unless this
demonstration
can
be made through other means.
2
4.
Modification of an incinerator, boiler or
industrial furnace unit in a manner that will not
likely affect the capability of the unit to meet
the regulatory performance standards but which
will
change
the
operating conditions or monitoring
requirements
specified
in
the
permit.
The
Agency
may
require
a
new
trial burn to demonstrate
compliance
with
the
regulatory
performance
standards.
5.
Operating requirements:
3
a.
Modification of the limits specified in the
permit for minimum or maximum combustion gas
temperature, minimum combustion gas residence
time,
oxygen concentration in the secondary
combustion chamber, flue gas carbon monoxide
or hydrocarbon concentration,’ maximum
temperature at the inlet to the PM emission
control system or operating parameters for
the air pollution control system.
The Agency
shall require a new trial burn to
substantiate compliance with the regulatory
performance standards unless this
demonstration can be made through other
means.
3
b.
Modification of any stack gas emission limits
specified in the permit, or modification of
any conditions in the permit concerning
emergency shutdown or automatic waste feed
0136-0562
31
cutoff procedures or controls.
2
c.
Modification of any other operating condition
or any inspection or recordkeeping
requirement specified in the permit.
6.
Burning different wastes:
3
a.
If
the
waste
contains
a
POHC
that
is
more
difficult to burn than authorized by the
permit or if burning of the waste requires
compliance with different regulatory
performance
standards
than
specified
in
the
permit, the Agency shall require a new trial
burn to substantiate compliance with the
regulatory performance standards, unless this
demonstration can be made through other
means.
2
b.
If the waste does not contain a POHC that is
more difficult to burn than authorized by the
permit and if burning of the waste does not
require compliance with different regulatory
performance standards than specified in the
permit.
BOARD NOTE:
See Section 703.280(g)
for
modification procedures to be used for the
management of newly listed or identified
wastes.
7.
Shakedown and trial burn:
2
a.
Modification of the trial burn plan or any of
the permit condjtions applicable during the
shakedown period for determining operational
readiness after construction, the trial burn
period or the period immediately following
the trial burn.
1*
b.
Authorization
of
up
to
an
additional
720
hours of waste burning during the shakedown
period for determining operational readiness
after construction, with the prior approval
of the Agency.
1*
c.
Changes in the operating requirements set in
the permit for conducting a trial burn,
provided the change is minor and has received
the
prior
approval
of
the
Agency.
1*
d.
Changes in the ranges of the operating
0136-0563
32
requirements set in the permit to reflect the
results of the trial burn, provided the
change is minor and has received the prior
approval of the Agency.
8.
Substitution of ~an alternate,
type-of nonhazardous
waste
fuel that is not specified in the permit.
BOARD
NOTE:
Derived from 40
CFR
270.42, Appendix
I
(1990),
as
amended
at
56
Fed.
Reg.
7206,
February
21,
1991.
(Source:
Amended at 16 Ill.
Reg.
,
effective
)
013605614
33
TITLE
35:
ENVIRONMENTAL
PROTECTION
SUBTITLE G:
WASTE
DISPOSAL
CHAPTER
I:
POLLUTION
CONTROL
BOARD
SUBCHAPTER c:
HAZARDOUS
WASTE
OPERATING
REQUIREMENTS
PART
720
HAZARDOUS
WASTE
MANAGEMENT
SYSTEM:
GENERAL
SUBPART
A:
GENERAL
PROVISIONS
Section
720.101
Purpose, Scope and Applicability
720.102
Availability of Information; Confidentiality of
Information
720.103
Use of Number and Gender
SUBPART B:
DEFINITIONS
SUBPART
C:
RULEMAKING PETITIONS
AND
OTHER PROCEDURES
Section
Rulemaking
Alternative Equivalent Testing Methods
Waste Delisting
Procedures
for
Solid
Waste
Determinations
Solid Waste Determinations
Boiler
Determinations
Procedures
for
Determinations
Additional regulation of certain hazardous waste
Recycling Activities on a case—by-case Basis
720.141
Procedures for case—by—case regulation of hazardous
waste Recycling Activities
Appendix A
Overview of 40 CPR, Subtitle C Regulations
AUTHORITY:
Implementing Section 22.4 and authorized by Section
27 of the Environmental Protection Act (Ill. Rev.
Stat.
1991,
ch.
111½,
pars.
1022.4 and 1027).
SOURCE:
Adopted in R81—22,
43 PCB 427, at 5 Ill. Reg.
9781,
effective as noted in 35 Ill. Ada.
Code, 700.106; amended and
codified in R8l—22,
45 PCB 317, at 6 Ill. Reg.
4828, effective as
noted in 35 Ill. Ada. Code 700.106; amended in R82-19 at 7
Ill.
Reg.
14015,
effective Oct.
12,
1983; amended in R84—9,
53 PCB 131
at 9
Ill. Reg.
11819, effective July 24,
1985; amended in R85—22
at 10 Ill.
Reg.
968, effective January 2,
1986; amended in R86—1
at 10 Ill.
Reg.
13998, effective August 12,
1986; amended in R86-
19 at
10 Ill. Reg. 20630, effective December 2,
1986; amended in
R86-28 at 11 Ill. Reg.
6017, effective March 24, ‘1987; amended in
R86-46 at 11 Ill.
Reg.
13435, effective August
4,
1987; amended
in R87—5 at 11 Ill. Reg.
19280, effective November 12,
1987;
0136-0565
Section
720.110
720. 111
Definitions
References
720. 120
720.121
720.
122
720.
130
720.
131
720.
132
720.
133
720. 140
34
amended in R87-26 at 12
Ill.,
Reg. 2450, effective January 15,
1988;
amended in R87—39 at 12
Ill. Reg.
12999, effective July 29,
1988;
amended in R88—16 at 13
Ill. Reg. 362, effective December
27,
1988; amended in R89—1 at
13
Ill. Reg.
18278, effective
November
13,
1989;
amended
in
R89—2
at
14
Ill.
Reg.
3075,
effective February 20,
1990~..anended.in R89-9 at 14 Iii.. Reg.
6225, effective April 16,
1990;
amended in R90—10 at 14 Ill. Reg.
16450, effective September 25,
1990; amended in R90—17 at 15 Ill.
Req.
7934,
effective
May
9,
1991;
amended
in
R90—11
at
15
Ill.
Reg. 9323, effective June 17, 1991; amended in R91—l at 15 Ill.
Reg.
14446, effective September 30,
1991;
amended
in R91—13 at
16 Ill. Reg. 9489, effective June 9,
1992;
amended in R92—1 at
16
Ill. Reg.
,
effective
;
amended in R92-
10 at 16 Ill. Reg.
,
effective
SUBPART B:
DEFINITIONS
Section 720.110
Definitions
When used in 35 Ill.
Ada. Code 720 through 726 and 728 only, the
following terms have the meanings given below:
“Aboveground tank” means
a device meeting the
definition of “tank” that is situated in such a way
that the entire surface area of the tank is completely
above the plane of the adjacent surrounding surface and
the entire surface area of the tank (including the tank
bottom)
is able to be visually inspected.
“Act” or “RCRA” means the Solid Waste Disposal Act, as
amended by the Resource Conservation and Recovery Act
of 1976,
as amended
(42 U.S.C.
6901 et seq.)
“Active life” of a facility means the period from the
initial receipt of hazardous waste at the facility
until the Agency receives certification of final
closure.
“Active portion” means that portion of a facility where
treatment, storage or disposal operations are being or
have been conducted after May 19,
1980, and which is
not a closed portion.
(See also “closed portion” and
“inactive portion”.)
“Administrator” means the Administrator of the U.S.
Environmental Protection Agency or the Administrator’s
designee.
“Agency” means the Illinois Environmental Protection
Agency.
“Ancillary equipment” means any device including,
but
0136-0566
35
not limited to, such devices as piping,
fittings,
flanges, valves and pumps, that is used to distribute,
meter or control the flow of hazardous waste from its
point of generation to storage or treatment tank(s),
between hazardous waste storage and treatment tanks to
a point of disposaL. onsite,..or to a
~point.
-of shipment
for disposal off-site.
“Aquifer” means a geologic formation, group of
formations or part of a formation capable of yielding a
significant amount of groundwater to wells or springs.
“Authorized representative” means the person
responsible for the overall operation of a facility or
an operational unit
(i.e., part of a facility),
e.g.,
the
plant manager,
superintendent or person of
equivalent
responsibility.
“Board” means the
Illinois
Pollution
Control
Board.
“Boiler”
means
an enclosed device using controlled
flame combustion and having the following
characteristics:
The unit must have physical provisions for
recovering and exporting thermal energy in the
form of steam, heated fluids or heated gases; and
the unit’s combustion chamber and primary energy
recovery section(s) must be of integral design.
To be of integral design, the combustion chamber
and the primary energy recovery section(s)
(such
as waterwalls and superheaters) must be physically
formed into one manufactured or assembled unit.
A
unit in which the combustion chamber and the
primary energy recovery section(s)
are joined only
by ducts or connections carrying flue gas is not
integrally designed; however, secondary energy
recovery equipment (such as economizers or air
preheaters) need not be physically formed into the
same unit as the combustion chamber and the
primary energy recovery section.
The following
units are not precluded from being boilers solely
because they are not of integral design:
process
heaters
(units that transfer energy directly to a
process stream), and fluidized
bed
combustion
units; and
While
in operation, the unit must maintain a
thermal
energy
recovery
efficiency
of
at
least
60
percent, calculated in terms of the recovered
energy compared with the thermal value of the
fuel;
and
0136-0567
36
The
unit
must
export
and utilize at least 75
percent
of the recovered energy, calculated on an
annual
basis.
In
this
calculation,
no
credit
shall be given for recovered heat used internally
in the same unit.
(Examples of internal use are
the preheating.,of fuel or combustion. air1 and the
driving of induced or forced draft fans or
feedwater pumps); or
The unit is one which the Board has determined,
on
a case—by—case basis,
to be a boiler,
after
considering the standards in Section 720.132.
“Carbon regeneration unit” means any enclosed thermal
treatment device used to regenerate spent activated
carbon.
“Certification” means a statement of professional
opinion based upon knowledge and belief.
“Closed Portion” means that portion of a facility which
an owner or operator has closed in accordance with the
approved facility closure plan and all applicable
closure requirements.
(See also “active portion” and
“inactive portion”.)
“Component”
means
either
the
tank
or
ancillary
equipment
of
a
tank
system.
“Confined aquifer” means an aquifer bounded above and
below by impermeable beds or by beds of distinctly
lower permeability than that of the aquifer itself; an
aquifer containing confined groundwater.
“Container” means any portable device in which a
material is stored,
transported, treated, disposed of
or otherwise handled.
“Contingency plan” means a document setting out an
organized, planned and coordinated course of action to
be followed in case of a fire, explosion or release of
hazardous waste or hazardous waste constituents which
could threaten human
health
or
the
environment.
“Corrosion
expert” means a person who, by reason of
knowledge of the physical sciences and the principles
of engineering and mathematics, acquired by a
professional education and related practical
experience,
is qualified to engage in the practice of
corrosion control on buried or submerged metal piping
systems and metal tanks.
Such a person must be
certified as being qualified by the National
0136-0568
37
Association of Corrosion Engineers
(NACE)
or be a
registered
professional
engineer
who
has
certification
or
licensing
that
includes education and experience in
corrosion control on buried or submerged metal piping
systems
and
metal
tanks.
“Designated facility” means a hazardous waste
treatment,
storage or disposal facility,
Which:
Has received a
RCRA
permit
(or
interim
status) pursuant to 35 Ill. Ada. Code 702,
703
and
705;
Has
received
a
RCRA
permit from USEPA
pursuant
to
40
CFR
124
and
270
(1~J89
1991);
Has received a RCRA permit from a state
authorized by USEPA pursuant to 40 CFR 271
(1~8~l991);or
Is regulated under 35 Ill. Ada. Code
721.106(c)
(2)
or
266.Subpart
F;
and
Which has been designated on the manifest by the
generator pursuant to 35 Ill. Ada. Code 722.120.
If a waste is destined to a facility in a state,
other than Illinois, which has been authorized by
USEPA pursuant to 40
CFR
271, but which has not
yet obtained authorization to regulate that waste
as hazardous, then the designated facility must be
a facility allowed by the receiving state to
accept such waste.
“Dike” means an embankment or ridge of either natural
or manmade materials used to prevent the movement of
liquids, sludges, solids or other materials.
“Director” means the Director of
the
Illinois
Environmental
Protection
Agency.
“Discharge” or “hazardous waste discharge” means
the
accidental or intentional spilling,
leaking, pumping,
pouring,
emitting, emptying or dumping of hazardous
waste into or on any land or water.
“Disposal” means the discharge, deposit,
injection,
dumping,
spilling,
leaking
or placing of any solid
waste or hazardous waste into or on any land or water
so that such solid waste or hazardous waste or any
0136-0569
38
constituent thereof may enter the environment or be
emitted
into
the
air or discharged into any waters,
including
groundwaters.
“Qisposal facility” means a facility or part of a
facility at which hazardous.
waste
i.e intentionally
placed into or on any land or water and at which waste
will
remain
after
closure.
“Drip pad” means an engineered structure consisting of
a curbed, free—draining base, constructed of non-
earthen materials and designed to convey preservative
kick-back
or
drippage
from
treated
wood,
precipitation
and surface water run—on to an associated collection
system
at
wood
preserving
plants.
“Elementary
neutralization
unit”
means
a device which:
Is used for neutralizing wastes which are
hazardous only because they exhibit the
corrosivity characteristic defined in 35 Ill. Ada.
Code 721.122 or are listed in 35 Ill. Ada. Code
721.Subpart D only for this reason; and
Meets the definition of tank, ‘tank system,
container, transport vehicle or vessel in this
Section.
“EPA” or “USEPA
“
means United States Environmental
Protection Agency.
“EPA
hazardous
waste
number”
or
“USEPA
hazardous
waste
number” means the number assigned by EPA to each
hazardous waste listed in 35 Ill. Ada. Code 721.Subpart
D and to each characteristic identified in 35 Ill.
Ada.
Code 721.Subpart C.
“EPA
identification
number”
or “USEPA identification
number”
means the number assigned by USEPA pursuant to
35 Ill.
Ada. Code 722 through 725 to each generator,
transporter and treatment,
storage or disposal
facility.
“EPA region” means the states and territories found in
any one of the following ten regions:
Region
I:
Maine, Vermont, New Hampshire,
Massachusetts, Connecticut and Rhode Island
Region
II:
New
York,
New
Jersey,
Commonwealth
of
Puerto Rico and the U.S. Virgin Islands
0136-0570
39
Region
III:
Pennsylvania,
Delaware,
Maryland,
West
Virginia,
Virginia
and
the
District
of
Columbia
Region IV:
Kentucky, Tennessee, North Carolina,
Xississippi, Alabama~Georgia,. .South.Carolina and
Florida
Region V:
Minnesota, Wisconsin,
Illinois,
Michigan, Indiana and Ohio
Region VI:
New Mexico, Oklahoma, Arkansas,
Louisiana
and
Texas
Region VII:
Nebraska,
Kansas,
Missouri
and
Iowa
Region VIII:
Montana, Wyoming, North Dakota,
South Dakota, Utah and Colorado
Region IX:
California, Nevada,
Arizona, Hawaii,
Guam, American Samoa and Commonwealth of the
Northern Mariana Islands
Region X:
Washington, Oregon,
Idaho and Alaska
“Equivalent method” means any testing or analytical
method approved by the Board pursuant to Section
720.120.
“Existing hazardous waste management
(HWM)
facility” or
“existing facility” means a facility which was in
operation or for which construction commenced on or
before November 19,
1980.
A facility had commenced
construction if the owner or operator had obtained the
federal, state and local approvals or permits necessary
to begin physical construction and either:
A continuous on-site, physical construction
program had
begun
or
The owner or operator had entered into contractual
obligations
--
which could not be cancelled or
modified without substantial loss
--
for
physical
construction of the facility to be completed
within a reasonable time.
“Existing portion” means that land surface area of an
existing waste management unit,
included in the
original Part A permit application, on which wastes
have been placed prior to the issuance of a permit.
“Existing
tank
system”
or
“existing
component”
means
a
0136-0571
40
tank
system
or
component that is used for the storage
or treatment of hazardous waste and that is in
operation,
or for which installation has commenced on
or prior to July 14,
1986.
Installation will be
considered to have commenced if the owner or operator
has
obtain,,,ed all federal,,~,Stateand local approvals ,or
permits necessary to begin physical construction of the
site or installation of the tank system and if either
A continuous on—site physical construction or
installation
program
has begun; or
The owner or operator has entered into contractual
obligations
——
which cannot be canceled or
modified without substantial loss
--
for physical
construction
of
the
site
or
installation
of
the
tank
system
to
be
completed
within
a
reasonable
time.
“Facility”
means
all
contiguous
land
and
structures,
other appurtenances and improvements on the land used
for
treating,
storing
or disposing of hazardous waste.
A facility may consist of several treatment, storage or
disposal operational units
(e.g.,
one or more
landfills, surface impoundments or combinations of
them).
“Final closure” means the closure of all hazardous
waste management units at the facility in accordance
with all applicable closure requirements so that
hazardous waste management activities under 35 Ill.
Ada. Code 724 and 725 are no longer conducted at the
facility unless subject to the provisions of 35 Ill.
Ada. Code 722.134.
“Federal agency” means any department,
agency or other
instrumentality of the federal government, any
independent agency or establishment of the federal
government including any government corporation and the
Government Printing Office.
“Federal, state and local approvals or permits
necessary to begin physical construction” means permits
and approvals required under federal,
state or local
hazardous waste control statutes, regulations or
ordinances.
“Food—chain crops” means tobacco,
crops grown for human
consumption and crops grown for feed for animals whose
products are consumed by humans.
“Freeboard” means the vertical distance between the top
0136-0572
41
of
a
tank
or
surface
impoundment
dike
and
the
surface
of
the
waste contained therein.
“Free liquids” means liquids which readily separate
from the solid portion of a waste under ambient
temperature and pressure..
“Generator” means any person, by site, whose act or
process produce hazardous waste identified or listed in
35
Ill.
Ada.
Code
721
or
whose
act
first
causes
a
hazardous waste to become subject to regulation.
“Groundwater” means water below the land surface in a
zone of saturation.
“Hazardous
waste”
means
a
hazardous
waste
as
defined
in
35
Ill.
Ada.
Code
721.103.
“Hazardous waste constituent” means a constituent which
caused the hazardous waste to be listed in 35 Ill. Ada.
Code 721.Subpart D, or a constituent listed in of 35
Ill. Ada. Code 721.124.
“Hazardous waste management unit”
is a contiguous area
of land on or in which hazardous waste is placed,
or
the largest area in which there is significant
likelihood of mixing hazardous waste constituents in
the same area.
Examples of hazardous waste management
units include a surface impoundment, a waste pile, a
land treatment area,
a landfill cell, ‘an incinerator,
a
tank and its associated piping and underlying
containment system and a container storage area.
A
container alone does not constitute a unit; the unit
includes containers and the land or pad upon which they
are placed.
“Inactive portion” means that portion of a facility
which is not operated after November 19,
1980.
(See
also “active portion” and “closed portion”.)
“Incinerator” means any enclosed device that:
Uses controlled flame combustion and neither:
Meets the criteria for classification as a
boiler, sludge dryer or carbon regeneration
unit, nor
Is listed as an industrial furnace;
or
Meets the definition of infrared incinerator or
plasma arc incinerator.
UI 36-0573
42
“Incompatible
waste”
means
a
hazardous
waste
which
is
suitable
for:
Placement in a particular device or facility
because it may cause corrosion or decay of
containment .materials..(e.g., container inner
liners
or
tank
walls);
or
Commingling with another waste or material under
uncontrolled conditions because the commingling
might produce heat or pressure, fire or explosion,
violent reaction, toxic dusts, mists,
fumes or
gases or flammable fumes or gases.
(See 35 Ill.
Ada. Code 725.Appendix E for
examples.)
“Industrial furnace” means any of the following
enclosed devices that are integral components of
manufacturing processes and that use thermal treatment
to accomplish recovery of materials or energy:
Cement kilns
Lime kilns
Aggregate kilns
Phosphate kilns
Coke ovens
Blast
furnaces
Smelting,
melting and refining furnaces
(including
pyrometallurgical devices such as cupolas,
reverberator furnaces, sintering machines,
roasters and foundry furnaces)
Titanium dioxide chloride process oxidation
reactors
Methane reforming furnaces
Pulping liquor recovery furnaces
Combustion devices used in the recovery of sulfur
values from spent sulfuric acid
Halogen acid furnaces (HAFs)
for the production of
acid from halogenated hazardous waste generated by
chemical production facilities where the furnace
UI 36-05Th
43
is located
on
the
site
of
a
chemical
production
facility, the acid product has a halogen acid
content of at least 3,
the acid product is used
in a manufacturing process and, except for
hazardous waste burned as fuel, hazardous waste
fed to the furnace has a minimum
ial’ogen content
of 20,
as generated.
Any
other such device as the Agency determines to
be an “Industrial Furnace” on the basis of one or
more of the following factors:
The design and use of the device primarily to
accomplish recovery of material products;
The use of the device to burn or reduce raw
materials to make a material product;
The use, of the device to burn or reduce
secondary materials as effective substitutes
for raw materials,
in processes using raw
materials
as
principal
feedstocks;
The
use
of
the device to burn or reduce
secondary materials as ingredients in an
industrial
process
to
make
a
material
product;
The
use
of
the device in common industrial
practice to produce a material product; and
Other
relevant
factors.
“Individual generation site” means the contiguous site
at or on which one or more hazardous wastes are
generated.
An individual generation site, such as a
large manufacturing plant, may have one or more sources
of hazardous waste but is considered a single or
individual generation site if the site or property is
contiguous.
“Infrared incinerator” means any enclosed device which
uses electric powered resistance heaters as a source of
radiant heat and which is not listed as an industrial
furnace.
“Inground tank” means a device meeting the definition
of “tank” whereby a portion of
the
tank wall is
situated to any degree within the ground, thereby
preventing visual inspection of that external surface
area of the tank that is in the ground.
0136-0575
44
“In operation” refers to a facility which is treating,
storing or disposing of hazardous waste.
“Injection well” means a well into which fluids are
being injected.
(See also “underground injection”.)
“Inner liner” means a continuous layer of’ material
placed inside a tank or container which protects the
construction materials of the tank or container from
the contained waste or reagents used to treat the
waste.
“Installation inspector” means a person who, by reason
of knowledge of the physical sciences and
the
principles of engineering, acquired by a professional
education and related practical experience,
is
qualified to supervise the installation of tank
systems.
“International shipment” means the transportation of
hazardous waste into or out of the jurisdiction of the
United
States.
“Land
treatment
facility” means a facility or part of a
facility at which hazardous waste is applied onto or
incorporated into the soil surface; such facilities are
disposal facilities if the waste will remain after
closure.
“Landfill” means a disposal facility or part of a
facility where hazardous waste is placed in or on land
and which is not a pile,
a land treatment facility, a
surface impoundment, an underground injection well,
a
salt dome formation, an underground mine or a cave.
“Landfill cell” means a discrete volume of a hazardous
waste landfill which uses a liner to provide isolation
of wastes from adjacent cells or wastes.
Examples of
landfill cells are trenches and pits.
“laDS” means leak detection system.
“Leachate” means any liquid, including any suspended
components in the liquid, that has percolated through
or drained from hazardous waste.
“Liner”
means
a
continuous
layer
of
natural
or
manmade
materials beneath or on the sides of a surface
impoundment, landfill or landfill cell, which restricts
the downward or lateral escape of hazardous waste,
hazardous waste constituents or leachate.
0136-0576
45
“Leak—detection
system”
means
a
system
capable
of
detecting the failure of either the primary or
secondary containment structure or the presence of a
release of hazardous waste or accumulated liquid in the
secondary containment structure.
Such a system must
employ operational controls
(e.g.
.,.
daily
visual
inspections for releases into the secondary containment
system of aboveground
tanks)
or
consist
of
an
interstitial monitoring device designed to detect
continuously and automatically the failure of the
primary or secondary containment structure or the
presence of a release of hazardous waste into the
secondary containment structure.
“Management” or “hazardous waste management” means the
systematic
control
of
the
collection,
source
separation, storage, transportation,
processing,
treatment, recovery and disposal of hazardous waste.
“Manifest” means the shipping document originated and
signed by the generator which contains the information
required by 35 Ill. Ada. Code 722.Subpart B.
“Manifest document number” means the USEPA twelve digit
identification number assigned to the generator plus a
unique five digit document number assigned to the
manifest by the generator for recording and reporting
purposes.
“Mining overburden returned to the mine site” means any
material overlying an economic mineral deposit which is
removed to gain access to that deposit and is then used
for reclamation of a surface mine.
“Miscellaneous unit” means a hazardous waste management
unit where hazardous waste is treated, stored or
disposed of and which is not a container,
tank, tank
system, surface impoundment, pile,
land treatment unit,
landfill, incinerator, boiler, industrial furnace,
underground injection well with appropriate technical
standards under 35
Ill. Ada. Code 730, or a unit
eligible for a research, development and demonstration
permit under 35 Ill. Ada. Code 703.231.
“Movement” means that hazardous waste transported to a
facility
in
an
individual
vehicle.
“New hazardous waste management facility” or “new
facility” means a
facility
which
began
operation,
or
for which construction commenced,
after November 19,
1980.
(See also “Existing hazardous waste management
facility”.)
0136-0577
46
“New tank system” or “new tank component” means
a
tank
system or component that will be used for the storage
or treatment of hazardous waste and for which
installation
commenced after July 14,
1986; except,
however, for purposes of
35
Ill.
Ada.
Code
724.293 (g) (2,) and 725.29.3(g) (2), a nevtank system is
one for which construction commences after July 14,
1986.
(See also “existing tank system.”)
“Onground tank” means a device meeting
the
definition
of “tank” that is situated in such a way that the
bottom of the tank is on
the
same level as the adjacent
surrounding surfaces so that the external tank bottom
cannot be visually inspected.
“On—site” means the same or geographically contiguous
property which may be divided by public or private
right—of—way, provided the entrance and exit between
the properties is at a crossroads intersection and
access is by crossing as opposed to going along the
right-of-way.
Noncontiguous properties owned by the
same person but connected by a right—of—way which he
controls and to which the public does not have access
is also considered on—site property.
“Open burning” means the combustion of ‘any material
without the following characteristics:
Control of combustion air to maintain adequate
temperature for efficient combustion;
Containment of the combustion reaction in an
enclosed device to provide sufficient residence
time and mixing for complete combustion; and
Control of emission of the gaseous combustion
products.
(See also “incineration” and “thermal treatment”.)
“Operator” means the person responsible for the overall
operation of a facility.
“Owner” means the person who owns a facility or part of
a facility.
“Partial closure” means
the
closure
of
a
hazardous
waste management unit in accordance with the applicable
closure
requirements
of
35
Ill.
Ada.
Code
724
or
725
at
a
facility
which
contains
other
active hazardous waste
management
units.
For
example,
partial
closure
may
include
the
closure
of
a tank (including its associated
0136-0578
47
piping
and
underlying
containment
systems),
landfill
cell,
surface
impoundment,
waste
pile
or
other
hazardous waste management unit, while other units of
the same facility continue to operate.
“Person” means an individual, trust,
.firm~,.~~.joint
stock.
company,
federal agency, corporation (including a
government corporation), partnership, association,
state, municipality, commission,
political subdivision
of a state or any interstate body.
“Personnel” or “facility personnel” means all persons
who work at or oversee the operations of a hazardous
waste facility and whose actions or failure to act may
result in noncompliance with the requirements of 35
Ill. Ada. Code 724 or 725.
“Pile” means any noncontainerized accumulation of
solid,
non—flowing
hazardous waste that is used for
treatment
or
storage.
“Plasma arc incinerator” means any enclosed device
which uses a high intensity electrical discharge or arc
as a source of heat and which is not listed as an
industrial furnace.
“Point source” means any discernible, confined and
discrete conveyance including, but not limited to, any
pipe, ditch, channel, tunnel,
conduit, well,
discrete
fissure, container, rolling stock, concentrated animal
feeding operation or vessel or other floating craft
from which pollutants are or may be discharged.
This
term does not include return flows from irrigated
agriculture.
“Publicly owned treatment works” or “POTW” is as
defined in 35 Ill. Ada. Code 310.110.
“Qualified aroundwater scientist” means a scientist or
enaineer who has received a baccalaureate or oost-
graduate
degree
in
the
natural
sciences
or
engineerina.
and has sufficient training and experience in
aroundwater
hydroloav and related fields. as
demonstrated by state reaistration. professional
certifications or completion of accredited university
courses that enable the individual to make sound
professional
ludaments
regarding
aroundwater
monitoring
and contaminant fate and transport.
BOARD
NOTE:
“State registration” includes, but is
not limited to. registration as a Drofessiona.
enaineer
with the DeDartment of Professional
0136-0579
48
Regulation.
pursuant
to
Ill.
Rev. Stat.
1991.
ch.
111. par.
5201 and 68
Ill.
Ada. Code 1380.
“Professional certification” includes, but is not
limited to, certification under the certified
around water professional
proaram
of the National
Ground Water Association.
“Regional Administrator” means the Regional
Administrator for the EPA Region in which the facility
is located or the Regional Administrator’s designee.
“Representative sample” means a sample of a universe or
whole
(e.g., waste pile,
lagoon, groundwater) which can
be expected to exhibit the average properties of the
universe
or
whole.
“ReDlacement
unit”
means
a
landfill,
surface
impoundment
or waste pile unit from which all or
substantially all of the waste is removed, and which is
subse~entlyreused 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 Dlan apDroved by USEPA or
the Aaency.
“Runoff” means any rainwater,
leachate or other liquid
that drains over land from any part of a facility.
“Runon” means any rainwater,
leachate or other liquid
that drains over land onto any part of a facility.
“Saturated zone” or “zone of saturation” means that
part of the earth’s crust in which all voids are filled
with water.
“SIC Code” means Standard Industrial Code as defined in
Standard Industrial Classification Manual, incorporated
by reference in Section 720.111.
“Sludge” means any solid, semi—solid or liquid waste
generated from a municipal, commercial or industrial
wastewater treatment plant, water supply treatment
plant
or
air pollution control facility exclusive of
the treated effluent from a wastewater treatment plant.
“Sludge dryer” means any enclosed thermal treatment
device which is used to dehydrate sludge and which has
a total thermal input, excluding the heating value of
the sludge itself, of 2500 Btu/lb or less of sludge
0136-0580
49
treated on a wet weight basis.
“Small Quantity Generator” means a generator which
generates less than 1000 kg of hazardous waste in a
calendar month.
“Solid
waste”
means
a
solid
waste
as
defined
in
35
Ill.
Ada. Code
721.102.
“Sump” means any pit or reservoir that meets the
definition of tank and those troughs or trenches
connected to it that serve to collect hazardous waste
for transport to hazardous waste storage, treatment or
disposal facilities; except that,
as used in the
landfill. surface impoundment and waste nile rules,
“sum~” means
any
lined
Dit
or reservoir that serves to
collect
liquids
drained
from a leachate collection and
removal system or leak detection system for subseauent
removal from the system.
“State” means any of the several states, the District
of Columbia, the Commonwealth ‘of Puerto Rico, the
Virgin Islands, Guam, American Samoa and the
Commonwealth of the Northern Mariana Islands.
“Storage” means the holding of hazardous waste for a
temporary period, at the end of which the hazardous
waste is treated, disposed of or stored elsewhere.
“Surface impoundment” or “impoundment” means a facility
or part of a facility which is a natural topographic
depression,
manmade
excavation
or
diked
area
formed
primarily of earthen materials (although it may be
lined with manmade materials) which is designed to hold
an accumulation of liquid wastes or wastes containing
free liquids and which is not an injection well.
Examples of surface impoundments are holding, storage,
settling
and
aeration
pits,
ponds
and
lagoons.
“Tank” means a stationary device, designed to contain
an accumulation of hazardous waste which is constructed
primarily of nonearthen materials
(e.g., wood,
concrete,
steel, plastic) which provide structural
support.
“Tank system” means a hazardous waste storage or
treatment tank and its associated ancillary equipment
and containment system.
“Thermal treatment” means the treatment of hazardous
waste
in
a
device
which
uses
elevated temperature’s as
the primary means to change the chemical, physical or
0136-0581
50
biological character or composition of the hazardous
waste.
Examples of thermal treatment processes are
incineration, molten salt, pyrolysis,
calcination, wet
air oxidation and microwave discharge.
(See also
“incinerator” and “open burnina”.)
“Totally enclosed treatment facility” means a facility
for the treatment of hazardous waste which is directly
connected
to
an
industrial
production
process
and
which
is constructed and operated in a manner
which
prevents
the release of any hazardous waste or any constituent
thereof into the environment during treatment.
An
example
is
a
pipe
in
which
waste
acid
is
neutralized.
“Transfer
facility”
means
any transportation related
facility
including
loading
docks,
parking
areas,
storage areas and other similar areas where shipments
of hazardous waste are held during the normal course of
transportation.
“Transport
vehicle”
means
a
motor
vehicle
or
rail
car
used for the transportation of cargo by any mode.
Each
cargo-carrying
body
(trailer, railroad freight car,
etc.)
is
a
separate
transport
vehicle.
“Transportation” means the movement of hazardous waste
by air,
rail, highway or water.
“Transporter”
means
a
person
engaged
in the off-site
transportation
of hazardous waste by air, rail,
highway
or
water.
“Treatability study” means:
A
study
in
which
a
hazardous
waste
is
subjected
to
a treatment process to determine:
Whether the waste is amenable to
the
treatment
process.
What
pretreatment
(if
any)
is
required.
The
optimal
process
conditions
needed
to
achieve the desired treatment.
The efficiency of a treatment process for a
specific waste or wastes.
Or,
The characteristics and volumes of residuals
from a particular treatment process.
Also
included
in
this
definition
for
the
purpose
0136-0582
51
of
35 Ill. Ada. Code
721.104(e)
and
(f)
exemptions
are liner compatibility, corrosion and other
material compatibility studies and toxicological
and health effects studies.
A “treatability
study” is not a means to commercially treat or
dispose of hazardous. waste.
“Treatment” means any method, technique or process,
including neutralization, designed to change the
physical, chemical or biological character or
composition of any hazardous waste so as to neutralize
such waste, or so as to recover energy or material
resources from the waste or so as to render such waste
non—hazardous or less hazardous; safer to transport,
store or dispose of; or amenable for recovery, amenable
for storage or reduced in volume.
“Treatment zone” means a soil area of the unsaturated
zone of a land treatment unit within which hazardous
constituents are degraded, transformed or immobilized.
“Underground injection” means the subsurface
emplacement of fluids through a bored, drilled or
driven
well;
or
through
a
dug
well,
where
the
depth
of
the dug well is greater than the largest surface
dimension.
(See also “injection well”.)
“Underground
tank”
means
a
device
meeting
the
definition of “tank” whose entire surface area is
totally
below
the
surface
of
and
covered
by the ground.
“Unfit—for—use tank system” means a tank system that
has been determined through an integrity assessment or
other
inspection
to
be
no
longer
capable
of
storing
or
treating hazardous waste without posing a threat of
release of hazardous waste to the environment.
“Uppermost aquifer” means the geologic formation
nearest the natural ground surface that is an aquifer,
as well as lower aquifers that are hydraulically
interconnected with this aquifer within the facility’s
property boundary.
“United States” means the 50 States,
the
District
of
Columbia, the Commonwealth of
Puerto
Rico, the U.S.
Virgin
Islands,
Guam,
American
Samoa
and
the
Commonwealth
of
the
Northern
Mariana
Islands.
“Unsaturated zone” or “zone of aeration” means the zone
between
the
land
surface
and the water table.
“USEPA”
means
United
States
Environmental
Protection
0 136-0583
52
Agency.
“Vessel” includes every description of watercraft, used
or capable of being used as a means of transportation
on the water.
“Wastewater treatment unit” means a device which:
Is part of a wastewater treatment facility which
has an NPDES permit pursuant to 35 Ill. Ada. Code
309 or a pretreatment permit or authorization to
discharge pursuant to 35 Ill. Ada. Code 310; and
Receives and treats or stores an influent
wastewater which is a hazardous waste as defined
in 35 Ill. Ada. Code 721.103,
or generates and
accumulates a wastewater treatment sludge which is
a hazardous waste as defined in 35 Ill. Ada. Code
721.103, or treats or stores a wastewater
treatment
sludge
which
is
a
hazardous
waste
as
defined
in
35
Ill.
Ada.
Code
721.103;
and
Meets
the
definition
of
tank
or
tank
system
in
this
Section.
“Water
(bulk
shipment)”
means the bulk transportation
of hazardous waste which is loaded or carried on board
a vessel without containers or labels.
“Well” means any shaft or pit dug or bored into the
earth, generally of a cylindrical form, and often
walled
with
bricks
or
tubing to prevent the earth from
caving in.
“Well
injection”
(See
“underground
injection”).
“Zone of engineering control” means an area under the
control of the owner or operator that, upon detection
of a hazardous waste release, can be readily cleaned up
prior to the release of hazardous waste or hazardous
constituents to groundwater or surface water.
(Source:
Amended at 16 Ill. Reg.
,
effective
)
01 36_Q55t4
53
TITLE
35:
ENVIRONMENTAL
PROTECTION
SUBTITLE G:
WASTE
DISPOSAL
CHAPTER
I:
POLLUTION
CONTROL BOARD
SUBCHAPTER c:
HAZARDOUS
WASTE
OPERATING
REQUIREMENTS
PART
721
IDENTIFICATION
AND
LISTING OF HAZARDOUS WASTE
Section
721.
101
721.
102
721.
103
721. 104
721.
105
721.
106
721.
107
721. 108
SUBPART
A:
GENERAL PROVISIONS
Purpose and Scope
Definition
of
Solid
Waste
Definition of Hazardous Waste
Exclusions
Special Requirements for Hazardous Waste Generated by
Small
Quantity
Generators
Requirements for Recyclable Materials
Residues
of
Hazardous
Waste
in Empty Containers
PCB
Wastes
Regulated
under
TSCA
SUBPART
B:
CRITERIA
FOR
IDENTIFYING
THE CHARACTERISTICS
OF
HAZARDOUS
WASTE
AND
FOR
LISTING
HAZARDOUS
WASTES
Section
721.110
Criteria
for
Identifying
the
Characteristics
of
Hazardous Waste
721.111
Criteria for Listing Hazardous Waste
Section
721.120
721.
121
721.
122
721.123
721.
124
Section
721.
130
721.
131
721.132
721.133
SUBPART
C:
CHARACTERISTICS
OF
HAZARDOUS
WASTE
General
Characteristic of Ignitability
Characteristic of Corrosivity
Characteristic of Reactivity
Toxicity Characteristic
SUBPART
D:
LISTS
OF
HAZARDOUS
WASTE
General
Hazardous Wastes From Nonspecific Sources
Hazardous Waste from Specific Sources
Discarded Commercial Chemical Products,
Off-
Specification Species, Container Residues and Spill
Residues Thereof
721.135
Wood Preserving Wastes
721.Appendix A Representative Sampling Methods
721.Appendix B Method 1311 Toxicity Characteristic Leaching
Procedure (TCLP)
C Chemical Analysis Test Methods
Analytical Characteristics of Organic Chemicals
(Repealed)
Table B
Analytical Characteristics of Inorganic Species
721. Appendix
Table
A
0 136-0585
54
(Repealed)
Table
C
Sample
Preparation/Sample
Introduction
Techniques
(Repealed)
721.Appendix G Basis for Listing Hazardous Wastes
721.Appendix H Hazardous Constituents
721.Appendix I Wastes. Excluded..under Section 720.120...and .720.122
Table A
Wastes Excluded from Non—Specific Sources
Table B
Wastes Excluded from Specific Sources
Table C
Wastes Excluded From Commercial Chemical Products,
Off-Specification Species, Container Residues, and
Soil Residues Thereof
Table D
Wastes Excluded by Adjusted Standard
72l.Appendix J Method of Analysis for Chlorinated Dibenzo-p-
Dioxins and Dibenzofuraris
721.Appendix
Z Table to Section 721.102
AUTHORITY:
Implementing
Section
22.4 and authorized by Section
27 of the Environmental Protection Act
(Ill. Rev.
Stat.
1991,
ch.
111½, pars.
1022.4
and
1027).
SOURCE:
Adopted
in
R81-22,
43
PCB
427,
‘at
5 Ill. Reg.
9781,
effective as noted in 35 Ill. Ada. Code 700.106; amended and
codified in R81—22, 45 PCB 317, at 6 Ill. Reg.
4828, effective as
noted in 35 Ill.
Ada. Code 700.106; amended in R82-18,
51 PCB 31,
at 7
Ill.
Reg. 2518,
effective February 22,
1983; amended in R82-
19,
53 PCB 131, at 7 Ill. Reg. 13999, effective October 12,
1983;
amended in R84—34,
61 PCB 247, at 8 Ill. Reg.
24562,
effective
December 11,
1984; amended in R84-9,
at 9 Ill. Reg.
11834,
effective July 24,
1985; amended in R85—22 at 10 Ill. Reg. 998,
effective January
2,
1986;
amended in R85-2 at 10 Ill. Reg. 8112,
effective May 2,
1986; amended in R86—1 at 10 Ill.
Reg.
14002,
effective August 12,
1986;
amended in R86—19 at 10 Ill.
Reg.
20647, effective December 2,
1986; amended in R86-28 at 11 Ill.
Reg.
6035, effective March 24,
1987; amended in R86—46 at 11 Ill.
Reg.
13466,
effective August 4,
1987; amended in R87-32 at 11
Ill.
Reg.
16698,.
effective
September
30,
1987;
amended
in
R87-5
at
11
Ill.
Reg.
19303,
effective
November
12,
1987;
amended
in
R87—26
at
12
Ill.
Reg.
2456,
effective
January
15,
1988;
amended
in R87—30 at 12
Ill.
Reg. 12070, effective July 12,
1988; amended
in
R87—39
at
12
Ill.
Reg.
13006,
effective
July
29,
1988;
amended
in R88—16 at 13 Ill. Reg.
382, effective December 27,
1988;
amended in R89—1 at 13 Ill. Reg. 18300, effective November 13,
1989; amended in R90—2 at 14 Ill. Reg.
14401, effective August
22,
1990;
amended
in
R90—10
at
14
Ill.
Reg.
16472,
effective
September 25,
1990; amended in R90—17 at 15 Ill. Reg. 7950,
effective May 9,
1991; amended in R90—11 at 15 Ill. Reg. 9332,
effective June 17,
1991; amended in R91—1 at 15 Ill. Reg.
14473,
effective September 30,
1991;
amended in R91—12 at 16 Ill. Reg.
2155, effective January 27,
1992;
amended in R91—26 at 16 Ill.
Reg. 2600, effective February 3,
1992;
amended
in
R91-13
at
16
Ill. Reg.
9519, effective June 9,
1992;
amended in R92—1 at 16
Ill.
Reg.
,
effective
;
amended
in
R92—10
0136-0586
55
at 16 Ill. Reg.
,
effective
SUBPART A:
GENERAL
PROVISIONS
Section
721.103
Definition
of
Hazardous
Waste
a)
A solid waste, as defined in Section 721.102,
is a
I~iazardous waste
if:
1)
It is not excluded from regulation as a hazardous
waste under Section 721.104(b); and
2)
It meets any of the following criteria,-~
A)
It exhibits any of the characteristics of
hazardous waste identified in Subpart
C.
Except that any mixture of a waste from the
extraction, beneficiation or processing of
ores
or
minerals
excluded
under
Section
721.104(b) (7) and any other solid waste
exhibiting a characteristic of hazardous
waste under Subpart C is a hazardous waste
only:
if
it
exhibits
a
characteristic
that
would
not
have
been
exhibited by the excluded
waste alone if such mixture had not occurred;
or,
if it continues to exhibit any of the
characteristics exhibited by the non-excluded
wastes prior to mixture.
Further,
for the
purposes of applying the EP toxicity
(cxtraotion
prooedurc
toxicity)
toxicity
characteristic, characteristic to such
mixtures, the mixture is also a hazardous
waste:
if it exceeds the maximum
concentration for any contaminant listed in
Section 721.124 that would not have been
exceeded by the excluded waste alone if the
mixture had not occurred; or,
if it continues
to exceed the maximum concentration for any
contaminant
exceeded
by
the
nonexempt
waste
prior to mixture.
B)
It is listed in Subpart D and has not been
excluded from the lists in Subpart D under 35
Ill.
Ada.
Code
720.120
and
720.122.
C)
It is a mixture of a solid waste and a
hazardous waste that is listed in Subpart D
solely because it exhibits one or more of the
characteristics of hazardous waste identified
in Subpart C, unless the resultant mixture no
longer exhibits any characteristic of
hazardous waste identified in Subpart C, or
0136 -0587
56
unless
the
solid
waste:
is excluded from
regulation under Section 721.104(b) (7); and,
the resultant mixture no longer exhibits any
characteristic of hazardous waste identified
in Subpart C for which the hazardous waste
.listed in
Subpart
D
was
listed.
D)
It is a mixture of solid waste and one or
more hazardous wastes listed in Subpart D and
has not been excluded from this paragraph
this subsection (a~(2~under 35 Ill. Ada.
Code 720.120 and 720.122; however, the
following mixtures of solid wastes and
hazardous wastes listed in Subpart D are not
hazardous wastes (except by application of
subsection
(a) (2) (A) or
(B), above)
if the
generator can demonstrates that the mixture
consists of wastewater the discharge of which
is subject to regulation under either 35 Ill.
Ada. Code 309 or 310
(including wastewater at
facilities which have eliminated the
discharge of wastewater) andt~
i)
One
or
more
of the following apcnt
solvents listed in Section 721.131
-
carbon tetrachloride, tetrachioro
cthylcnetetrachloroethvlene,
trichloroethylene
-
provided that the
maximum total weekly usage of these
solvents (other than the amounts that
can be demonstrated not to be discharged
to wastewater) divided by the average
weekly flow of wastewater into ‘the
headworks of the facility’s wastewater
treatment or prc-trcatmcnt pretreatment
system does not exceed 1 part per
million; or
ii)
One or more of the following spent
solvents listed in Section 721.131
—
methylene chloride,
1,1,1
-
trichloroethane, chlorobenzene,
o—dichlorobenzene, cresols, cresylic
acid, nitrobenzene, toluene, methyl
ethyl ketone, carbon disulfide,
isobutanol, pyridine, spent ohloro
fluorocarbon chlorofluorocarbon solvents
-
provided that th’e maximum total weekly
usage of these solvents (other than the
amounts that can be demonstrated not to
be discharged to wastewater) divided by
the average weekly flow of wastewater
0136-0588
57
into the headworks of the facility’s
wastewater treatment or prc—trcatmcnt
pretreatment system does not exceed 25
parts per million; or
iii)
One of the .following wastes..listed in
Section 721.132
-
heat exchanger bundle
cleaning sludge from the petroleum
refining industry (EPA Hazardous Waste
No. K050); or
iv)
A
~
chemical product, or chemical
intermediate
listed
in
Section
721.133,
arising from de minimis losses of these
materials
from
manufacturing
operations
in
which
these
materials
are
used
as
raw
materials
or
are
produced
in
the
manufacturing
process.
For
purposes
of
this subsection,
“de minimis” losses
include
those
from normal material
handling operations
(e.g.,
spills from
the unloading or transfer of materials
from
bins
or
other
containers,
leaks
from pipes, valves or other devices used
to transfer materials); minor leaks of
process equipment, storage tanks or
containers;
leaks
from
well—maintained
pump packings and seals; sample
purgings; relief device discharges;
discharges from safety showers and
rinsing and cleaning of personal safety
equipment; and rinsate from empty
containers or from containers that are
rendered empty by that rinsing; or
v)
Wastewater resulting from laboratory
operations
containing
toxic
(T)
wastes
listed in Subpart D, provided that the
annualized average flow of laboratory
wastewater does not exceed one percent
of total wastewater flow into the
headworks of
the
facility’s wastewater
treatment or pro-treatment pretreatment
system, or provided that the wastes
combined annualized average
concentration does not exceed one part
per million in the headworks of the
facility’s
wastewater
treatment
or
prc-trcntmcnt
pretreatment
facility.
Toxic
(T)
wastes
used
in
laboratories
that are demonstrated not to be
0136-0589
58
discharged to wastewater are not to be
included in this calculation.
b)
A
solid
waste
which
is
not
excluded
from
regulation
under
subsection
(a)
(1),
above,
becomes
a
hazardous
waste when any of the following events occur:
1)
In the case of a waste listed in Subpart D, when
the waste first meets the listing description set
forth in Subpart D.
2)
In the case of a mixture of solid waste and one or
more listed hazardous wastes, when a hazardous
waste listed in Subpart D is first added to the
solid waste.
3)
In
the
case
of
any
other
waste
(including
a
waste
mixture), when the waste exhibits any of the
characteristics
identified
in
Subpart
C.
c)
Unless
and
until
it
meets
the
criteria
of
subsection
(d),
below:
1)
A
hazardous
waste
will
remain
a
hazardous
waste.
2)
Specific inclusions and exclusions~
A)
Except as otherwise provided in subsection
(c) (2) (B), below, any solid waste generated
from the treatment,
storage or disposal of a
hazardous waste,
including any sludge, spill
residue, ash, emission control dust or
leachate
(but not including precipitation
run—off),
is a hazardous waste.
(However,
materials that are reclaimed from solid
wastes and that are used beneficially are not
solid wastes and hence are not, hazardous
wastes under this provision unless the
reclaimed material is burned for energy
recovery or used in a manner constituting
disposal.)
B)
The following solid wastes are not hazardous
even though they are generated from the
treatment, storage or disposal of a hazardous
waste, unless they exhibit one or more of the
characteristics of hazardous waste:
i)
Waste pickle liquor sludge generated by
lime stabilization of spent pickle
liquor from the iron and steel industry
(SIC Codes 331 and 332)
(Standard
0136-0590
59
Industrial Codes, as defined and
incorporated by reference in 35 Ill.
Ada. Code 720.110 and 720.111).
ii)
Wastes from burning any of the materials
exempted from regulation by ,Section
721.106(a)(3)(E),
(F),
(G) or
(H).
iii)
Nonwastewater residues, such as slag,
resulting from high temperature metal
recovery (HTMR)
processing of K061
waste, in units identified below, that
are disposed of in non—hazardous waste
units, provided that these residues meet
the generic exclusion levels identified
below for all constituents, and exhibit
no characteristics of hazardous waste.
The types of units are:
rotary kilns,
flame
reactors, electric furnaces,
plasma arc furnaces, slag reactors,
rotary hearth furnace/electric furnace
combinations or the following types of
industrial furnaces (as defined in 35
Ill. Ada. Code 720.110):
blast
furnaces, smelting, melting and refining
furnaces (including pyrometallurgical
devices such as cupolas, reverberator
furnaces,
sintering
machines,
roasters
and
foundry
furnaces),
and
other
furnaces designated by the Agency
pursuant to that definition.
Testing
requirements
must
be
incorporated
in
a
facility’s waste analysis plan or a
generator’ s self—implementing waste
analysis plan;
at a minimum, composite
samples of residues must be collected
and analyzed quarterly and when the
process or operation generating the
waste changes.
The generic exclusion
levels are:
Constituent
Maximum for any single
composite sample
(mg/L)
Antimony....
....
..
0.063
Arsenic......
.
.
.
.
0.055
Barium
.
.
.
.
.
.
.
.
.
.
.
6
.
3
Beryllium
.
.
0.0063
Cadmium
.
.
.
.
.
.
.
.
.
.
0.032
Chromium (total)
0.33
Lead
.
.
.
0
.
095
Mercury
.
.
.
.
.
.
.
.
.
0.009
0136-0591
60
Nickel..
0.63
Selenium.
0.16
Silver
.
.
.
.
.
.
.
.
.
.
.
0.30
Thallium.....
...
.
.
0.013
Vanadium......
.
.
.
.
1.26
For each shipment of K061 HTMR residues
sent to a nonha~ardouswaste management
unit, a notification and certification
must be sent to the Agency
(or, for out-
of-State shipments, to the appropriate
Regional Administrator of USEPA or state
agency authorized to implement 40 CFR
268 requirements).
The notification
must include the following information:
The name and address of the nonhazardous
waste
management
unit
receiving
the
waste shipment;
The USEPA hazardous
waste number and treatability group at
the initial point of generation;
The
treatment
standards
applicable
to
the
waste at the initial point of
generation.
‘The certification must be
signed by an
authorized
representative
and must state as follows:
“I certify under penalty of law that the
generic exclusion levels for all
constituents have been met without
impermissible dilution and that no
characteristic of hazardous waste is
exhibited.
I am aware that there are
significant penalties for submitting a
false certification, including the
possibility of fine and imprisonment.”
d)
Any
solid waste described in subsection
(c), above,
is
not a hazardous waste if it meets the following
criteria:
1)
In the case of any solid waste,
it does not
exhibit
any
of
the
characteristics
of
hazardous
waste identified in Subpart C.
(However, wastes
which exhibit a characteristic at the point of
generation may still be subject to the
requirements
of
35
Ill.
Ada.
Code
728,
even
if
they no longer exhibit a characteristic at the
point
of
land
disposal.)
2)
In
the
case
of
a
waste
which
is
a
listed
waste
under Subpart D,
contains a waste listed under
Subpart
D
or
is
derived
from
a
waste
listed
in
UI 36-0592
61
Subpart
D,
it also has been excluded from
subsection
(c), above, under 35 Ill. Ada. Code
720.120
and
720.122.
Sunset
provision.
Subsections
(al
(21
(Dl
and
(cI
(21
(A)
above
shall
remain
in
effect
only
until
April
28
1993.
(Source:
Amended at 16 Ill. Reg.
,
effective
)
Section 721.104
Exclusions
a)
Materials which are not solid wastes.
The following
materials are not solid wastes for the purpose of this
Part:
1)
Sewage:
A)
Domestic
sewage;
and
B)
Any
mixture
of
domestic
sewage
and
other
waste that passes through a sewer system to
publicly—owned
treatment
works
for
treatment.
“Domestic
sewage”
means
untreated
sanitary
wastes that pass through a sewer system.
2)
Industrial wastewater discharges that are point
source discharges with NPDES permits issued by the
Agency pursuant to Section 12(f) of the
Environmental Protection Act and 35 Ill. Ada. Code
309.
BOARD
NOTE:
This
exclusion
applies only to the
actual point source discharge.
It does not
exclude industrial wastewaters while they are
being collected,
stored or treated before
discharge, nor does it exclude sludges that are
generated by industrial wastewater treatment.
3)
Irrigation return flows.
4)
Source, special nuclear or by—product material as
defined by the Atomic
Energy
Act of 1954,
as
amended
(42
U.S.C.
2011
et
seq.)
5)
Materials subjected to in—situ mining techniques
which are not removed from the ground as part of
the extraction process.
6)
Pulping liquors (i.e., black liquor) that are
reclaimed in a pulping liquor recovery furnace and
then reused in the pulping process, unless
0136-0593
62
accumulated speculatively as defined in Section
721.101(c);
7)
Spent
sulfuric
acid
used
to
.produce
virgin
sulfuric acid,
unless it is accumulated
speculatively as defined in Section 721.101 (,c).
8)
Secondary materials that are reclaimed and
returned to the original process or processes in
which they were generated where they are reused in
the production process, provided:
A)
Only tank storage is involved, and the entire
process through completion of reclamation is
closed by being entirely connected with pipes
or other comparable enclosed means of
conveyance;
B)
Reclamation does not involve controlled’~flame
combustion (such as occurs in boilers,
industrial furnaces or incinerators);
C)
The secondary materials are never accumulated
in such tanks for over twelve months without
being
reclaimed;
and
D)
The
reclaimed
material
is not used to produce
a fuel,
or used to produce products that are
used in a manner constituting disposal.
9)
Wood preserving wastes.
A)
Spent wood preserving solutions that have
been used and are reclaimed and reused for
their original intended purpose;
and
B)
Wastewaters from the wood preserving process
that have been reclaimed and are reused to
treat wood.
10)
When ucod so a fuel, coke
and
ooal tar from the
iron and steel industry that contains or is
produood from decanter tank tar sludge, UCEFA
hasardous i.aato K087.
The process of producing
ookc
and
coal
tar
from
such
dooanter tank tar
oludge in a cake oven is like~ieeexcluded from
reqalation.Hazardous
waste
number
K087. a~dany
wastes from the coke by—products processes which
are hazardous only because they exhibit the
toxicity characteristic specified in Section
721.124. when.
subseauent to generation. these
materials
are recycled to coke ovens, to the tar
01 36-059k
63
recovery process as a feedstock to produce coal
tar or are mixed with coal tar engr to the tar’s
sale or refining.
This exclusion is conditioned
on there being no land diseosal of the wastes from
the point they are aenerated to the point they are
recycled to coke ovens cr
the
tar
refining
process.
11)
Nonwastewater splash condenser dross residue from
the treatment of K061 in high temperature metals
recovery units, provided it is shipped in drums
(if shipped) and not land disposed before
recovery.
b)
Solid
wastes
which are not hazardous wastes.
The
following
solid
wastes are not hazardous wastes:
1)
Household waste,
including household waste that
has been collected, transported, stored,
treated,
disposed, recovered (e.g., refuse—derived fuel) or
reused.
“Household waste” means any waste
material
(including
garbage,
trash and sanitary
wastes in septic tanks) derived from households
(including single and multiple residences, hotels
and motels,
bunkhouses, ranger stations, crew
quarters, campgrounds, picnic grounds and day—use
recreation areas).
A resource recovery facility
managing municipal solid waste shall not be deemed
to be treating, storing, disposing of or otherwise
managing hazardous wastes for the purposes of
regulation under this Part,
if such facility:
A)
Receives and burns only:
i)
Household waste (from single and
multiple dwellings, hotels, motels and
other residential sources) and
ii)
Solid waste from commercial or
industrial sources that does not contain
hazardous waste; and
B)
Such
facility
does not accept hazardous waste
and the owner or operator of such facility
has established contractual requirements or
other appropriate notification or inspection
procedures to assure that hazardous wastes
are not received at or burned in such
facility.
2)
Solid wastes generated by any of the following and
which are returned to the soil as fertilizers:
0 136-0595
64
A)
The growing and harvesting of agricultural
crops.
B)
The raising of animals, including animal
manures.
3)
Mining overburden returned to the mine site.
4)
Fly ash waste,
bottom ash waste, slag waste and
flue gas emission control waste generated
primarily from the combustion of coal or other
fossil fuels, except as provided in 35 Ill. Ada.
Code 726.212 for facilities that burn or process
hazardous waste.
5)
Drilling fluids, produced waters, and other wastes
associated
with
the
exploration,
development,
or
production
of
crude
oil,
natural gas or geothermal
energy.
6)
Chromium
wastes:
A)
Wastes
which
fail
the
test
for
the
toxicity
characteristic
(Section
721.124
and
Appendix
B)
because
chromium
is
present
or are listed
in Subpart D due to the presence of chromium,
which do not fail the test for the toxicity
characteristic for any other constituent or
are not listed due to the presence of any
other constituent, and which do not fail the
test for any other characteristic,
if it is
shown by a waste generator or by waste
generators that:
i)
The chromium in the waste is exclusively
(or nearly exclusively) trivalent
chromium;
and
ii)
The waste is generated from an
industrial process which uses trivalent
chromium exclusively
(or nearly
exclusively) and
the
process does not
generate hexavalent chromium; and
iii) The waste is typically and frequently
managed in non-oxidizing environments.
B)
Specific wastes 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 toxicity, and do not fail
DI 36-0596
65
#he—~eet--#e*--e~ijbjt~anyother
characteristic)
are~
i)
Chrome
(blue) trimmings generated by the
following subcategories of the leather
tanning
and
finishing
industry;
hair
pulp/chrome tan/retan/wet finish; hair
save/chrome tan/retan/wet finish;
retan/wet finish; no beamhouse;
through-
the-blue; and ahearling.
ii)
Chrome
(blue) shavings generated by the
following subcategories of the leather
tanning and finishing industry; hair
pulp/chrome tan/retan/wet finish; hair
save/chrome tan/retan/wet finish;
retan/wet finish; no beamhouse; through-
the-blue; and shearling.
iii)
Buffing
dust generated by the following
subcategories of the leather tanning and
finishing
industry:
hair
pulp/chrome
tan/retan/wet finish; hair save/chrome
tan/retan/wet
finish;
retan/wet
finish;
no
beamhouse;
through-the-blue.
iv)
Sewer
screenings
generated
by
the
following
subcategories
of the leather
tanning and finishing industry;
hair
pulp/chrome tan/retan/wet finish; hair
save/chrome tan/retan/wet finish;
retan/wet finish; no beamhouse; through-
the-blue; and shearling.
v)
Wastewater treatment sludges generated
by the following subcategories of the
leather tanning and finishing industry:
hair pulp/chrome tan/retan/wet finish;
hair save/chrome tan/retan/wet finish;
retan/wet finish; no beazhouse; through-
the—blue; and shearling.
vi)
Wastewater treatment sludges generated
by the following subcategories of
the
leather tanning and finishing industry:
hair pulp/chrome tan/retan/wet finish;
hair save/chrome tan/retan/wet finish;
and through-the-blue.
vii) Waste scrap leather from the leather
tanning
industry, the shoe manufacturing
industry, and other leather product
0136-0597
66
manufacturing
industries.
viii)
Wastewater
treatment
sludges
from
the
production
of
titanium
dioxide
pigment using chromium—bearing ores
by. the chloride pr.ocess
7)
Solid waste from the extraction, beneficiation and
processing of ores and minerals (including coal,
phosphate rock and overburden from the mining of
uranium ore), except as provided by 35 Ill. Ada.
Code 726.212 for facilities that burn or process
hazardous waste.
For purposes of this subsection,
beneficiation of ores and minerals is restricted
to the following activities:
crushing, grinding,
washing, dissolution, crystallization, filtration,
sorting, sizing, drying,
sintering, pelletizing,
briquetting, calcining to remove water or carbon
dioxide, roasting, autoclaving or chlorination in
preparation for leaching
(except where the
roasting or autoclaving or chlorination)/leaching
sequence produces a final or intermediate product
that does not undergo further beneficiation or
processing),
gravity
concentration,
magnetic
separation,
electrostatic
separation,
floatation,
ion exchange, solvent extraction, electrowinning,
precipitation, amalgamation, and heap, dump, vat
tank
and
in situ leaching.
For the purposes of
this
subsection,
solid
waste from the processing
of ores and minerals includes only the following
wastes:
A)
Slag from primary copper processing;
B)
Slag
from
primary
lead
processing;
C)
Red and brown muds from bauxite refining;
D)
Phosphogypsum from phosphoric acid
production;
E)
Slag from elemental phosphorus production;
F)
Gasifier ash from coal gasification;
G)
Process wastewater from coal gasification;
H)
Calcium sulfate wastewater treatment plant
sludge from primary copper processing;
I)
Slag tailings from primary copper processing;
0136-0598
67
3)
Fluorogypsum
from
hydrofluoric
acid
production;
K)
Process wastewater from hydrofluoric acid
production;
L)
Air pollution control dust/sludge from iron
blast
furnaces;
M)
Iron blast furnace slag;
N)
Treated residue from roasting/leaching of
chrome ore;
0)
Process
wastewater
from
primary
magnesium
processing by the anhydrous process;
P)
Process wastewater from phosphoric acid
production;
Q)
Basic oxygen furnace and open hearth furnace
air
pollution
control
dust/sludge
from
carbon
steel
production;
R)
Basic oxygen furnace and open hearth furnace
slag from carbon steel production;
S)
Chloride
processing
waste
solids
from
titanium tetrachloride production;
and,
T)
Slag
from
primary
zinc
smelting.
8)
Cement kiln dust waste, except as provided by 35
Ill. Ada. Code ~4~~.212
for facilities that burn
or process hazardous waste.
9)
Solid
waste
which
consists
of
discarded
arsenical-
treated wood or wood products which fails the test
for the toxicity characteristic eddy
for arocnic
for hazardous waste codes D004 through D017 and
which is not a hazardous waste for any other
reason or roacono if the waste is generated by
persons who utilize the arsenical—treated wood and
wood products for these materials’
intended end
use.
10)
Petroleum-contaminated media and debris that fail
the test for the toxicity characteristic of
Section
721.124
(hazardous waste codes D018
through D043 only) and are subject to corrective
action
regulations
under
35
Iii.
Ada.
Code
731.
0 136-0599
68
11)
Injected
groundwater
that
is
hazardous
only
because
it exhibits the toxicity characteristic
(USEPA hazardous waste codes D018 through D024
only)
in Section 721.124 that is reinjected
through an underground injection well pursuant to
free phase hydrocarbon recovery operations
undertaken at petroleum rétineriés,’petróleum
marketing terminals petroleum bulk plants,
petroleum pipelines and petroleum spill sites
until January 25,
1993.
This extension applies to
recovery operations in existence, or for which
contracts have been issued, on or before March 25,
1991.
For groundwater returned through
infiltration galleries from such at petroleum
refineries, marketing terminals and bulk plants,
until
October
2,
1991.
New operations involving
injection
wells
(beginning
after
March
25,
1991)
will qualify for this compliance date extension
(until
January
25, 1993) only if:
A)
Operations are performed pursuant to a “free
product removal report” pursuant to 35 Ill.
Ada. Code 731.164;
and
B)
A
copy
of
the
“free
product
removal
report”
has
been
submitted
to:
Characteristics
Section
(OS-333)
USEPA
401 N Street, SW
Washington,
D.C.
20460
12)
Used chlorofluorocarbon refrigerants from totally
enclosed heat transfer equipment,
including mobile
air conditioning systems, mobile refrigeration,
and commercial and industrial air conditioning and
refrigeration systems, which use chlorofluoro—
carbons as the heat transfer fluid in a
refrigeration cycle, provided the refrigerant is
reclaimed for further use.
~
Non-terne elated used oil filters which are not
mixed with wastes listed in
Subeart
D.
if these
oil filters have been aravity hot—drained using
one of the following methods:
~j
Puncturing the filter anti-drain back valve
or the filter dome end and hot—draining
~
Hot-draining and crushina:
~
Dismantling and hot-draining;
or.
0136-0600
69
Q).
Any
other
eauivalent
hot-draining
method
which
will
remove
used
oil.
c)
Hazardous wastes which are exempted from certain
regulations.
A hazardous waste which is generated in a
product or raw material storage tank,
a product or raw
material transport vehicle or vessel, a product or raw
material pipeline,
or in a manufacturing process unit
or an associated non—waste—treatment manufacturing
unit,
is not subject to regulation under 35 lU.. Ada.
Code 702, 703, 705 and 722 through 725 and 728 or to
the notification requirements of Section 3010 of RCRA
until it exits the unit in which it was generated,
unless .the unit is a surface impoundment, or unless the
hazardous waste remains in the
unit
more than 90 days
after the unit ceases to be operated for manufacturing,
or
for
storage
or
transportation
of
product
or
raw
materials.
d)
Samples
1)
Except as provided in subsection
(d) (2), below,
a
sample of solid waste or a sample of water,
soil
or air, which is collected for the sole purpose of
testing to determine its characteristics or
composition,
is not subject to any requirements of
this Part or 35
Ill. Ada. Code 702,
703, 705 and
722 through 728.
The sample qualifies when:
A)
The sample is being transported to a
laboratory for the purpose of testing; or
B)
The sample is being transported back to the
sample Gollector after testing; or
C)
The sample is being stored by the sample
collector before transport to a laboratory
for
testing;
or
I))
The sample is being stored in a laboratory
before testing; or
E)
The sample
‘is being stored in a laboratory
for testing but before it is returned to the
sample collector; or
F)
The sample is being stored temporarily in the
laboratory after testing for a specific
purpose (for example, until conclusion of a
court case or enforcement action where
further
testing
of the sample may be
necessary).
0136-0601
70
2)
In
order
to
qualify
for
the exemption in
subsection
(d)(1)(A) and
(B), above, a sample
collector
shipping
samples
to
a
laboratory
and
a
laboratory
returning samples to a sample collector
must:
A)
Comply with U.S. Department of Transportation
(DOT),
U.S. Postal Service
(USPS) or any
other applicable shipping requirements; or
B)
Comply with the following requirements if the
sample collector determines that DOT, USPS or
other shipping requirements do not apply to
the shipment of the sample:
i)
Assure that the following information
accompanies the sample:
The sample
collector’s
name,
mailing
address
and
telephone number; the laboratory’s name,
mailing address and telephone number;
the quantity of
the
sample; the date of
the shipment; and a description of the
sample.
ii)
Package the sample so that it does not
leak, spill or vaporize from its
packaging.
3)
This exemption does not apply if the laboratory
determines that the waste is hazardous but the
laboratory is no longer meeting any of the
conditions stated in subsection
(d) (1), above.
e)
Treatability study samples.
1)
Except as is provided in subsection
(e) (2),
below,
persons who generate or collect samples for the
purpose of conducting treatability studies, as
defined in 35 Ill. Ada. Code 720.110, are not
subject to any requirement of 35 Ill. Ada. Code
721 through 723 or to
the
notification
requirements of Section 3010 of the Resource
Conservation and Recovery Act.
Nor are such
samples included in the quantity determinations of
Section 721.105 and 35 Ill. Ada. Code 722.134(d)
when:
A)
The sample is being collected and prepared
for transportation by the generator or sample
collector;
or,
B)
The
sample
is
being
accumulated
or
stored
by
0
I 36-0602
71
the
generator
or
sample
collector
prior
to
transportation
to
a
laboratory
or
testing
facility;
or
C)
The sample is being transported to the
laboratory or testing facility for the
purpose of conducting a treatability study.
2)
The exemption in subsection
(e) (1), above,
is
applicable ‘to samples of hazardous waste being
collected and shipped for the purpose of
conducting
treatability
studies
provided
that:
A)
The generator or sample collector uses
(in
“treatability
studies”)
no
more than 1000 kg
of any non—acute hazardous waste,
1 kg of
acute hazardous waste or 250 kg of soils,
water or debris contaminated with acute
hazardous
waste
for each process being
evaluated for each generated wastestream; and
B)
The mass of each shipment does not exceed
1000 kg of non-acute hazardous waste,
1 kg of
acute
hazardous
waste or 250 kg of soils,
water or debris contaminated with acute
hazardous
waste;
and
C)
The sample must be packaged so that it does
not leak, spill or vaporize from its
packaging during shipment and the
requirements
of
subsections
(e)
(2)
(C) (i)
or
(ii), below,
are met.
i)
The transportation of each sample
shipment complies with U.S.
Department
of Transportation (DOT), U.S. Postal
Service
(USPS) or any other applicable
shipping requirements; or
ii)
If the DOT, USPS or other shipping
requirements do not apply to the
shipment of the sample, the following
information must accompany the sample:
The name, mailing address and telephone
number of the originator of the sample;
the name,
address and telephone number
of the facility that will perform the
treatability study; the quantity of the
sample; the date of the shipment; and,
a
description of the sample, including its
USEPA hazardous waste number.
0
I 36-0603
72
D)
The sample is shipped to a laboratory or
testing
facility
which
is
exempt
under
subsection
(f),
below, or has an appropriate
RCRA
permit
or
interim
status.
E)
The generator or sample collector maintains
the following records for a period ending
3
years after completion of the treatability
study:
i)
Copies of the shipping documents;
ii)
A copy of the contract with the facility
conducting the treatability study;
iii) Documentation showing:
The amount of
waste shipped under this exemption; the
name, address and USEPA identification
number of the laboratory or testing
facility
that
received
the
waste;
the
date
the
shipment
was
made;
and,
whether
or not unused samples and residues were
returned to the generator.
F)
The generator reports the information
required
in
subsection
(e) (2) (E) (iii),
above,
in
its
report
under
35
Ill.
Ada.
Code
722.141.
3)
The Agency may grant requests, on a case—by—case
basis,
for quantity limits in excess of those
specified
in
subsection
(e)(2)(A),
above,
for
up
to an additional 500 kg of any non—acute hazardous
waste,
1 kg of acute hazardous waste and 250 kg of
soils,
water
or
debris
contaminated
with
acute
hazardous
waste,
to
conduct
further
treatability
study
evaluation
when:
There
has
been
an
equipment or mechanical failure during the conduct
of the treatability study; there is need to verify
the results of a previously conducted treatability
study;
there is
a need to study and analyze
alternative techniques ~within a previously
evaluated treatment process;
or, there is a need
to do further evaluation of an ongoing
treatability study to determine final
specifications for treatment.
The additional
quantities allowed are subject to all the
provisions in subsections
(e) (1) and
(e) (2) (B)
through
(F), above.
The generator or sample
collector must apply to the Agency and provide in
writing
the
following
information:
0l36-060~
73
A)
The
reason
why
the
generator
or
sample
collector requires additional quantity of
sample for the treatability study evaluation
and the additional quantity needed;
B)
Documentation accounting for all samples of
hazardous
waste
from
the
wastestream
which
have been sent for or undergone treatability
studies, including
the
date each previous
sample was shipped, the quantity of each
previous shipment, the laboratory or testing
facility to which it was shipped, what
treatability study processes were conducted
on each sample shipped, and the available
results
of
each treatability study;
C)
A
description
of
the
technical
modifications
or
change
in
specifications
which
will,
be
evaluated and the expected results;
D)
If such further study is being required due
to
equipment
or
mechanical
failure,
the
applicant must include information regarding
the reason for the failure or breakdown and
also include what procedures or equipment
have
been
made
to
protect
against
further
breakdowns;
and,
E)
Such
other
information
as the Agency
determines is necessary.
4)
Final
Agency
determinations
pursuant
to
this
subsection
may
be
appealed
to
the
Board.
f)
Samples undergoing treatability studies at laboratories
or testing facilities.
Samples undergoing treatability
studies and the laboratory or testing facility
conducting such treatability studies (to
the
extent
such facilities are not otherwise subject to
RCRA
requirements)
are
not
subject
tO
any
requirement
of
this Part,
or of 35 Ill.
Ada.
Code 702, 703, 705, 722
through 726, and 728,
or to the notification
requirements of Section 3010 of the Resource
Conservation and Recovery Act, provided that the
requirements
of
subsections
(f)
(1)
through
(f) (11),
below, are met.
A mobile treatment unit may qualify as
a testing facility subject to subsections
(f) (1)
through
(f) (11),
below.
Where a group of mobile
treatment
units
are
located
at
the
same
site,
the
limitations specified in subsections
(f) (1) through
(f)
(11),
below,
apply
to
the
entire
group
of
mobile
treatment
units collectively as
if the group were one
0136-0605
74
mobile
treatment
unit.
1)
No
less
than
45
days
before
conducting
treatability studies, the facility notifies the
Agency in writing that it intends to conduct
treatability studies under this
subsection.
2)
The laboratory or testing facility conducting the
treatability
study has a USEPA identification
number.
3)
No more than a total of 250 kg of “as received”
hazardous waste is subjected to initiation of
treatability studies in any single day.
“As
received” waste refers to the waste as received in
the shipment from the generator or sample
collector.
4)
The
quantity
of
“as received” hazardous waste
stored at the facility for the purpose of
evaluation in treatability studies does not exceed
1000 kg, the total of which can include 500 kg of
soils,
water
or
debris contaminated with acute
hazardous waste or 1 kg of acute hazardous waste.
This quantity limitation does not include:
A)
Treatability study residues; and,
B)
Treatment materials (including nonhazardous
solid waste)
added to “as received” hazardous
waste.
5)
No more than 90 days have elapsed since the
treatability study for the sample was completed,
or no more than one year has elapsed since the
generator
or
sample
collector
shipped
the
sample
to the laboratory or testing facility, whichever
date first occurs.
6)
The treatability study does not involve the
placement of hazardous waste on the land or open
burning of hazardous waste.
7)
The facility maintains records for 3 years
following completion of each study that show
compliance with the ‘treatment rate limits and the
storage time and quantity limits.
The following
specific information must be included for each
treatability study conducted:
A)
The name, address and USEPA identification
number of the generator or sample collector
0136-0606
75
of each waste sample;
B)
The
date
the
shipment
was
received;
C)
The quantity of waste accepted;
D)
The quantity of “as received” ‘waste in
storage each day;
E)
The date the treatment study was initiated
and the
amount
of “as received” waste
introduced to treatment each day;
F)
The date the treatability study was
concluded;
G)
The date any unused sample or residues
generated from the treatability study were
returned
to the generator or sample collector
or,
if sent to a designated facility, the
name of the facility and the USEPA
identification
number.
B)
The
facility
keeps,
on-site,
a
copy
of
the
treatability study contract and all shipping
papers associated with the transport of
treatability
study
samples
to
and
from
the
facility
for
a
period
ending
3
years
from
the
completion
date
of
each
treatability
study.
9)
The facility prepares and submits a report to the
Agency by March 15 of each year that estimates the
number
of studies and the amount of waste expected
to
be
used
in
treatability
studies
during
the
current
year,
and
includes
the
following
information for the previous calendar year:
A)
The name, address and USEPA identification
number of the facility conducting the
treatability studies;
B)
The types
(by process) of treatability
studies conducted;
C)
The names and addresses of persons for whom
studies have been conducted (including their
USEPA identification numbers);
D)
The total quantity of waste in storage each
day;
E)
The quantity and types of waste subjected to
0136-0607
76
treatability
studies;
F)
When each treatability study was conducted;
G)
The final disposition of residues and unused
sample from e~irhtreatability studyj
10)
The facility determines whether any unused sample
or residues generated by the treatability study
are hazardous waste under Section 721.103
and,
if
so, are subject to 35 Ill. Ada. Code 702, 703 and
721 through 728, unless
the
residues and unused
samples are returned to the sample originator
under the subsection
(e)
exemption, above.
11)
The facility notifies the Agency by letter when
the facility is no longer planning to conduct any
treatability studies at the site.
(Source:
Amended at 16 Ill. Reg.
,
effective
)
SUBPART
B:
CRITERIA FOR IDENTIFYING
THE CHARACTERISTICS
OF HAZARDOUS WASTE
AND
FOR LISTING HAZARDOUS WASTES
Section 721.111
Criteria for Listing Hazardous Waste
a)
USEPA lists a solid waste as a hazardous waste only
upon determining that the solid waste meets one of the
following criteria:
1)
It exhibits any of the characteristics of
hazardous waste identified in Subpart C;
or
2)
Acute hazardous waste.
It has been found to be
fatal to humans in low doses or,
in the absence of
data on human toxicity,
it has been shown in
studies to have an oral LD 50 toxicity (rat)
of
less than 50 ag/kg,
an inhalation LC 50 toxicity
(rat)
of
less
than
2
ag/L,
or
a
dermal
LD
50
toxicity (rabbit) of less than 200 mg/kg or is
otherwise capable of causing or significantly
contributing to an increase in serious
irreversible or incapacitating reversible,
illness.
BOARD
NOTE:
Waste listed in ‘accordance with these
criteria are designated Acute Hazardous Waste.
3)
Toxic
waste.
It contains any of the toxic
constituents listed in Appendix H and, after
considering any of the following factors, USEPA
0 136-0608
77
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:
BOARD NOTE:
Substances are listed in Appendix H
only if they have been shown in scientific studies
to have toxic, carcinogenic, autagenic or
teratogenic effects on humans or other life forms.
A)
The nature of the toxicity presented by the
constituent.
B)
The concentration of the constituent in the
waste.
C)
The
potential
of
the
constituent
or
any
toxic
degradation
product
of
the
constituent
to
migrate
from
the
waste
into
the
environment
under
the
types
of
improper
management
considered in subsection
(a) (3) (G).
D)
The
persistence
of
the
constituent
or
any
toxic degradation product of the constituent.
E)
The potential for the constituent or any
toxic degradation product of the constituent
to degrade into northarmful constituents and
the rate of degradation.
F)
The degree to which the constituent or any
degradation product of the constituent
bioaccumulates
in
ecosystems.
G)
The
plausible
types
of
improper
management
to
which
the
waste
could
be
subjected.
H)
The quantities of the waste generated at
individual generation sites or on a regional
or national basis.
I)
The nature and severity of the human health
and environmental damage that has occurred as
a result of
the
improper management of the
wastes containing the constituent.
J)
Action taken by other governmental agencies
or regulatory programs based on
the
health
or
environmental hazard posed by the waste or
waste
constituent.
0136-0609
78
K)
Such
other
factors
as
may be appropriate.
BOARD
NOTE:
Wastes listed
in
accordance
with
these criteria are designated toxic wastes.
b)
USEPA
may
list
classes
or
types of solid waste as
hazardous waste if USEPA has reason to believe that
individual wastes, within the class or type of waste,
typically
or
frequently
are
hazardous
under
the
definition of hazardous waste found in Section 1004(5)
of the Resource Conservation and Recovery Act
(42 USC
6901
et
seq.)
c)
USEPA
will
use
the
criteria
for
listing
specified
in
this Section to establish the exclusion limits referred
to
in
Section
721.105(c).
(Source:
Amended
at
16
Ill.
Reg.
,
effective
0136-06 10
79
TITLE 35:
ENVIRONMENTAL
PROTECTION
SUBTITLE G:
WASTE
DISPOSAL
CHAPTER I:
POLLUTION
CONTROL
BOARD
SUBCHAPTER
C:
HAZARDOUS
WASTE OPERATING REQUIREMENTS
PART
724
STANDARDS
FOR
OWNERS AND
OPERATORS
OF
HAZARDOUS
WASTE
TREATMENT,
STORAGE
AND
DISPOSAL FACILITIES
SUBPART
A:
GENERAL
PROVISIONS
Purpose,
Scope
and
Applicability
Relationship
to
Interim
Status
Standards
SUBPART
B:
GENERAL
FACILITY
STANDARDS
Applicability
Identification
Number
Required
Notices
General
Waste
Analysis
Security
General
Inspection
Requirements
Personnel
Training
General
Requirements
for
Ignitable,
Reactive
or
Incompatible
Wastes
724.119
Construction
Quality
Assurance
Program
724.118
Location
Standards
SUBPART C:
PREPAREDNESS
AND
PREVENTION
Section
724. 130
724.131
724.132
724. 133
724.134
724.135
724. 137
Applicability
Design
and
Operation
of
Facility
Required
Equipment
Testing
and
Maintenance
of
Equipment
Access
to
Communications
or
Alarm
System
Required
Aisle
Space
Arrangements
with
Local
Authorities
SUBPART
D:
CONTINGENCY
PLAN
AND EMERGENCY PROCEDURES
Section
724.
150
724. 151
724. 152
724.153
724. 154
724.155
724
•
156
Applicability
Purpose
and
Implementation
of
Contingency
Plan
Content
of
Contingency
Plan
Copies
of
Contingency
Plan
Amendment of
Contingency
Plan
Emergency
Coordinator
Emergency
Procedures
SUBPART E:
MANIFEST
SYSTEM, RECORDKEEPING AND REPORTING
Section
724.170
Applicability
724.171
Use
of
Manifest
System
Section
724. 101
724.103
Section
724.110
724.
111
724
•
112
724.
113
724.
114
724.
115
724.116
724.117
0136-0611
80
724.172
Manifest
Discrepancies
724.173
Operating
Record
724.174
Availability,
Retention
and
Disposition
of
Records
724.175
Annual
Report
724.176
Unmanifested Waste Report
724.177
Additional
Reports
SUBPART
F:
RELEASES
FROM
SOLID
WASTE
MANAGEMENT
UNITS
Applicability
Required Programs
Groundwater
Protection
Standard
Hazardous Constituents
Concentration
Limits
Point
of
Compliance
Compliance
Period
General
Groundwater
Monitoring
Requirements
Detection
Monitoring
Program
Compliance
Monitoring
Program
Corrective
Action
Program
Corrective
Action
for
Solid
Waste
Management
Units
SUBPART G:
CLOSURE
AND
POST-CLOSURE
Applicability
Closure
Performance
Standard
Closure
Plan;
Amendment
of
Plan
Closure;
Time
Allowed
For
Closure
Disposal
or
Decontamination
of
Equipment,
Structures
and
Soils
Certification
of
Closure
Survey
Plat
Post—closure
Care
and
Use
of
Property
Post—closure
Plan;
Amendment
of
Plan
Post—closure
Notices
Certification
of
Completion
of
Post-closure
Care
SUBPART
H:
FINANCIAL
REQUIREMENTS
Section
724.240
Applicability
724.241
Definitions of Terms As Used In This Subpart
724.242
Cost
Estimate
for
Closure
724.243
Financial
Assurance
for
Closure
724.244
Cost
Estimate
for
Post-closure
Care
724.245
Financial
Assurance
for
Post-closure
Care
724.246
Use
of
a
Mechanism
for
Financial
Assurance
of
Both
Closure
and
Post-closure
Care
724.247
Liability
Requirements
724.248
Incapacity
of
Owners or Operators, Guarantors or
Financial
Institutions
724.251
Wording
of
the
Instruments
0136-0612
Section
724.190
724.191
724. 192
724. 193
724
.
194
724.
195
724.196
724
.
197
724
.
198
724
.
199
724,200
724.
201
Section
724.210
724.211
724.212
724 .213
724.214
724.215
724.216
724.217
724.218
724.219
724.220
81
SUBPART
I:
USE
AND MANAGEMENT
OF
CONTAINERS
Applicability
Condition
of
Containers
Compatibility
of
Waste
With
Container
Management of Containers
Inspections
Containment
Special
Requirements
for
Ignitable
or
Reactive
Waste
Special
Requirements
for
Incompatible
Wastes
Closure
SUBPART
J:
TANK
SYSTEMS
Applicability
Assessment
of
Existing
Tank
System’s
Integrity
Design
and
Installation
of
New
Tank
Systems
or
Components
Containment
and
Detection
of
Releases
General
Operating
Requirements
Inspections
Response
to
Leaks
or
Spills
and
Disposition
of
Leaking
or unfit—for—use Tank Systems
Closure
and
Post—Closure
Care
Special
Requirements
for
Ignitable
or
Reactive
Waste
Special
Requirements
for
Incompatible
Wastes
Special
Requirements
for
Hazardous
Wastes
F020,
F021,
F022,
F023,
F026
and
F027
SUBPART
K:
SURFACE
IMPOUNDMENTS
Applicability
Design
and
Operating
Requirements
Doublc-lincd
Curfact
Impoundmcntoz
Excmption
from
L~uflpart Fi
Cround-wator
Protcotion
Rt~miiremcnts
(Rcpcalod)
Action Leakage Rate
Response
Actions
Monitoring
and
Inspection
Emergency
Repairs;
Contingency
Plans
Closure
and
Post—closure
Care
Special
Requirements
for
Ignitable
or
Reactive
Waste
Special
Requirements
for
Incompatible
Wastes
Special
Requirements
for
Hazardous
Wastes
F020,
F021,
F022,
F023,
F026
and
F027
SUBPART L:
WASTE
PILES
~
~
LL-om Cubpart
r~
Cround-
i~quircmcnto
(Rcpo~tled)
Action
Leakage
0136-0613
Section
724.270
724. 271
724. 272
724.273
724.274
724. 275
724.276
724.277
724
.
278
Section
724 .290
724 .291
724.292
724.293
724.294
724.295
724 .296
724.297
724.
298
724.299
724.300
Section
724.
320
724.321
724
•
322
724.323
724.326
724.327
724.
328
724.329
724.330
724.
331
Section
724.350
724.351
724.352
Applicability
Design
and
Operating
Requirements
Rate
82
Inopcction of
~
Linero,
Throtcotion
Excmption from
Rcquircmcnta
Cubpart
F:
(Rcpealed)
Response
Action
Plan
Monitoring
and
Inspection
Special
Requirements
for
Ignitable
or
Reactive
Waste
Special Requirements for Incompatible Wastes
Closure
and
Post-closure
Care
Special Requirements for Hazardous Wastes F020,
F021,
F022,
F023,
F026
and
F027
SUBPART M:
LAND
TREATMENT
Applicability
Treatment Program
Treatment
Demonstration
Design
and
Operating
Requirements
Food—chain
Crops
Unsaturated
Zone
Monitoring
Recordkeeping
Closure
and
Post-closure
Care
Special
Requirements
for
Ignitable
or
Reactive
Waste
Special
Requirements
for
Incompatible
Wastes
Special
Requirements
for
Hazardous
Wastes
F020,
F021,
F022,
F023,
F026
and
F027
SUBPART
N:
LANDFILLS
~,
~
.1.
—
a. a.a.~
~
.~
S
a. a. a.
•
Ma..afl.,
.
a.
~a.
as
~.eaa
hJ ~j.St*S
‘..
.1.
tccta.on 1(caulrcmnntn
______
724 .403
724.404
__________________
724.409
Surveying
and
Recordkeeping
724.410
Closure
and
Post—closure
Care
724.412
Special
Requirements
for
Ignitable
or
Reactive
Waste
724.413
Special
Requirements
for
Incompatible
Wastes
724.414
Special
Requirements
for
Bulk
and
Containerized
Liquids
724.415
Special
Requirements
for
Containers
724.416
Disposal
of
Small
Containers
of
Hazardous
Waste
in
Overpacked Drums
(Lab
Packs)
724.417
Special
Requirements
for
Hazardous
Wastes
F020,
F021,
F022,
F023,
F026
and
F027
SUBPART 0:
INCINERATORS
Applicability
Waste
Analysis
Principal
Organic
Hazardous
Constituents
(POHCs)
Performance
Standards
Hazardous
Waste
Incinerator
Permits
0136-06U4
724 .353
724.354
724.356
724.357
724.358
724.359
Section
724.370
724.371
724. 372
724.373
724 .376
724
•
378
724 .379
724.380
724.
381
724.382
724.383
Section
724.400
724.401
724.402
Applicability
Design
and
Operating
Requirements
1
~
~
c
1
1
~..
~
~~
.c......
~
D.
Leakage Rate
Monitoring
and
Inspection
Response
Actions
(Rcpcalcd)
Action
Section
724.440
724
.
441
724.442
724. 443
724.444
83
724.445
724.447
724.451
Section
724.
670
724.671
724
•
672
724.673
724.
674
724.675
Section
724.701
724.
701
724.702
724.703
Operating
Requirements
Monitoring
and
Inspections
Closure
SUBPART
W:
DRIP
PADS
Applicability
Assessment
of
existing
drip
pad
integrity
Design
and
installation
of
new
drip
pads
Design
and
operating
requirements
Inspections
Closure
SUBPART
X:
MISCELLANEOUS UNITS
Applicability
Environmental
Performance
Standards
Monitoring,
Analysis,
Inspection,
Response,
Reporting
and
Corrective
Action
Post—closure
Care
SUBPART
AA:
AIR
EMISSION
STANDARDS
FOR
PROCESS
VENTS
Section
724.930
724
•
931
724.932
724.933
724.934
724.935
724.936
Applicability
Definitions
Standards:
Process
Vents
Standards:
Closed—vent
Systems
and
Control
Devices
Test
methods
and
procedures
Recordkeeping requirements
Reporting
Requirements
SUBPART
BB:
AIR
EMISSION
STANDARDS
FOR
EQUIPMENT
LEAKS
Pumps in Light Liquid Service
Compressors
Pressure
Relief
Devices
in
Gas/Vapor
Sampling
Connecting
Systems
Open—ended Valves or Lines
Valves
in
Gas/Vapor
or
Light
Liquid
Service
Pumps,
Valves,
Pressure
Relief
Devices
and
Standards:
Standards:
Standards:
Standards:
Other
Connectors
Standards:
Delay
of
Repair
Standards:
Closed—vent
Systems
and
Control
Devices
Alternative
Percentage
Standard
for
Valves
Skip
Period
Alternative
for
Valves
Test
Methods
and
Procedures
Recordkeeping
Requirements
Reporting
Requirements
Applicability
Definitions
Standards:
Standards:
Standards:
Service
Section
724.950
724.951
724.952
724.953
724. 954
724.955
724.956
724.957
724. 958
724.959
724.960
724.961
724.962
724.963
724.964
724.965
0 136-0615
84
Appendix
A
Recorcikeeping
Instructions
Appendix B
EPA
Report
Form
and
Instructions
(Repealed)
Appendix D
Cochran’s Approximation to the Behrens-Fisher
Student’s T-Test
Appendix E
Examples of Potentially Incompatible Waste
~ppendix I
Groun4water Monitoring List
AUTHORITY:
Implementing
Section
22.4
and
authorized
by
Section
27 of the Environmental Protection Act
(Ill. Rev. Stat.
1991,
ch.
111½, pars.
1022.4 and 1027).
SOURCE:
Adopted in R82—19,
53 PCB 131, at 7 Ill. Reg.
14059,
effective October 12,
1983; amended in R84—9 at
9 Ill. Reg.
11964, effective July 24,
1985; amended in R85—22 at 10 Ill. Reg.
1136,
effective
January
2,
1986; amended in R86-1 at 10 Ill.
Reg.
14119,
effective
August
12,
1986;
amended
in
R86—28
at
11
Ill.
Reg.
6138,
effective
March
24,
1987;
amended
in
R86—28
at
11
Ill.
Reg.
8684,
effective
April
21,
1987;
amended
in
R86-46
at
11
Ill.
Reg.
13577, effective August
4,
1987; amended in R87—5 at 11 Ill.
Reg.
19397, effective November 12,
1987;
amended in R87—39 at
12
Ill.
Reg.
13135, effective July 29,
1988; amended in R88—16 at 13
Ill.
Reg.
458,
effective
December
28,
1988;
amended
in
R89-1
at
13
Ill.
Reg.
18527,
effective
November
13,
1989;
amended
in
R90—2
at
14
Ill.
Reg.
14511,
effective
August
22,
1990;
amended
in
R90—
10 at 14 Ill. Reg.
16658, effective September 25, 1990; amended
in R90-11 at 15 Ill. Reg. 9654, effective June 17,
1991; amended
in R91—1 at 15 Ill. Reg. 14572, effective October
1,
1991;
amended
in
R91—13 at 16 Ill.
Reg.
9833, effective June 9,
1992;
amended
in
R92-1
at
16
Ill.
Reg.
,
effective
;
amended in R92-10 at 16
Ill.
Reg.
,
effective
SUBPART B:
GENERAL FACILITY STANDARDS
Section 724.113
General Waste Analysis
a)
Analysis:
1)
Before
an
owner or operator treats, stores or
disposes of any hazardous waste~,or non—hazardous
waste~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, thia ~g
analysis
must contain all the information which must be
known to treat,
store or dispose of the waste in
accordance with the rcquircmcnta of this Part e~
~
35
Ill. Adm. Code 728, or with thc conditiono
of a permit iooued under 35 Ill. Ada. Code 702,
703 and 705.
2)
The analysis may include data developed under 35
0136-06 16
85
Ill.
Ada.
Code
721,
and
existing
published
or
documented
data
on
the
hazardous
waste
or
on
hazardous
waste
generated
from similar processes.
BOARD
NOTE:
For
example,
the
facility’s
records
of analyses performed on the waste before the
effective date of these regulations, or studies
conducted on hazardous waste generated from
processes similar to that which generated the
waste to be managed at the facility, may be
included in the data base required to comply with
subsection
(a) (1).
The owner or operator of an
off—site
facility
may
arrange
for
the
generator
of
the hazardous waste to supply part or all of the
information required by subsection
(a) (1), except
as
otherwise
specified
in
35
Ill.
Ada.
Code
728.107(b)
and
(c).
If
the
generator
does
not
supply
the
information,
and
the
owner
or
operator
chooses
to
accept
a
hazardous
waste,
the
owner
or
operator
is
responsible
for
obtaining
the
information required to comply with this Section.
3)
The analysis must be repeated as necessary to
ensure
that
it
is
accurate
and
up
to
date.
At
a
minimum,
the
analysis
must
be
repeated:
A)
When
the
owner
or
operator
is
notified,
or
has reason to believe, that the process or
operation
generating
the
hazardous
waste,
or
non—hazardous
waste
if
applicable
under
Section 724.213(d), has changed; and
B)
For
off-site
facilities,
when
the
results
of
the
inspection
required
in
subsection
(a)(4)
indicate
that
the
hazardous
waste
received
at
the
facility
does
not
match
the
waste
designated
on
the
accompanying
manifest
or
shipping paper.
4)
The owner or operator of an off-site facility
shall inspect and,
if necessary,
analyze each
hazardous waste movement received at the facility
to determine whether it matches the identity of
the waste specified on the accompanying manifest
or
shipping
paper.
b)
The
owner
or
operator
shall
develop and follow a
written waste analysis plan which describes the
procedures which it will carry out to comply with
subsection
(a).
The owner or operator shall keep this
plan
at
the
facility.
At
a
minimum,
the
plan
must
specify:
0136-05j7
86
1)
The
parameters
for
which
each
hazardous
waste,
or
non—hazardous
waste
if
applicable
under
Section
724.213(d),
will
be
analyzed
and
the
rationale
for
the selection of these parameters
(i.e., how
analysis for these parameters will provide
sufficient information on the, ~~aste’sproperties
to comply with subsection
(a)).
2)
The test methods which will be used to test for
these
parameters.
3)
The sampling method which will be used to obtain a
representative sample of the waste to be analyzed.
A representative sample may be obtained using
either:
A)
One
of
the
sampling
methods described in 35
Ill.
Ada.
Code
72l.Appendix
A;
or
B)
An equivalent sampling method.
BOARD
NOTE:
See 35 Ill. Ada. Code
720.121 for related discussion.
4)
The
frequency
with
which
the
initial
analysis
of
the waste will be reviewed or repeated to ensure
that
the
analysis
is
accurate and up to date.
5)
For
off—site
facilities,
the waste analyses that
hazardous
waste
generators
have
agreed
to
supply.
6)
Where applicable, the methods which will be used
to meet the additional waste analysis requirements
for
specific
waste
management
methods
as
specified
in
Sections
724.117,
724.414,
724.441,
724.934(d)
and
724.963(d),
and
35
Ill.
Ada. Code 728.107.
And,
7)
For
surface
impoundments
exempted
from
land
disposal
restrictions
under
35
Ill.
Ada.
Code
728.104(a),
the
procedures
and schedules for:
A)
The sampling of impoundment contents;
B)
The analysis of test data;
and,
C)
The
annual
removal
of
residues
which
are
not
delisted
under
35
Ill.
Ada.
Code
720.122
or
which
exhibit
a
characteristic
of
hazardous
waste,
and
either:
i)
Do
not
meet
applicable
treatment
0136-06t8
87
standards
of
35
Ill.
Ada.
Code
728.Subpart
D;
or
ii)
Where no treatment standards have been
established:
Such
residues
are
prohibited from land disposal under 35
Ill. Ada. Code 728.132 or 728.139; or
such residues are prohibited from land
disposal
under
35
Ill.
Ada.
Code
728.133(f).
C)
For
off-site
facilities,
the waste analysis plan
required in subsection
(b) must also specify the
procedures
which
will
be
used
to
inspect
and,
if
necessary, analyze each movement of hazardous waste
received
at
the
facility
to
ensure
that
it
matches
the
identity
of
the
waste
designated
on
the
accompanying
manifest
or
shipping
paper.
At
a
minimum,
the
plan
must
describe:
1)
The
procedures
which
will
be
used
to
determine
the
identity
of
each
movement
of
waste
managed
at
the
facility;
and
2)
The
sampling
method
which
will
be
used
to
obtain
a
representative
sample
of
the
waste
to
be
identified,
if
the
identification
method
includes
sampling.
BOARD
NOTE:
35
Ill.
Ada.
Code 703, requires
that
the
waste
analysis
plan
be
submitted
with
Part
B
of
the
permit
application.
(Source:
Amended
at
16
Ill.
Reg.
,
effective
)
Section
724.115
General
Inspection
Requirements
a)
The owner or operator shall conduct inspections often
enough to identify problems in time to correct them
before
they
harm
human health or the environment.
The
owner or operator shall inspect the facility for
malfunctions and deterioration, operator errors and
discharges
which
may
be causing, or may lead to:
1)
Release of hazardous waste constituents to the
environment;
or
2)
A
threat
to
human
health.
b)
Inspection
schedule.
0136-0619
88
1)
The
owner
or
operator
shall
develop
and
follow
a
written
schedule
for inspecting monitoring
equipment,
safety
and emergency equipment,
security devices and operating and structural
equipment (such as dikes and sump pumps) that are
important to preventing,
detecting or responding
to
environmental
or
human
health
hazards.
2)
The owner or operator shall keep this schedule at
the
facility.
3)
The
schedule
must identify the types of problems
(e.g., malfunctions or deterioration) which are to
be looked for during the inspection
(e.g.,
inoperative
sump
pump,
leaking fitting, eroding
dike,
etc.).
4)
The frequency of inspection may vary for the items
on the schedule.
However,
it should be based on
the
rate
of
poooiblc
deterioration
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.
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 tcrao items
and frequencies called for in Sections 724.274,
724.2~)4,
724.293,
724.295.
724.326,
7-2-4.353,
724.354,
724.378,
724.403,
724.447,
724.702,
724.933, 724.952,
724.953 and 724.958, where
applicable
BOARD
NOTE:
35
Ill.
Ada.
Code 703 requires the
inspection schedule to be submitted with Part B of
the permit application.
The Agency will evaluate
the schedule along with the rest of the
application to ensure that it adequately protects
human health and the environment.
As part of this
review, the Agency may modify or amend the
schedule
as may be necessary.
c)
The owner or operator shall remedy any deterioration or
malfunction of equipment or structures which the
inspection
reveals
on a schedule which ensures that the
problem
does
not
lead
to
an
environmental
or
human
health hazard.
Where a hazard is imminent or has
already occurred, remedial action must be taken
immediately.
d)
The
owner
or
operator
shall
record
inspections
in
an
inspection
log
or
summary.
The
owner
or
operator
shall
0 136-0620
89
keep
these
records
for
at
least
three
years
from
the
date
of
inspection.
At
a
minimum,
these
records
must
include
the
date
and
time
of
the
inspection,
the
name
of
the
inspector,
a
notation
of
the
observations
made
and the date and nature of any repairs or other
remedial actions.
(Source:
Amended at 16 Ill. Reg.
,
effective
)
Section 724.119
Construction Quality Assurance Program
~j
Construction
quality
assurance
(COA) oroaram.
fl~
A CQA ~roqram is required for all surface
impoundment. waste pile and landfill units that
are required to comply with Sections 724.321(c)
and
(d), 724.351(c) and
(d). and 724.401(c)
and
(d).
The program must ensure that the constructed
unit meets or exceeds all design criteria and
specifications in the permit.
The
~roaram
must
be
developed and implemented under the direction of a
CQA officer who is a registered professional
engineer.
IL
The
COA
program must address the ~following
Physical components, where applicable:
~
Foundations
~
Dikes
~j
Low-permeability soil liners
Q)
Geomenthranes
(flexible membrane liners)
~
Leachate collection
and
removal sYstems and
leak detection systems; and
~j.. Final cover systems.
~j
Written CQA plan.
The owner or oDerator of units
subject to the CQA program under subsection
(a)
above
must develop and implement a written CQA plan.
The
plan must identify stePs that will be used to monitor
and document the quality of materials and the condition
and manner of their installation.
The
CQA
Plan must
include:
jj
Identification of ap~1icpbleunits. and a
description of how they will be constructed.
0136-0621
90
IL
Identification of key personnel in the development
and implementation of the CQA plan.
and CQA
officer qualifications.
A description of inspection and sampling
activities for all unit corn~onentsidentified
in,
subsection
(a) (2)
above,
including observations
and tests that will be used before, during and
after construction to ensure that the construction
materials and the installed unit comoonents meet
the design specifications.
The description must
cover: Samplina size and locations; fre~encyof
testing; data evaluation procedures: acceptance
and re-lection criteria for construction materials;
~1ans for implementing corrective measures; and
data
or
other
information
to
be
recorded
and
retained in the operating record under Section
724. 173.
çì
Contents of Program.
il
The
CQA
program
must
include
observations.
inspections, tests and measurements sufficient to
ensure:
~j.
Structural stability and integrity of all
components of the unit identified in
subsection
(a) (2) above
~j
Proper construction of all components of the
liners,
leachate collection and removal
system, leak detection system and final cover
system, according to permit specifications
and aood engineering practices and proper
installation of all components
(e.g.,
pipes)
according to design specifications:
ci
Conformity
of
all materials used with design
and other material specifications under
Sections 724.321. 724.351 and 724.401.
IL
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 accent an
alternative demonstration,
in lieu of a test fill,
01360622
91
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.
~j
Certification.
Waste
must
not
be
received
in
a
unit
subject to Section 724.119
until
the
owner
or
operator
has submitted to the Aaencv by certified mail or hand
delivery a certification signed by the COA officer that
the
approved CQA plan has been successfully carried out
and
that
the
unit
meets
the
reauirements
of
Sections
724.321(c) or
(d).
724.351(c)
or
(d). or 724.401(c) or
(d): and
the
procedure
in
35
Ill.
Ada. Code 703.247(b)
has been completed.
Documentation suPportina the CQA
officer’s certification must be furnished to the Agency
upon request.
(Source:
Added at 16
Ill. Reg.
,
effective
)
SUBPART E:
MANIFEST SYSTEM, RECORDKEEPING AND
REPORTING
Section 724.173
Operating Record
a)
The owner or operator shall keep a written operating
record at the facility.
b)
The following information must be recorded, as it
becomes available, and maintained in the operating
record until closure of the facility:
1)
A description and the quantity of each hazardous
waste received, and the method or methods and date
or dates of its treatment,
storage or disposal at
the facility as required by Appendix A;
2)
The location of each hazardous waste within the
facility and the quantity at each location.
For
disposal facilities,
the location and quantity of
each hazardous waste must be recorded on a map or
diagram of each cell or disposal area.
For all
facilities,
this information must include cross—
references to specific manifest document numbers,
if the waste was accompanied by a manifest;
BOARD NOTE:
See Section 724.219 for related
requirements.
3)
Records and results of waste analyses performed as
specified in Sections 724.113, 724.117,
724.414,
724.441,
724.934,
724.963, and in 35 Ill. Ada.
UI 36-0623
92
Code
728.104(a)
and
728.107;
4)
Summary reports and details of all incidents that
require implementing the contingency plan as
specified
in
Section
724.156(j);
5)
Records and results of inspections as required by
Section
724.115(d)
(except
these
data
need
to
be
kept
only
three
years);
6)
Monitoring, testing or analytical data and
corrective
action
data
where
required
by
Subpart
F
or Sections 724.119, 724.291.
724.293.
724.295,
724.322.
724.323. 724.326,
724.353,
724.352
through 724.354, 724.376,
724.378,
724.380,
724.403,
724.402
through 724.404,
724.409,
724.447,
724.702,
724.934(c)
through
(f),
724.935,
724.963(d)
through
(i) or 724.964.
7)
For off—site facilities,
notices to generators as
specified in Section 724.112(b);
8)
All
closure
cost
estimates
under
Section
724.242
and, for disposal facilities, all post-closure
cost estimates under Section 724.244;
9)
A certification by the permittee, no less often
than annually: that the permittee has a program in
place to reduce the volume and toxicity of
hazardous waste that the permittee generates,
to
the degree the permittee
determines
to
be
economically practicable; and that the proposed
method of treatment, storage or disposal is that
practicable method currently available to the
permittee which minimizes the present and future
threat to human health and the environment;
10)
Records of the quantities
(and date of placement)
for each shipment of hazardous waste placed in
land disposal units under an extension of the
effective date of any land disposal restriction
granted pursuant to 35 Ill. Ada. Code 728.105,
a
petition pursuant to 35 Ill. Ada. Code 728.106 or
a certification under 35 Ill. Ada. Code 728.108,
and the applicable notice required of a generator
under 35 Ill. Ada. Code 728.107(a);
11)
For an off-site treatment facility, a copy of the
notice, and the certification and demonstration,
if applicable, required of the generator or the
owner
or operator under 35 Ill. Ada. Code 728.107
or 728.108;
01 36-062L~
93
12)
For an on-site treatment facility, the information
contained in the notice
(except the manifest
number), and the certification and demonstration,
if applicable,
required of the generator or the
owner or operator under 35 Ill. Ada. Code 728 .107
or 728.108;
13)
For an off—site land disposal facility,
a copy of
the notice, and the certification and
demonstration,
if applicable,
required of the
generator or the owner or operator of a treatment
facility under
35 Ill. Ada. Code 728.107 or
728.108, whichever is applicable; and
14)
For an on-site land disposal facility, the
information contained in the notice required of
the generator or owner or operator of a treatment
facility under 35 Ill. Ada. Code 728.107, except
for the manifest number, and the certification and
demonstration if applicable, required under 35
Ill. Ada. Code 728.108, whichever is applicable.
15)
For an off-site storage facility, a copy of the
notice, and the certification and demonstration if
applicable, required of the generator or the owner
or operator under 35 Ill. Ada. Code 728.107 or
728.108;
and,
16)
For an on-site storage facility, the information
contained in the notice
(except the manifest
number), and the certification and demonstration
if applicable, required of the generator or the
owner or operator under 35 Ill. Ada. Code 728.107
or 728.108.
(Source:
Amended at 16 Ill. Reg.
,
effective
)
SUBPART K:
SURFACE IMPOUNDMENTS
Section 724.321
Design and Operating Requirements
a)
Any
surface impoundment that it not covered by
subsection
(c)
or 35
Ill.
Ada. Code 725.321 must have a
liner for all portions of the impoundment
(except for
existing portions of such impoundment).
The liner must
be designed, constructed and installed to prevent any
migration of wastes out of the impoundment to the
adjacent subsurface soil or groundwater or surface
water at any time during the active life (including the
closure period)
of the impoundment.
The liner may be
constructed of materials that may allow wastes to
0136-0625
94
migrate into the liner
(but not into the adjacent
subsurface soil or groundwater or surface water)
during
the active life of the facility, provided that the
impoundment is closed in accordance with Section
724
•
328(a) (1).
For impoundments that will be closed in
accordance with Section 724.32.8 (a) (2), the liner must
be constructed of materials that can prevent wastes
from migrating into the liner during the active life of
the facility.
The liner must be:
1)
Constructed of materials that have appropriate
chemical properties and sufficient strength and
thickness to prevent failure due to pressure
gradients (including static head and external
hydrogeologic forces), physical contact with the
waste or leachate to which they are exposed,
climatic conditions,
the stress of installation
and the stress of daily operation;
2)
Placed upon a foundation or base capable of
providing support to the liner and resistance to
pressure gradients above and below the liner to
prevent failure of the liner due to settlement,
compression or uplift; and
3)
Installed to cover all surrounding earth likely to
be in contact with the waste or leachate.
b)
The owner or operator will be exempted from the
requirements of subsection
(a) above if the Board
findo-
baciod on a dcmonBtration
by
the owner or
opcra’cor,
in a variance aniijor -uitc—opc~xric
rulemaking, grants an ad-lusted standard pursuant to 35
Ill. Ada. Code 106.Subpart G.
The level of
justification is a demonstration by the owner or
operator that alternate design andg~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 excmptionadiusted 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
0136-0626
95
quality and mobility of the leachate produced and
the potential for it to migrate to groundwater or
surface water.
c)
The owner or operator of each new surface impoundment,-
each ncw
gun
ace iapoundaent unit at.an oxieting
facility, caoh replacement of an cxiating
surface
impoundment unit and each lateral oupansion of an
existing surface impoundment unit, must inatall two or
more liners and a lcaohate collection syatom between
such lincre.
The lincra and loaohatc collection syatce
muot protect human health and the environment.
The
requirements of this subsection apply with reapeot to
all wnatc received after
the
iccuanoc of the permit for
unite where Part B of tho permit application in
received by the Agency or UCEPA after November 8, 1~C4.
The requirement for the installation of two or more
lincro
in
thia oubocotion may be satisfied by the
inctallation of a top liner dcaigncd, operated and
constructed of matcriala to prevent the migration of
any oonetitucnt into
auoh
liner during the period such
facility remaino in operation (including any poet-
closure monitoring period), and a lower liner designed,
operated and constructed to prevent the migration of
any constituent through such liner during ouch period.
For the purpose of the preceding sentence, a lower
liner ahall be deemed to satisfy such requirement if it
is conatruoted of at least a 3—foot thick layer of
recompooted clay or other natural material with a
permeability of no morc than
I x
10.! centimeter
per
second. unit on which construction commences after
January 29.
1992.
each lateral expansion of a surface
impoundaent 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.
“Construction commences” is as defined in
35 Ill. Ada. Code 720.1.10 under “existing facility”.
fl.
Liner requirements.
~j
The liner system must include:
,jJ..
A to~liner designed and constructed of
materials (e.g.. a aeomembrane) to
prevent the migration of hazardous
constituents into such liner during the
active life and cost—closure care
period; and
0136-0627
96
jjJ~ A composite bottom liner, consisting of
at least two components.
The upper
component must be desianed and
constructed of materials
(e.g..
a
geomembrane) to prevent the migration of
hazardous constituents into this
component during the active life and
post-closure care period.
The lower
component must be designed and
constructed of materials to minimize the
migration of hazardous constituents if
a
breach in the u~~ercomponent were to
occur.
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 1
x 10~cm/sec.
~j
The liners must comply with subsections
(a) (1)
.
(2)
and
(3) above.
21
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
(LDS).
This
LDS
must be capable
of detecting, collecting and removing leaks of
hazardous constituents at the earliest practicable
time through all areas of the to~liner likely to
be exposed to waste or ).eachate during the active
life and post—closure care period.
The
requirements for a LDS in this subsection are
satisfied by installation of a system that is, at
a minimum:
~j
Constructed with
a bottom slope of one
percent or more
~j
Constructed of granular drainage materials
with a hydraulic conductivity of 1 x i0’
cm/sec or more and a thickness of 12 inches
(30.5 cm~or more; or constructed of
synthetic
or
aeonet drainage materials with a
transinjssjvity of
3 x 10’ in2/sec or more
QJ~.
Constructed of materials that are chemically
resistant to the waste manaaed in the surface
impoundment and the leachate expected to be
generated. and of sufficient strength and
thickness to prevent collapse under the
pressures exerted by overlying wastes and any
0 136-0628
97
waste cover materials or equipment used at
the surface impoundment
P1
Designed and operated to minimize c1og~in~
during the active life and post—closure care
period; and
~
Constructed with sumps and li~idremoval
methods
(e.g... Dumps) of sufficient size to
collect and remove liquids from the
sump
and
prevent liquids from backing u~into the
drainage layer.
Each unit must have its
own
sum~(s). The design of each sump and removal
system must provide a method for measuring
and recording the volume of liquids Dresent
in the sump and of liquids removed.
fl
The owner or oPerator shall collect and remove
Pum~ableliquids in the sumps to minimize the head
on the bottom liner.
il
The owner or operator of a
LDS that
is not located
completely above
the
seasonal high water table
must demonstrate that the operation of the LDS
will not be adverselY affected by the presence of
groundwater.
d)
Subsection
(c) will not apply if the owner or operator
demonstrates to the Agency and the Agency finds for
such surface impoundment, that alternative design and
~operating
practices, together with location
characteristics,
will
j..
.jj.
Will prevent the migration of any hazardous
constituent into the groundwater or surface water
at least as effectively as ouch the liners and
leachate collection and removal systeme-~-specified
in subsection
(c) above;
and
21
Will allow detection of leaks of hazardous
constituents through the top liner at least as
effectively.
e)
The double liner requirement set forth in subsection
(c) may be waived by the Agency for any monofill,
if:
1)
The monofill contains only hazardous wastes from
foundry furnace emission controls or metal casting
molding sand, and such wastes do not contain
constituents which would render the wastes
hazardous
for
reasons
other than the toxicity
characteristic in 35 Ill. Ada. Code 721.124; and
0136-0629
98
2)
Design and location.
A)
Liner,
location and groundwater monitoring.
i)
The monofill has at least one liner for
which there is no evidence that such
liner is leaking.
For the purposes of
this subsection, the term “liner” means
a liner designed, constructed, installed
and operated to prevent hazardous waste
from passing into the liner at any time
during the active life of the facility,
or a liner designed, constructed,
installed and operated to prevent
hazardous waste from migrating beyond
the liner to adjacent subsurface soil,
groundwater or surface water at any time
during the active life of the facility.
In the case of any surface impoundment
which has been exempted from the
requirements of subsection
(c) on the
basis of a liner designed, constructed,
installed and operated to prevent
hazardous waste from passing beyond the
liner,
at the closure of such
impoundment, the owner or operator must
remove or decontaminate all waste
residues, all contaminated liner
material
and
contaminated
soil
to
the
extent practicable.
If all contaminated
soil is not removed or decontaminated,
the owner or operator of such
impoundment will comply with appropriate
post—closure requirements, including but
not limited to groundwater monitoring
and corrective action;
ii)
The monofill
is located more than one-
quarter mile from an underground source
of drinking water
(as that term is
defined in 35 Ill. Ada. Code
702.110
and
iii) The monofill is in compliance with
generally applicable groundwater
monitoring requirements for facilities
with permits or
B)
The owner or operator demonstrates to the
Board that the monofill is located, designed
and operated so as to assure that there will
be no migration of any hazardous constituent
into groundwater or surface water at any
0136-0630
99
future time.
~j
The owner or operator of any replacement surface
imnoundment unit is exempt from subsection
(ci
above
i~i
jJ.
The existing
unit
was constructed in compliance
with the design standards of 35 Ill. Ada. Code
724.321(c).
(di
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
(0)
(1)
(A) (ii and
(0)
(5) of the Resource
Conservation and Recovery Act
(42 U.S.C. 6901
et seq.).
21
There is no reason to believe that the liner is
not functioning as designed.
g)
A surface impoundment must be designed, constructed,
maintained and operated to prevent overtopping
resulting from normal or abnormal operations;
overfilling; wind and wave action; rainfall; run-on;
malfunctions of level controllers, alarms and other
equipment; and human error.
~)
A surface impoundment must have dikes that are
designed, constructed and maintained with sufficient
structural integrity to prevent massive failure of the
dikes.
In ensuring structural integrity,
it must not
be presumed that the liner system will function without
leakage during the active life of the unit.
j)
The Agency will specify in the permit all design and
operating practices that are necessary to ensure that
the requirements of this Section are satisfied.
(Source:
Amended at 16 Ill. Reg.
,
effective
)
Section 724.322
Double-lined Surface Impounamcntsi
xxcmption
from Cubpart ~
Cround-water Protection
Requirements (Rcpca1cd~ActionLeakaae Rate
~j
The
Aaencv shall approve an action leakage rate for
surface impoundment units subiect to Section 724.321(c)
or
(di.
The action leakaae rate is the maximum design
flow rate that the
LDS
can remove without the fluid
head on the bottom liner exceeding
1 foot.
The action
1eaka~erate must include an ade~atesafety margin to
allow for uncertainties in the design
(e.g..
slope.
0136-0631
100
hydraulic conductivity, thickness of drainage
material), construction, operation and location of the
LDS.
waste and leachate characteristics,
likelihood and
amounts of other sources of liquids in the
LDS.
and
proposed
response
actions
(e.g..
the
action
leakage
rate must consider decreases in the flow capacity of
the
system
overtime resulting from siltation and
clogain~,rib layover and creep of synthetic components
of_the system. overburden pressures. etc.).
~
To determine if the action leakaae rate has been
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 stamp must be
calculated weekly during the active life and closure
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).
(Source:
Section repealed at 10 Ill.
Reg.
14119, effective
August 12,
1986;
new Section adopted at 16 Ill. Reg.
effective
)
Section 724.323
Response Actions
~j
The owner or operator of surface impoundment units
subject
to
Section
724.321(c)
or
(di
shall
have
an
approved response action plan before receipt of waste.
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.
~j
If the flow rate into the LDS exceeds the action
leakage rate for any
sum~.
the owner or operator shall:
jj
Notify the Agency in writing of the exceedence
within
7 days of the determination:
21
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
21
Determine to the extent practicable the location,
size and cause of any leak:
ii
Determine whether waste receipt should cease or be
0.136-0632
101
curtailed1 whether any waste should be removed
from the unit for inspection, repairs or controls,
and_whether or not the unit should be closed:
~
Determine
any
other
short-term
and
longer-term
actions to be taken to mitigate or stop any leaks
~.j
Within 30 days after the notification that the
action leakaae rate has been exceeded. submit to
the Aaency 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 leakaae rate.
the owner or operator shall submit to the Agency a
report summarizing the results of any remedial
actions taken and actions planned.
~
To make the leak or remecliation determinations in
subsections
(bi (3).
(4)
and
(5)
above,
the owner or
operator shall:
fl
Either:
~j.. Assess the source of liquids and amounts of
liquids by source
~
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
~j
Assess the seriousness of any leaks in terms
of potential for esca~inainto the
environment: or
21
Document why such assessments are not needed.
(Source:
Added at 16 Ill. Reg.
,
effective
)
Section 724.326
Monitoring and Inspection
a)
During construction and installation, liners
(except in
the case of existing portions of surface impoundments
exempt from Section 724.321(a))
and cover systems
(e.g., membranes,
sheets, or coatings) must be
inspected for uniformity, damage and imperfections
(e.g., holes,
cracks, thin spots or foreign materials).
Immediately after construction or installation:
0 136-0633
102
1)
Synthetic liners and covers must be inspected to
ensure tight seams and joints and the absence of
tears, punctures and blisters; and
2)
Soil—based and admixed liners and covers must be
inspected for imperfections including lenses,
cracks, channels, root holes or other structural
non—uniformities that may cause an increase in the
permeability of that liner or cover.
b)
While a surface impoundment is in operation,
it must be
inspected weekly and after storms to detect evidence of
any of the following:
1)
Deterioration, malfunctions or improper operation
of overtopping control systems;
2)
Sudden drops
in the level of the impoundment’s
contents;
and,
3)
Severe erosion or other signs of deterioration in
dikes or other containment devices.
c)
Prior to the issuance of a permit, and after any
extended period of time (more than six months) during
which the impoundment was not in service, the owner or
operator must shall obtain a certification from a
qualified engineer that the impoundment’s dike,
including that portion of any dike which provides
freeboard, has structural integrity.
The certification
must establish,
in particular,
that the dike:
1)
Will
withstand the stress of the pressure exerted
by the types and amounts of wastes to be placed in
the impoundment; and
2)
Will not fail due to scouring or piping, without
dependence on any liner system included in the
surface impoundment construction.
~
Monitoring of
LDS.
fl..
An owner or operator required to have a
lIDS
under
Section 724.321(c) or
(di
shall record the amount
of liquids removed from each
lIDS
sump at least
once each week during the active life and closure
period.
21
After the final cover
is installed, the amount of
liquids removed from each
lIDS
stamp must be
recorded at least monthly.
If the liquid level in
the
sum~
stays below the pump operating level for
0136-063’~
103
two consecutive months, the
amount
of liquids in
the sumps must be recorded at least auarterly.
If
the liquid level in the sum~stays below the pump
operating level for two consecutive auarters,
the
amount
of
liquids
in
the
aum~s
must
be recorded at
least s~mi-annual1y. If at any time during the.
post-closure care
period
the
pump
operating level
is exceeded at units on auarterly or semi-annual
recording schedules, the owner or ooerator shall
return to monthly recording of amounts of liquids
removed from each
stamp until the liquid level
aaain stays below the ~
operatina level for two
consecutive months.
fl
“Puma
operating level”
is a liquid level proposed
by the owner or
operator
pursuant
to
35
Ill.
Ada.
Code 703
•
203 (b) (5)
and approved by the Agency
based on pump activation level. sump dimensions
and level that avoids backu~into the drainage
layer and minimizes head in the
stamp.
(Source:
Amended at 16 Ill. Reg.
,
effective
)
Section 724.328
Closure and Post—closure Care
a)
At
closure,
the owner or operator must shall:
1)
Remove or decontaminate all waste residues,
contaminated containment system components
(liners, etc.),
contaminated subsoils and
structures and equipment contaminated with waste
and leachate, and manage them as hazardous waste
unless 35 Ill. Ada. Code 721.103(d)
applies; or
2)
Closure in place.
A)
Eliminate free liquids by removing liquid
wastes or solidifying the remaining wastes
and waste residues;
B)
8tablilicc Stabilize remaining wastes to a
bearing capacity sufficient to support final
cover; and
C)
Cover the surface impoundment with a final
cover designed and constructed to:
i)
Provide long-term minimization of the
migration of liquids through the closed
impoundment;
0136-0635
104
ii)
Function with minimum maintenance;
iii) Promote drainage and minimize erosion or
abrasion of the final cover;
iv)
Accommodate settling and subsidence so
that~the cover’s integrity
1s
maintained; and
v)
Have a permeability less than or equal
to the permeability of any bottom liner
system or natural subsoils present.
b)
If some waste residues or contaminated materials are
left in place at final closure, the owner or operator
must shall comply with all post—closure requirements
contained
in
Sections
724.217
through
724.220,
including maintenance and monitoring throughout the
post—closure care period
(specified in the permit under
Section 724.217). The owner or operator must shall:
1)
Maintain the integrity and effectiveness of the
final cover,
including making repairs to the cap
as necessary to correct the effects of settling,
subsidence,
erosion or other events;
21
Maintain and monitor the
LDS
in accordance with
Sections 724.321(c) (2) (Di and
(c)(3)
and
724.326(d). and comply with all other applicable
LDS
requirements of this Part
3
~)
Maintain and monitor the ground-water groundwater
monitoring system and comply with all other
applicable requirements of Subpart F; and
3
~)
Prevent run—on and run—off from eroding or
otherwise damaging the final cover.
C)
Contingent plans.
1)
If an owner or operator plans to close a surface
impoundment in accordance with subsection
(a) (1),
and the impoundment does not comply with the liner
requirements of Section 724.321(a)
and is not
exempt from them in accordance with Section
724.321(b),
then:
A)
The closure plan for the impoundment under
Section 724.212 must include both a plan for
complying with subsection
(a) (1)
and a
contingent plan for complying with subsection
(a) (2)
in case not all contaminated subsoils
0136-0636
105
can
be
practicably
removed
at
closure;
and
B)
The owner or operator must shall prepare a
contingent post—closure plan under Section
724.218 for complying with subsection
(b)
in
case not all contaminated subsoils can be
practicably removed at closure.
2)
The cost estimates calculated under Sections
724.242 and 724.244 for closure and post-closure
care of an impoundment subject to this subsection
must include the cost of complying with the
contingent closure plan and the contingent
post-closure plan,
but are not required to include
the cost of expected closure under subsection
(a) (1).
(Source:
Amended at 16 Ill.
Reg.
,
effective
SUBPART
L:
WASTE
PILES
Section 724.351
Design and Operating Requirements
a)
A waste pile (except for an existing portion of a waste
pile) must have:
1)
A liner that is designed, constructed and
installed to prevent any migration of wastes out
of the pile into the adjacent subsurface soil or
groundwater or surface water at any time during
the active life (including the closure period)
of
the waste pile. The liner may be constructed of
materials that may allow waste to migrate into the
liner itself (but not into the adjacent subsurface
soil or ground-water groundwater or surface water)
during the active life of the facility. The liner
must be:
A)
Constructed
of materials that have
appropriate chemical properties and
sufficient strength and thickness to prevent
failure due to pressure gradients (including
static head and external hydrogeologic
forces), physical contact with the waste or
leachate to which they are exposed, climatic
conditions,
the stress of installation and
the stress of daily operation;
B)
Placed upon a foundation or base capable of
providing support to the liner and resistance
to pressure gradients above and below the
01360637
106
liner to prevent failure of the liner due to
settlement,
compression or uplift; and
C)
Installed to cover all surrounding earth
likely to be in contact with the waste or
leachate; and
2)
A leachate collection and removal system
immediately above the liner that is designed,
constructed, maintained and operated to collect
and remove leachate from the pile. The Agency will
shall specify design and operating conditions in
the permit to ensure that the leachate depth over
the liner does not exceed 30 cm (one foot). The
leachate collection and removal system must be:
A)
Constructed of materials that are:
i)
Chemically reaiotcnt resistant to the
waste managed in the pile and the
leachate expected to be generated; and
ii)
Of sufficient strength and thickness to
prevent collapse under the pressures
exerted by overlying wastes, waste cover
materials and by any equipment used at
the pile; and
B)
Designed and operated to function without
clogging through the scheduled closure of the
waste pile.
b)
The owner or operator will be exempted from the
requirements of paragraph subsection
(a)
above
if the
Board finds,
based on a demonstration by the owner or
operator,
in a variance anu~orsito-opocirio
rulemaking,
grants an adjusted standard pursuant to 35
Ill. Ada. Code 1O6.Sub~artG.
The level of
justification is a demonstration by the owner or
operator that alternate design e~d~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 exomptionad-justed 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
0136-0638
107
the liners and soils present between the pile 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.
~j
The owner or operator of each new waste pile unit on
which construction commences after January 29,
1992,
each lateral expansion of a waste pile
unit
on which
construction commences after July 29.
1992.
and each
reølacement of an existing waste pile unit that is to
commence reuse after July 29.
1992.
shall install two
or more liners and
a leachate collection and removal
system above and between such liners.
“Construction
commences” is as defined in Section
720.110
under
“existing facility”.
.1J
Liners.
Al
The liner system must include:
jj.
A to~liner designed and constructed of
materials (e.g..
a geonieanbrane) to
prevent the migration of hazardous
constituents into such liner during the
active life and post—closure care
period; and
jj)..
A composite bottom liner,
consisting of
at least two components.
The upper
component must be designed and
constructed of materials
(e.g..
a
geomembrane) to prevent the migration of
hazardous constituents into this
component during the active life and
post—closure care period.
The lower
component must be designed and
constructed of materials to minimize the
miaration of hazardous constituents if a
breach in the uo~ercomponent were to
occur.
The lower component must be
constructed of at least
3 feet
(91 cm)
of compacted soil material with a
hvdr~u1icconductivity of no more than
1X10
cm/sec.
~j
The liners must comply with subsections
(a)(1)(A).
(B) and
(C)
above.
0136-0639
108
21
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
Agency will specify desian and operating
conditions in the permit to ensure that the
leachate depth over the liner does not exceed 30
cm (one foot)’.
The leachate collection and
removal system must comply with subsections
(c)(3)(C1 and
(Di
below.
21
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
(lIDS).
This
LDS
must be capable
of detecting.
collecting and removing leaks of
hazardous constituents at the earliest practicable
time through all areas of the top liner likely to
be exposed to waste or leachate during the active
life and post-closure care period.
The
requirements for a LDS in this subsection are
satisfied by installation of a system that is. at
a minimum:
Al
Constructed with a bottom slope of one
percent or more:
~J
Constructed of aranular 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 3X105 m2/sec or more:
~l
Constructed of materials that are chemically
resistant to the waste managed in the waste
nile and
the
leachate expected to be
generated. and of sufficient strength and
thickness to prevent collapse under the
pressures exerted bY overlying wastes, waste
cover materials and equipment used at the
waste pile
~
Designed and operated to minimize clogging
during the active life and post—closure care
period; and
~j
Constructed with sumps and liquid removal
methods (e.g., pumps)
of sufficient size to
01 36-06L~O
109
collect and remove liquids from the sum~and
prevent liquids from backing u~into the
drainage layer.
Each unit must have its
own
suinp(s).
The design of each stamp and removal
system must provide a method for measuring
and recording the volume of liquids present
in the
sum~
and of liquids removed.
j)..
The owner or operator shall collect and remove
pumpable liquids in the
LDS
sum~sto minimize the
head
on
the
bottom
liner.
~j
The owner or operator of
a lIDS that is not located
completely above the seasonal high water table
shall demonstrate that the operation of the
LDS
will not be adversely affected by the presence of
around water.
~
The A~encvshall 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 or operating practices,
toaether with location characteristics:
fl.
Will
prevent the migration of any hazardous
constituent into the around water or surface water
at least as effectively as the liners and leachate
collection and removal systems soecified in
subsection
(ci
above; and
21
Will allow detection of leaks of hazardous
constituents throuah the to~liner at least as
effectively.
~j
Subsection
(ci
above does not
pppy
to monofills that
are aranted a waiver by the Agency in accordance with
Section 724.321(e).
Q
The owner or operator of any replacement waste pile
unit is exempt from subsection
(ci
above if:
fl
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.
0136-061i.1
110
including a top liner desianed, 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 óonstituent
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 mater*al with a permeability of
no more than
1 x 10
cm/sec.
21
There
is no reason to believe that the liner is
not functioning as designed.
e
g)
The owner or operator must shall design, construct,
operate and maintain a run—on control system capable of
preventing flow onto the active portion of the pile
during peak discharge from at least a 25—year storm.
h)
The owner or operator must shall design,
construct,
operate and maintain a run—off management system to
collect and control at least the water volume resulting
from a 24—hour, 25—year storm.
e
j)
Collection and holding facilities
(e.g.
tanks or
basins)
associated with run—on and run—off control
systems must be emptied or otherwise managed
expeditiously after storms to maintain design capacity
of the system.
~)
If the pile contains any particulate matter which may
be subject to wind dispersal, the owner or operator
must shall cover or otherwise manage the pile to
control wind dispersal.
g
~)
The Agency will shall specify in the permit all design
and operating practices that are necessary to ensure
that the requirements of this ocotion Section are
satisfied.
(Source:
Amended at 16 111. Reg.
,
effective
)
Section 724.352
Double-lined Pilcos
~
from Cubp
Fi
Cround—watcr Protection Requirements
(Repealed)
Action Leakage Rate
0136- 06L~2
111
~j
The Agency shall a~~rovean action leakage rate for
surface im~oundaentunits subject to Section 724.351(c)
or
(di.
The action leakage rate is the maximum desictn
flow rate that the
lIDS
can remove without the fluid
head on the bottom liner exceeding
1 foot.
The action
leakaae rate must include an adeauate safety margin to
allow for uncertainties in the design (e.g..
slope.
hydraulic conductivity, thickness of drainage
material).
construction. operation and location of the
LDS.
waste and leachate characteristics,
likelihood and
amounts of other sources of liquids in the
lIDS
and
proposed response actions
(e.a.. the action leakage
rate must consider decreases in the flow capacity of
the system over time resultina from siltation and
clogging, rib layover and creep of synthetic components
of the system, overburden pressures.
etc.).
.~j
To determine if the action leakaae 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 sump.
The averaae daily flow rate for each sump must be
calculated weekly during the active life and closure
period.
(Source:
Section repealed at 10 Ill. Reg.
14119, effective
August 12,
1986;
new Section adopted at 16 Ill. Reg.
effective
)
Section 724.353
in~pco-cion
at
i...incrae
Exemption from
Pnhnr1’-L~
Crouna-water Protection Rcquircmcn’--
(Repealed) Response Action Plan
~j
The owner or operator of waste pile units subject to
Section_724.351(c)
or
(dl
shall have an approved
response action plan before receipt of waste.
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 elan must describe the
actions specified j~subsection
(b)
below.
~j
If the flow rate into the
LDS
exceeds the action
leakage rate for any
stamp, the owner or operator shall:
IL
Notify the Aaency in writing of the exceedence
within
7 days of the determination
21
Submit a preliminary written assessment to the
Ag~ncvwithin 14 days of the determination, as to
the amount of liquids,
likely sources of liquids,
possible location, size and cause of any leaks,
0136 -06L~3
112
and short-term actions taken and planned:
21
Determine to the extent practicable the location.
size and cause of any leak
il
fletermine whether waste receipt should cease or be
curtailed, whether
p~y
waste should be removed
from the unit for inspection.
repairs or controls,
and_whether or not the
unit
should be closed;
.~j.
Determine any other short—term and long—term
actions to be taken to mitigate or stop any leaks:
~
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
lIDS
exceeds the action leakaae rate.
the owner or operator shall submit to the Agency a
report summarizing the results of any remedial
actions taken and actions planned.
gj
To make the leak or remediation determinations in
subsections
(bi (3).
(4) and
(5)
above, the owner or
operator shall:
IL
Either
Al
Assess the source of liquids and amounts of
liquids by source
~j
Conduct a finoerprint. hazardous constituent
or other analyses of the liquids in the LDS
to identify the source of liquids and
~ossib1e location of any leaks.
and the
hazard and mobility of the liquid: and
~l
Assess the seriousness of any leaks
in terms
of potential for escapina into the
environment; or
21
Document why such assessments are not needed.
(Source:
Section repealed at 10 Ill. Reg.
14119, effective
August
12, 1986;
new Section adopted at 16 Ill. Reg.
effective
)
Section 724.354
Monitoring and Inspection
0 136-O6kL
113
a)
During construction or installation, liners (except in
the case of existing portions of piles exempt from
Section 724.351(a))
and cover systems
(e.g.,
membranes,
Sheets or coatings) must be inspected for uniformity,
damage and imperfections
(e.g., holes,
cracks, thin
spots or foreign materials).
Immediately after
construction or installation:
1)
Synthetic liners and covers must be inspected to
ensure tight seams and joints and the absence of
tears, punctures and blisters; and
2)
Soil-based and admixed liners and covers must be
inspected for imperfections including lenses,
cracks,
channels, root holes or other structural
non-uniformities that may cause an increase in the
permeability of the liner or cover.
b)
While a waste pile is in operation,
it must be
inspected weekly and after storms to detect evidence of
any of the following:
1)
Deterioration, malfunctions or improper operation
of run-on and run—off control systems;
2)
Proper functioning of wind dispersal control
systems, where present; or
3)
The presence of leachate in and proper functioning
of leachate collection and removal systems, where
present.
~j
An owner or operator required to have a LDS under
Section 724.351(c) shall record the amount of liquids
removed from each lIDS
sum~
at least once each week
durina the active life and closure period.
(Source:
Amended at 16 Ill. Reg.
,
effective
)
SUBPART N:
LANDFILLS
Section 724.401
Design and Operating Requirements
a)
Any
landfill that is not covered by subsection
(c)
or
35 Ill.
Ada. Code 725.401(a) must have a liner system
for all portions of the landfill (except for existing
portions of such landfill). The liner system must have:
1)
A liner that is designed, constructed and
installed to prevent any migration of wastes out
of the landfill to the adjacent subsurface soil.or
01 36-06~45
114
groundwater or surface water at any time during
the active life (including the closure period)
of
the landfill. The liner must be constructed of
materials that prevent wastes from passing into
the liner during the active life of the facility.
The liner must be:
A)
Constructed of materials that have
appropriate chemical properties and
sufficient strength and thickness to prevent
failure due to pressure gradients (including
static head and external hydrogeologic
forces), physical contact with the waste or
leachate
to which they are exposed, climatic
conditions,
the stress of installation and
the stress of daily operation;
B)
Placed upon a foundation or base capable of
providing support to the liner and resistance
to pressure gradients above and below the
liner to prevent failure of the liner due to
settlement,
compression or uplift; and
C)
Installed to cover all surrounding earth
likely to be in contact with the waste or
leachate; and
2)
A leachate collection and removal system
immediately above the liner that is designed,
constructed, maintained and operated to collect
and remove leachate from the landfill. The Agency
will shall specify design and operating conditions
in the permit to ensure that the leachate depth
over the liner does not exceed 30 cm
(one foot).
The leachate collection and removal system must
be:
A)
Constructed of materials that are:
i)
Chemically resistant to the waste
managed in the landfill and the leachate
expected to be generated; and
ii)
Of sufficient strength and thickness to
prevent collapse under the pressures
exerted by overlying wastes, waste cover
materials and by any equipment used at
the landfill; and
B)
Designed and operated to function without
clogging through the scheduled closure of the
landfill.
0136- 06L~6
115
b)
The owner or operator will be exempted from the
requirements of subsection
(a)
above if the Board
finds, based on a demonstration by the owner or
operator,
in a variance and/or site-specific
ruicmaking,
grants an adjusted standard pursuant to 35
Ill. Ada. Code 106.Subpart G.
The level of
justification is a demonstration by the owner or
operator that alternative design ei~4~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 exemption adjusted 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
landfill 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.
c)
The owner or operator of each new landfill, each new
ianutii.i. unit
~
an
Oxisciny
z~ioiiit~y,
caan
rcp.u~iuemcnt
of an existing landfill unit and each lateral expansion
of an existing landfill unit, must install two or more
liners and a leachato collection system above and
between the liners. The liners and lcaohate collection
systems must protect human health and the environment.
This subsection applies with respect to all waste
received after issuance of the Dermit for
units
where
Ayunuy ur
~
~rter uovemnor
c,
~
....e
ruguirement
for
the
installation
of
two
or
more
liners
in
this
subsection
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 dosigned, operated and
constructed to prevent the migration of any constituent
through such liner during ouoh 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 rooompaoted clay or
0I36-061~7
Part B of the ~~it
application ic ~~ivcd
by the
y.nfln.
-—
a
q
an a
nfl..
—
116
other natural material with a permeability of no more
than 1 x ioZ centimeter per second. unit on which
construction commences after January 29,
1992. each
lateral expansion of a landfill
unit
on which
construction commences after July 29.
1992.
and each
replacement of an existing landfill unit that is to
commence reuse after July29.
1992.
sháll~install two
or more liners and a leachate collection and removal
system above and between such liners.
“Construction
commences”
is as defined in 35
Ill. Ada. Code 720.110
under “existing facility”.
11
Liner requirements.
Al
The liner system must include:
LL
A top liner designed and constructed of
materials
(e.a.~. a geomembrane)
to
prevent the migration of hazardous
constituents into such liner during the
active life and post-closure care
period; and
jj1
A composite bottom liner, consisting of
at least two components.
The upper
component must be designed and
constructed of materials
(e.g.
•
a
geomembrane) to prevent the migration of
hazardous constituents into this
component during the active life and
cost—closure care period.
The lower
component must be designed and
constructed
of
materials
to
minimize
the
migration
of
hazardous
constituents
if
a
breach in the upper component were to
occur.
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
1
X i0~
cm/sec.
~j
The liners must comply with subsections
(a)(1)(A).
(B) and
(C)
above.
21
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 landfill during the
active life and post-closure care period.
The
Agency will specify design and operatina
conditions in the permit to ensure that the
0136-06148
117
leachate depth over the liner does not exceed 30
cm (one foot).
The leachate collection and
removal system must comply with subsections
(c)(3)(C)
and
(Di below.
21
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
(lIDS).
This lIDS must be capable
of detectina.
collectina. and removing leaks of
hazardous constituents at the earliest practicable
time throuah all areas of the to~liner likely to
be exoosed to waste or leachate during the active
life and post-closure care period.
The
requirements for a lIDS in this subsection are
satisfied by installation of
a system that is. at
a minimum:
Al
Constructed with a bottom slope of one
percent or more
~j
Constructed of aranular 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 drainaae materials with a
transmjssivjty of
3 X 10~m2/sec or more
~j
Constructed of materials that are chemically
resistant to the waste managed in the
landfill and the leachate expected to be
aenerated. and of sufficient strenath and
thickness to prevent collapse under the
pressures exerted by overlying wastes, waste
cover materials and equipment used at the
landfill
Qj
Designed and operated to minimize cloczaing
during the active life and post-closure care
period; and
~
Constructed with swaps and liquid removal
methods
(e.g.. DumPs)
of sufficient size to
collect and remove liquids from the swap and
prevent liquids from backing up into the
drainaae layer.
Each
unit
must have its
own
swap(s).
The design of each
sum~
and removal
system must provide a method for measuring
and recording the volume of liquids present
in the swap and of liquids removed.
0136-06149
118
.41
The owner or operator shall collect and remove
pumpable liquids in the
lIDS
sumps to minimize the
head on the bottom liner.
~1
The owner or operator of a
lIDS
that is not located
completely above the seasonal high water tab1e~
shall demonstrate that
the
operation of the
lIDS
will not be adversely affected by the presence of
ground water.
d)
Subsection
(c) will not apply if the owner or operator
demonstrates to the Agency, and the Agency finds for
such landfill, that alternative design a~4~
operating
practices, together with location characteristics, will
fl
Will~preventthe migration of any hazardous
constituent into the groundwater or surface water
at least as effectively as ouch ~g
liners and
leachate collection and removal systems, specified
in subsection
(c)
above; and
21
Will allow detection of leaks of hazardous
constituents through the top liner at least as
effectively.
e)
The double lincr requirement Agency shall not require a
double liner as set forth in subsection
(c) be waived
by the Agency for any monofill,
if:
1)
The monofill contains only hazardous wastes from
foundry furnace emission controls or metal casting
molding sand,
and such wastes do not contain
constituents which would render the wastes
hazardous for reasons other than the toxicity
characteristics in 35 Ill. Ada. Code 721.124, with
USEPA hazardous waste numbers D004 through D017;
and
2)
No migration demonstration.
A)
Design and location requirements.
i)
The monofill has at least one liner for
which there is no evidence that such
liner is leaking.
ii)
The monofill is located more than
one—quarter mile from an underground
source of drinking water
(as that term
is defined in 35 Ill. Ada. Code 702.110.
0136-0650
119
iii) The monofill
is in compliance with
generally applicable groundwater
monitoring requirements for facilities
with RCRA permits; or
B)
The owner or operator demonstrates to the
Board that the monofill is located, designed
and operated so as to assure that there will
be no migration of any hazardous constituent
into groundwater or surface water at any
future time.
fi
The owner or operator of any replacement landfill unit
is exemPt from subsection
(C)
above if:
IL
The existina unit was constructed in compliance
with the design standards of 35 Ill. Ada. Code
724.401(c).
(di and
(e). as amended in R86-l.
at
10 Ill.
Req.
14119. effective Auaust 12.
1986;
and
BOARD NOTE:
The cited subsections
implemented the design standards of sections
3004(o) (1) (A) (i) and
(0)
(5)
of the Resource
Conservation and Recovery Act
(42 U.S.C.
6901
et sea.).
21
There is no reason to believe that the liner is
not functioning as designed.
g)
The owner or operator must shall design, construct,
operate and maintain a run—on control system capable of
preventing flow onto the active portion of the landfill
during peak discharge from at least a 25—year storm.
~)
The owner or operator must shall design, construct,
operate and maintain a run—off management system to
collect and control at least the water volume resulting
from a 24 hour,
25—year storm.
j)
Collection and holding facilities
(e.g., tanks or
basins) associated with run—on and run—off control
systems must be emptied or otherwise managed
expeditiously after storms to maintain design capacity
of the system.
~)
If the landfill.contains any particulate matter which
may be subject to wind dispersal, the owner or operator
must shall cover or otherwise manage the landfill to
control wind dispersal.
~)
The Agency will shall specify in the permit all design
and operating practices that are necessary to ensure
01 36-065
1
120
that the requirements of this Section are satisfied.
(Source:
Amended at
16 Ill. Reg.
,
effective
Section 724.402
Double-lined Landfills,
Exemption
~rf~m
~u~part ri
Croünd water Protection
Rcquiremanto
(Repealed)
Action Leakage Rate
~1
The Agency shall approve an action leakaae rate for
landfill units subject to Section 724.401(c) or
(d).
The action leakaae rate is the maximum design flow rate
that the lIDS can remove without the fluid head on the
bottom liner exceeding 1 foot.
The action leakage rate
must include an adequate safety margin to allow for
uncertainties in the design
(e.g., slope, hydraulic
conductivity, thickness of drainage material),
construction, operation and location of the LDS. waste
and leachate characteristics,
likelihood and amounts of
other sources of liquids in the lIDS,
and proposed
response actions
te.g.. the action leakaae rate must
consider decreases in the flow capacity of the system
over time resulting from siltation and clogging, rib
layover and creep of synthetic components of the
system, overburden pressures.
etc.).
ki
To determine if the action leakaae 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 ~er 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 p different
freauency pursuant to Section 724.403(c) (2).
(Source:
Section repealed at 10 Ill.
Reg.
14119, effective
August 12,
1986;
new Section adopted at 16 Ill. Reg.
effective
)
Section 724.403
Monitoring and Inspection
a)
During construction or installation,
liners (except in
the case of existing portions of landfills exempt from
Section 724.401(a))
and cover systems
(e.g., membranes,
sheets or coatings) must be inspected for uniformity,
damage and imperfections
(e.g.,
holes,
cracks, thin
spots or foreign materials). Immediately after
construction or installation:
1)
Synthetic liners and covers must be inspected to
0136-0652
121
ensure tight seams and joints and the absence of
tears, punctures or blisters; and
2)
Soil—based and admixed liners and covers must be
inspected for imperfections including lenses,
cracks, channels, root holes or other structural
non—uniformities that may cause an increase in the
permeability of the liner or cover.
b)
While
a landfill is
in operation, it must be inspected
weekly and after storms to detect evidence of any of
the following:
1)
Deterioration, malfunctions or improper operation
of run—on and run—off control systems;
2)
Proper functioning of wind dispersal control
systems, where present; and
3)
The presence of leachate in and proper functioning
of leachate collection and removal systems, where
present.
~j
Monitoring of LDS.
IL
An
owner
or
operator
required
to
have
a
lIDS
under
Section 724.401(c)
or
(d) shall record the amount
of liquids removed from each
LDS
swap at least
once each week during the active life and closure
period.
21
After the final cover
is installed, the amount of
liquids removed from each
lIDS
sum~must be
recorded at least monthly.
If the liquid level in
the swap stays below the pump operating level for
two consecutive months, the amount of liquids in
the swans must be recorded at least quarterly.
If
the liquid level in the sumo stays below
the
pump
operatina level for two consecutive quarters, the
amount of liquids in the sum~smust be recorded at
least semi-annually.
If at any time during the
post-closure care period the pump operatina level
is exceeded at units on ~arterly
or semi—annual
recording schedules. the owner or operator shall
return to monthly recording of amounts of liquids
removed from each swap until the liquid level
again stays below the pump operating level for two
consecutive months.
fl
“Pump operating level” is a liquid level proDosed
by the owner or operator pursuant to 35 Ill. Ada.
Code 703.207(b) (1) (E)
and approved by the Aaency
0136-0653
122
based on ~um~ activation level.
swan dimensions
and level that avoids backup into the drainaae
layer and minimizes bead in the sump.
(Source:
Amended at 16 Ill. Reg.
,
effective
)
Section 724.404
Response Actions
~j
The owner or operator of landfill units subject to
Section 724.401(c)
or
(d)
shall have an approved
response action plan before receipt of waste.
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 ~1an must describe the
actions specified in subsection
(b) below.
~
If the flow rate into the
LDS
exceeds the action
leakage rate for any
swn~,
the owner or operator shall:
IL
Notify the Aaencv in writing of the exceedence
within
7 days of the determination
21
Submit a oreliminarv written assessment to the
Agency within 14 dave 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
fl.
Determine to the extent practicable the location.
size and cause of any leak
j).
Determine whether waste receipt should cease or be
curtailed, whether any waste should be removed
from the unit for inspection. reDairs or controls.
and whether or not the unit should be closed
~j
Determine any other short-term and longer—term
actions to be taken to mitigate or stop any leaks;
and
.~1
Within 30 days after the notification that the
action leakage rate has been exceeded. submit to
the_Aaencv the results of the determinations
soecified in subsections
i~b)(3).
(4) and
(5)
above, the results of actions taken,
and actions
planned.
Monthly thereafter, as lona as the flow
rate
in
the
lIDS exceeds the
action
leakage
rate.
the owner or operator shall submit to the Aaency a
report summarizing the results of any remedial
actions taken and actions ~1anned.
0 136-06514
123
~j
To make the leak or remediation determinations in
subsections
(b) (3).
(4)
and
(5) above,
the owner or
operator shall:
IL
Either:
Al
Assess the source of liquids and amounts of
liquids by source
~j
Conduct a finaerprint
hazardous constituent
or other analyses of
the
liquids in the
I~1)S
to identify the source of liquids and
possible location of any leaks,
and the
hazard and mobility of the liquid: and
Qj
Assess the seriousness of any leaks in terms
of potential for escaping into the
environment; or
21
Document why such assessments are not needed.
(Source:
Added at 16
Ill. Reg.
,
effective
)
Section 724.410
Closure and Post—closure Care
a)
At final closure of the landfill or upon closure of any
cell, the owner or operator must shall cover the
landfill or cell with a final cover designed and
constructed to:
1)
Provide long-term minimization of migration of
liquids through the closed landfill;
2)
Function with minimum maintenance;
3)
Promote drainage and minimize erosion or abrasion
of the cover;
4)
Accommodate settling and subsidence so that the
cover’s integrity is maintained; and
5)
Have a permeability less than or equal to the
permeability of any bottom liner system or natural
subsoils present.
b)
After final closure, the owner or operator must shall
comply with all post—closure requirements contained in
Sections 724.217 through 724.220, including maintenance
and monitoring throughout the post—closure care period
(specified in the permit under Section 724.217). The
owner or operator must shall:
0136-0655
124
1)
Maintain the integrity and effectiveness of the
final cover,
including making repairs to the cap
as necessary to correct the effects of settling,
subsidence, erosion or other events;
2)
Continue to operate the leachate collection and
removal system until leachate is no longer
detected;
_~I
Maintain and monitor the
LDS
in accordance with
Sections 724.401(c) (3) (Di and
(ci (4) and
724.403(c).
and comply with all other applicable
LDS
requirements of this Part
3
.4)
Maintain and monitor the ground—water groundwater
monitoring system and comply with all other
applicable requirements of Subpart F;
4
~)
Prevent run—on and run—off from eroding or
otherwise damaging the final cover; and
~)
Protect and maintain surveyed benchmarks used in
complying with Section 724.409.
(Source:
Amended at 16 Ill.
Reg.
,
effective
)
SUBPART
W:
DRIP
PADS
Section 724.673
Design and operating requirements
a)
Drip pads must:
1)
Not be constructed of earthen materials, wood or
asphalt, unless the asphalt is structurally
supported;
2)
Be sloped to free-drain to the associated
collection system treated wood drippage, rain,
other waters, or solutions of drippage and water
or other wastes;
3)
Have a curb or berm around the perimeter;
4)
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;
and
0
36-0656
125
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 istaken.
The
requirement that existing drip cads 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.
5)
Be of sufficient structural strength and thickness
to prevent failure due to physical contact,
climatic conditions, the stress of installation
and the stress of daily operations,
e.g.,
variable
and moving loads such as vehicle traffic, movement
of wood,
etc.
BOARD
NOTE:
In judging the structural integrity
requirement of this subsection, the Agency should
generally consider applicable standards
established by professional organizations
generally recognized by the industry, including
ACI 318 or
ASTM
C94, incorporated by reference in
35
Ill. Ada. Code 720.111.
b)
A new drip pad or an existing drip pad, after the
deadline established in Section 724.671(b), must have:
1)
A synthetic liner installed below the drip pad
that is designed, constructed and installed to
prevent leakage from the drip pad into the
adjacent subsurface soil or groundwater or surface
water at any time during the active life
(including the closure period)
of the drip pad.
The liner must be constructed of materials that
will prevent waste from being absorbed into the
liner and to prevent releases into the adjacent
subsurface soil or groundwater or surface water
during the active life of the facility.
The liner
must be:
A)
Constructed of materials that have
appropriate chemical properties and
sufficient strength and thickness to prevent
failure due to pressure gradients (including
static head and external hydrogeologic
forces), physical contact with the waste or
drip pad leakage to which they are exposed,
climatic conditions, the stress of
01360657
126
installation and the stress of daily
operation (including stresses from vehicular
traffic on the drip pad);
B)
Placed upon a foundation or base capable of
providing support to the liner and resistance
to pressure gradients above and below the
liner to prevent failure of the liner due to
settlement, compression or uplift; and
C)
Installed to cover all surrounding earth that
could come in contact with the waste or
leakage; and
2)
A leakage detection system immediately above the
liner that is designed, constructed, maintained
and operated to detect leakage from the drip pad.
The leakage detection system must be:
A)
Constructed of materials that are:
i)
Chemically resistant to the waste
managed in the drip pad and the leakage
that might be generated; and
ii)
Of sufficient strength and thickness to
prevent collapse under the pressures
exerted by overlaying materials and by
any equipment used at the drip pad; and
B)
Designed and operated to function without
clogging through the scheduled closure of the
drip pad; and
C)
Designed so that it will detect the failure
of the drip pad or the presence of a release
of hazardous waste or accumulated
liquid
at
the earliest practicable time.
c)
Drip pads must be maintained such that they remain free
of cracks, gaps,
corrosion or other deterioration that
could cause hazardous waste to be released from the
drip pad.
BOARD NOTE: See subsection
(in) for remedial action
required if deterioration or leakage is detected.
d)
The drip pad and associated collection system must be
designed and operated to convey, drain and collect
liquid resulting from drippage or precipitation in
order to prevent run—off.
Q!36065~
127
e)
Unless the drip pad is protected by a structure, as
described in Section 724.670(b), the owner or operator
shall design,
construct,
operate and maintain a run—on
control system capable of preventing flow onto the drip
pad during peak discharge from at least a 24-hour,
25-
year storm, unless the system has sufficient excess
capacity to contain any run-on that might enter the
system.
f)
Unless the drip pad is protected by a structure or
cover, as described in Section 724.670(b), the owner or
operator shall design, construct,
operate and maintain
a run—off management system to collect and control at
least the water volume resulting from a 24—hour, 25—
year storm.
g)
The drip pad must be evaluated to determine that it
meets the requirements of subsections
(a) through
(f).
The owner or operator shall obtain a statement from an
independent, qualified, registered professional
engineer certifying that the drip pad design meets the
requirements of this Section.
h)
Drippage and accumulated precipitation must be removed
from the associated collection system as necessary to
prevent overflow onto the drip pad.
i)
The drip pad surface must be cleaned thoroughly at
least once every seven days such that accumulated
residues of hazardous waste or other materials are
removed, using an appropriate and effective cleaning
technique,
including but not limited to, rinsing,
washing with detergents or other appropriate solvents,
or steam cleaning.
The owner or operator shall
document,
in the facility’s operating log, the date and
time of each cleaning and the cleaning procedure used.
j)
Drip pads must be operated and maintained in a manner
to minimize tracking of hazardous waste or hazardous
waste constituents off the drip pad as a result of
activities by personnel or equipment.
k)
After being removed from the treatment vessel, treated
wood from pressure and non-pressure processes must be
held on the drip pad until drippage has ceased.
The
owner or operator shall maintain records sufficient to
document that all treated wood is held on the pad,
in
accordance with this Section, following treatment.
1)
Collection and holding units associated with run—on and
run—off control systems must be emptied or otherwise
managed as soon as possible after storms to maintain
01360659
128
design capacity of the system.
m)
Throughout the active life of the drip pad and as
specified in the permit,
if the owner or operator
detects a condition that could lead to or has caused a
release of hazardous waste, the condition must be
repaired within a reasonably prompt period of time
following discovery,
in accordance with the following
procedures:
1)
Upon detection of a condition that may have caused
or has caused a release of hazardous waste
(e.g.,
upon detection of. leakage in
the
leak detection
system), the owner or operator shall:
A)
Enter a record of the discovery in the
facility operating log;
B)
Immediately remove from service the portion
of the drip pad affected by the condition;
C)
Determine what steps must be taken to repair
the drip pad, clean up any leakage from below
the drip pad, and establish a schedule for
accomplishing the clean up and repairs;
D)
Within 24 hours after discovery of the
condition, notify the Agency of the condition
and, within 10 working days, provide written
notice to the Agency with a description of
the steps that will be taken to repair the
drip pad and clean up any leakage, and the
schedule for accomplishing this work.
2)
The Agency shall:
review the information
submitted; make a determination regarding whether
the pad must be removed from service completely or
partially until repairs and clean up are complete;
and notify the owner or operator of the
determination and the underlying rationale in
writing.
3)
Upon completing all repairs and clean up, the
owner or operator shall notify the Agency in
writing and provide a certification,
signed by an
independent, qualified, registered professional
engineer, that the repairs and clean up have been
completed according to the written plan submitted
in accordance with subsection
(m) (1) (D)
above.
n)
If a permit is necessary, the Agency shall specify in
the permit all design and operating practices that are
0136-0660
129
necessary to ensure that the requirements of this
Section are satisfied.
o)
The owner or operator shall maintain, as part of the
facility operating log, documentation of past operating
and waste handling practices.
This must include
identification of preservative formulations used in the
past,
a description of drippage management practices
and
a description of treated wood storage and handling
practices.
(Source:
Amended at 16 Ill. Reg.
,
effective
)
0136-0661
130
TITLE
35:
ENVIRONMENTAL
PROTECTION
SUBTITLE G:
WASTE DISPOSAL
CHAPTER
I:
POLLUTION CONTROL
BOARD
SUBCHAPTER
c:
HAZARDOUS
WASTE
OPERATING
REQUIREMENTS
PART
725
INTERIM
STATUS
STANDARDS
FOR
OWNERS AND
OPERATORS
OF HAZARDOUS
WASTE
TREATMENT,
STORAGE
AND
DISPOSAL FACILITIES
SUBPART A:
GENERAL
PROVISIONS
Section
725.101
Purpose, Scope and Applicability
725.104
Imminent Hazard Action
SUBPART
B:
GENERAL
FACILITY
STANDARDS
Section
725.110
Applicability
725.111
USEPA
Identification
Number
725.112
Required Notices
725.113
General Waste Analysis
725.114
Security
725.115
General Inspection Requirements
725.116
Personnel Training
725.117
General Requirements for Ignitable, Reactive or
Incompatible Wastes
725.118
Location Standards
725.119
Construction Quality Assurance Program
SUBPART
C:
PREPAREDNESS
AND
PREVENTION
Section
725. 130
Applicability
725. 131
Maintenance and Operation of Facility
725.132
Required Equipment
725.133
Testing and Maintenance of Equipment
725.134
Access to Communications or Alarm System
725.135
Required Aisle Space
725.137
Arrangements with Local Authorities
SUBPART
D:
CONTINGENCY
PLAN
AND EMERGENCY PROCEDURES
Section
725.150
Applicability
725.151
Purpose and Implementation of Contingency Plan
725.152
Content of Contingency Plan
725.153
Copies of Contingency Plan
725.154
Amendment of Contingency Plan
725.155
Emergency Coordinator
725.156
Emergency Procedures
SUBPART
E:
MANIFEST
SYSTEM,
RECORDKEEPING
AND
REPORTING
Section
725.170
Applicability
725.171
Use of Manifest System
0 136-0662
131
Manifest Discrepancies
Operating Record
Availability, Retention and Disposition of Records
Annual Report
Unmanifested Waste Report
Additional Reports
SUBPART
F:
GROUNDWATER MONITORING
Applicability
Groundwater Monitoring System
Sampling and Analysis
Preparation, Evaluation and Response
Recordkeeping and Reporting
SUBPART
G:
CLOSURE
AND
POST-CLOSURE
Applicability
Closure Performance Standard
Closure Plan; Amendment of Plan
Closure; Time Allowed for Closure
Disposal or Decontamination of Equipment, Structures
and Soils
Certification of Closure
Survey Plat
Post-closure Care and Use of Property
Post-closure Plan; Amendment of Plan
Post-Closure Notices
Certification of Completion of Post—Closure Care
SUBPART H:
FINANCIAL REQUIREMENTS
Applicability
Definitions of Terms as Used in this Subpart
Cost Estimate for Closure
Financial Assurance for Closure
Cost Estimate for Post—closure Care
Financial Assurance for Post—closure Monitoring and
Maintenance
Use of a Mechanism for Financial Assurance of Both
Closure and Post-closure Care
725.247
Liability Requirements
725.248
Incapacity of Owners or Operators, Guarantors or
Financial Institutions
725.251
Promulgation of Forms
(Repealed)
SUBPART
I:
USE
AND
MANAGEMENT
OF CONTAINERS
Section
725.270
Applicability
725.271
Condition of Containers
725.272
Compatibility of Waste with Container
725.273
Management of Containers
0135-0663
725.172
725.173
725.174
725.175
725.176
725.177
Section
725.190
725.191
725.192
725.193
725.194
Section
725.210
725.211
725. 212
725.213
725. 214
725. 2 15
725.216
725.217
725.218
725.219
725.220
Section
725.240
725.241
725.242
725.243
725.244
725.245
725.246
132
725.274
725.276
725.277
Section
725.290
725.291
725.292
725.293
725.294
725.295
725.296
725.297
725.298
725.299
725.300
725.301
Section
725.320
725.321
725.322
725.323
725.324
725.325
725.326
725.328
725.329
725.330
Section
725.350
725.351
725.352
725.353
725.354
725.355
725.356
725.357
725.358
725.359
725.360
Inspections
Special Requirements for Ignitable or Reactive Waste
Special Requirements for Incompatible Wastes
SUBPART
3:
TANK
SYSTEMS
Applicability
Assessment of Existing
Tank
System’s Integrity
Design and Installation of New Tank Systems or
Components
Containment and Detection of Releases
General Operating Requirements
Inspections
Response to leaks or spills and disposition of Tank
Systems
Closure and Post—Closure Care
Special Requirements for Ignitable or Reactive Waste
Special Requirements for Incompatible Wastes
Waste Analysis and Trial Tests
Generators of 100 to 1000 kg/mo.
SUBPART
K:
SURFACE IMPOUNDMENTS
Applicability
Design and Operating Requirements
Ccncrzil Opcrating Rcquircaentø Action Leakage Rate
Containmcnt ~yc3tcmResponse Actions
Containment System
Waste Analysis and Trial Tests
Monitoring and Inspections
Closure and Post—Closure Care
Special Requirements for Ignitable or Reactive Waste
Special Requirements for Incompatible Wastes
SUBPART
L:
WASTE PILES
Applicability
Protection from Wind
Waste Analysis
Containment
Design and Operating Requirements
Action Leakage Rates
Special Requirements for Ignitable or Reactive Waste
Special Requirements for Incompatible Wastes
Closure and Post—Closure Care
Response Actions
Monitoring and Inspection
Section
725.370
725. 372
SUBPART
M:
LAND
.
TREATMENT
Applicability
General Operating Requirements
0 I36-06&L~
133
725. 373
725.376
725.378
725.379
725.380
725.381
725.382
Waste Analysis
Food Chain Crops
Unsaturated Zone
(Zone of Aeration) Monitoring
Recordkeeping
Closure and Post—closure
Special Requirements for Ignitable or Reactive Waste
Special Requirements for Incompatible Wastes
SUBPART
N:
LANDFILLS
Section
725.400
725. 401
725.402
725.403
725.404
725.409
725. 410
725.412
725. 413
725. 414
725.415
725. 416
Section
725. 440
725. 441
725.445
725.447
725.451
725. 452
Section
725. 470
725. 473
725.475
725.477
725.481
725. 482
725.483
Applicability
General Operating Requirements
Waste Analysis and Trial Tests
Inspections
Closure
Applicability
Design Requirements
Cencrzd Opcrating RcquircJncnta
R~soon~A~tion~
Mr~nitrrrina
~
Tnsr~~~tinn
Action Leakaae Rate
Surveying and Recordkeeping
Closure and Post—Closure
Special Requirements for Ignitable or Reactive Waste
Special Requirements for Incompatible Wastes
Special Requirements for Liquid Wastes
Special Requirements for Containers
Disposal of Small Containers of Hazardous Waste in
Overpacked Drums
(Lab Packs)
SUBPART 0:
INCINERATORS
Applicability
Waste Analysis
General Operating Requirements
Monitoring and Inspection
Closure
Interim Status Incinerators Burning Particular
Hazardous Wastes
SUBPART
P:
THERMAL TREATMENT
Other
Thermal
Treatment
General Operating Requirements
Waste Analysis
Monitoring and Inspections
Closure
Open Burning; Waste Explosives
Interim Status Thermal Treatment Devices Burning
Particular Hazardous Waste
SUBPART Q:
CHEMICAL,
PHYSICAL AND BIOLOGICAL TREATMENT
Section
725.500
725.501
725.502
725.503
725.504
0136-0665
134
725.505
Special Requirements for Ignitable or Reactive Waste
725.506
Special Requirements for Incompatible Wastes
SUBPART
R:
UNDERGROUND
INJECTION
Section
725.53~)
Applicability
SUBPART W:
DRIP PADS
Section
725.540
Applicability
725.541
Assessment of existing drip pad integrity
725.542
Design
and installation of new drip pads
725.543
Design and operating requirements
725.544
Inspections
725.545
Closure
SUBPART
AA:
AIR EMISSION STANDARDS
FOR PROCESS VENTS
Applicability
Definitions
Standards:
Process Vents
Standards:
Closed-vent Systems and Control Devices
Test methods and procedures
Recordkeeping Requirements
SUBPART BB:
AIR EMISSION STANDARDS FOR EQUIPMENT
LEAKS
Applicability
Definitions
Standards:
Standards:
Standards:
Service
Standards:
Sampling Connecting Systems
Standards:
Open—ended Valves or Lines
Standards:
Valves in Gas/Vapor or Light Liquid Service
Standards:
Pumps, Valves, Pressure Relief Devices,
Flanges and Other Connectors
Standards:
Delay of Repair
Standards:
Closed—vent Systems and Control Devices
Percent Leakage Alternative for Valves
Skip Period Alternative for Valves
Test Methods and Procedures
Recordkeeping Requirements
725.Appendix A Recordkeeping Instructions
725.Appendix B EPA Report Form and Instructions (Repealed)
725.Appendix
C
EPA
Interim Primary Drinking Water Standards
725.Appendix
D
Tests for Significance
725.Appendix E Examples of Potentially Incompatible Waste
AUTHORITY:
Implementing Section 22.4 and authorized by Section
Section
725.930
725.931
725.932
725.933
725.934
725.935
Section
725.950
725.951
725.952
725.953
725.954
725.955
725.956
725.957
725.958
725.959
725.960
725.961
725. 962
725.963
725.964
Pumps in Light Liquid Service
Compressors
Pressure Relief Devices in Gas/Vapor
0136-0666
135
27 of the Environmental Protection Act
(Ill. Rev.
Stat.
1991,
ch.
111—1/2, pars.
1022.4 and 1027).
SOURCE:
Adopted in R81—22,
43 PCB 427, at 5 Ill. Reg.
9781,
effective as noted in 35 Ill. Ada. Code 700.106; amended and
codified in RB1—22, 45 PCB 317,
at
6 Ill. Reg.
4828, effective as
noted in 35 Ill.
Ada. Code 700.106; amended inR82-18,
51 PCB
831, at
7 Ill. Reg. 2518, effective February 22,
1983; amended in
R82—19,
53 PCB 131,
at
7 Ill. Reg.
14034, effective October 12,
1983; amended in R84—9, at
9 Ill.
Reg. 11869, effective July 24,
1985; amended in R85-22 at 10 Ill.
Reg. 1085, effective January
2,
1986; amended in R86—1 at 10 Ill. Reg.
14069, effective August
12, 1986;
amended in R86-28 at 11 Ill.
Reg. 6044, effective March
24,
1987; amended in R86—46 at 11 Ill. Reg. 13489, effective
August 4, 1987; amended in R87-5 at 11 Ill. Reg.
19338, effective
November 10,
1987; amended in R87—26 at 12
Ill.
Reg. 2485,
effective January 15,
1988; amended in R87-39 at 12
Ill. Reg.
13027, effective July 29,
1988; amended in R88—16 at 13 Ill. Reg.
437, effective December 28,
1988; amended in R89—1 at 13 Ill.
Reg.
18354,
effective November 13,
1989; amended in R90-2 at
14
Ill. Reg.
14447, effective August 22,
1990; amended in R90—lO at
14 Ill. Reg.
16498, effective September 25,
1990; amended in R90-
11 at 15 Ill.
Reg.
9398, effective June 17, 1991; amended in R91-
1 at 15 Ill. Reg.
14534, effective October
1,
1991;
amended in
R91—13 at 16
Ill.
Reg.
9578, effective June 9,
1992;
amended in
R92—1 at 16
Ill.
Reg.
,
effective
amended in R92-10 at 16 Ill. Reg.
,
effective
SUBPART B:
GENERAL FACILITY STANDARDS
Section 725.113
General Waste Analysis
a)
Waste analysis:
1)
Before an owner or operator treats,
stores or
disposes of any hazardous waste~,or non—hazardous
waste~if applicable under Section 725.213(d), the
owner or operator shall obtain a detailed chemical
and physical analysis of a representative sample
of the waste~. At a minimum, thia the analysis
must contain all the information which must be
known to treat,
store or dispose of the waste in
accordance with tho requiromonto of this Part and
35 Ill.
Adm.
Code
728.
2)
The analysis may include data developed under 35
Ill. Ada. Code 721 and existing published or
documented
data
on
the
hazardous
waste
or
on
waste
generated from similar processes.
BOARD NOTE:
For example, the facility’s
0136-0667
136
record of analyses performed on the waste
before
the
effective
date
of
these
regulations or studies conducted on hazardous
waste generated from processes similar to
that
which
generated
the
waste
to
be
managed
at
the
facility
may
be
include
in~thedata
base required to comply with subsection
(a) (1), above, except as otherwise specified
in 35 Ill. Ada. Code 728.107(b) and
(c).
The
owner
or
operator
of
an
off—site
facility
may
arrange
for
the
generator
of
the
hazardous
waste to supply part or all of the
information
required
by subsection
(a) (1),
above.
If
the
generator
does
not
supply
the
information
and
the
owner
or
operator
chooses
to accept a hazardous waste, the owner or
operator is responsible for obtaining the
information required to comply with this
Section.
3)
The
analysis
must
be
repeated
as
necessary
to
ensure
that
it
is
accurate
and
up
to
date.
At
a
minimum, the analysis must be repeated:
A)
When
the owner or operator is notified, or
has
reason
to
believe,
that
the
process
or
operation generating the hazardous waste,
or
non—hazardous waste if applicable under
Section 725.213(d), has changed; and
B)
For off-site facilities, when the results of
the inspection required in subsection
(a) (4),
below,
indicate that the hazardous waste
received
at
the
facility does not match the
waste designated on the accompanying manifest
or shipping paper.
4)
The owner or operator of an off-site facility
shall inspect and,
if necessary, analyze each
hazardous waste movement received at the facility
to determine whether it matches the identity of
the
waste
specified
on
the
accompanying
manifest
or shipping paper.
b)
The
owner
or
operator
shall develop and follow a
written
waste
analysis
plan
which
describes
the
procedures
which
the
owner
or
operator
will
carry
out
to comply with subsection
(a), above.
The
owner
or
operator shall keep this plan at the facility.
At a
minimum, the plan must specify:
1)
The parameters for which each hazardous waste,
or
0136-0668
137
non-hazardous waste if applicable under Section
725.213(d),
will
be
analyzed
and
the rationale for
the selection of these parameters
(i.e., how
analysis
for
these
parameters
will
provide
sufficient
information
on
the
waste’s
properties
to comply with subsection.~La), above.
2)
The test methods which will be used to test for
these parameters.
3)
The
sampling
method
which
will
be
used
to
obtain
a
representative
sample
of
the
waste
to
be
analyzed.
A
representative
sample
may
be
obtained
using
either:
A)
One of the sampling methods described in 35
Ill. Ada. Code 721.Appendix A or
B)
An equivalent sampling method.
BOARD
NOTE:
See
35
Ill.
Ada.
Code
720.120(c)
for related discussion.
4)
The frequency with which the initial analysis of
the waste will be reviewed or repeated to ensure
that the analysis is accurate and up—to—date.
5)
For off-site facilities, the waste analyses that
hazardous
waste
generators
have
agreed
to
supply.
6)
Where applicable, the methods which will be used
to meet the additional waste analysis requirements
for
specific
waste
management
methods
as
specified
in Sections 725.300,
725.325, 725.352,
725.373,
725.414,
725.441,
725.475,
725.502,
725.934(d)
and 725.963(d),
and 35 Ill. Ada. Code 728.107.
And,
7)
For surface impoundments exempted from land
disposal restrictions under 35 Ill. Ada. Code
728.104(a), the procedures and schedules for:
A)
The
sampling
of
impoundment
contents;
B)
The
analysis
of
test
data;
and,
C)
The annual removal of residues which are not
delisted under 35 Ill. Ada. Code 720.122 or
which exhibit a characteristic of hazardous
waste, and either:
1)
Do
not
meet
applicable
treatment
0136-0669
138
standards
of
35
Ill.
Ada.
Code
728.Subpart D; or
ii)
Where
no
treatment
standards
have
been
established:
Such residues are
prohibited from land disposal under 35
Ill. Ada. Code 728.132 or 728.139; or
such residues are prohibited from land
disposal under 35 Ill. Ada. Code
728 .133 (f).
c)
For off-site facilities,
the waste analysis plan
required
in
subsection
(b),
above,
must
also
specify
the procedures which will be used to inspect and,
if
necessary,
analyze each movement of hazardous waste
received at the facility to ensure that it matches the
identity of the waste designated on the accompanying
manifest or shipping paper.
At a minimum, the plan
must describe:
1)
The procedures which will be used to determine the
identity of each movement of waste managed at the
facility; and
2)
The sampling method which will be used to obtain a
representative sample of the waste to be
identified,
if the identification method includes
sampling.
(Source:
Amended at 16 Ill. Reg.
,
effective
)
Section 725.115
General Inspection Requirements
a)
The owner or operator shall inspect the facility for
malfunctions and deterioration, operator errors and
discharges which may be causing
-—
or may lead to
——
the conditions listed below.
The owner or operator
shall conduct these inspections often enough to
identify
problems
in
time
to
correct
them
before
they
harm
human health or the environment.
1)
Release
of
hazardous
waste
constituents
to
the
environment or
2)
A threat to human health.
b)
Written schedule.
1)
The owner or operator shall develop and follow a
written schedule for inspecting all monitoring
equipment, safety
and
emergency
equipment,
0136-0670
139
security devices and operating and structural
equipment
(such
as
dikes
and
sump
pumps)
that
are
important to preventing, detecting or responding
to environmental or human health hazards.
2)
The
owner
or.operator..shall
keep
this
schedule.at
the facility.
3)
The schedule must identify the
types
of
problems
(e.g., malfunctions or deterioration) which are to
be
looked
for
during
the
inspection
(e.g.,
inoperative sump pump,
leaking fitting, eroding
dike,
etc.).
4)
The
frequency
of
inspection
may
vary
for
the
items
on
the
schedule.
However,
it
should
be
based
on
the
rate
of
poociblo
deterioration
of
the
equipment and the probability of an environmental
or human health incident if the deterioration~
e~
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 must include the items and
frequencies called for in Sections 725.274,
725.293,
725.295, 725.i26, 725.360,
725.378,
725.404.
725.447,
725.477,
725.503,
725.933,
725.952,
725.953
and 725.958, where applicable.
c)
The owner or operator shall remedy any deterioration or
malfunction of equipment or structure which the
inspection reveals on a schedule which ensures that the
problem does not lead to an environmental or human
health hazard.
Where
a
hazard
is
imminent
or
has
already occurred, remedial action must be taken
immediately.
d)
The
owner
or
operator
shall
record
inspections
in an
inspection
log
or summary.
The owner or operator shall
keep these records for at least three years from the
date of inspection.
At a minimum, these records must
include the date and time of the inspection, the name
of the inspector,
a notation of the observations made
and
the
date
and
nature
of
any
repairs
or
other
remedial actions.
(Source:
Amended at 16 Ill. Reg.
,
effective
Section 725.119
Construction Quality Assurance Proaram
~j
CQA program.
0136-0671
140
A construction auality assurance (CQA) program is
_~_~.redfor all surface impoundment, waste pile
and
~1andf ill
units
that
are
required
to
comply
with Sections 725.321(a), 725.354 and 725.401(a).
The
~rograa
must ensure
that
the constructed unit
meets or ~xceQ~s all desian criteria and
specifications in this
Part.
The
proaram
must be
developed and implemented under the direction of a
CQA_officer who is a registered professional
enaineer.
21
The
COA
~roaram
must address the following
physical components. where applicable:
~I
Foundations
~
Dikes
Qi
Low-permeability soil liners
~
Geomembranes (flexible membrane liners)
~
Leachate collection and removal systems and
leak detection systems; and
fi
Final cover systems.
~j
Written CQA plan.
Before construction begins on a unit
subiect to the
CQA
program under subsection
(a)
above,
the owner or operator shall develop a written CQA plan.
The plan must identify steps that will be used to
monitor and document the quality of materials and the
condition and manner of their installation.
The CQA
plan must include:
fl
Identification of applicable units and a
description of how they will be constructed.
21
Identification
of
key
personnel
in
the
development
and
im~lementatjonof the
CQA
olan. and COA
officer aualifications.
21
A description of inspection and sampling
activities for all
unit
components identified in
subsection
(a) (2) above,
including observations
and tests that will be used before. during and
after c”nstruction to ensure that the con~truction
materials and the installed
unit
components meet
the design specifications.
The description must
cover: Sampling size and locations; freauency of
testing; data evaluation procedures; acceptance
and re-jectiori criteria for construction materials
0136-0672
141
Plans for implementing corrective measures; and
data or other information to be recorded and
retained in
the
operating record under Section
725.173.
~
Contents of
.proaram...
fl.
The
COA
program
must
include
observations.
inspections. tests and measurements sufficient to
ensure:
~j
Structural stability and integrity of all
components of the unit identified in
subsection
(a)(2)
above:
~
Proper construction of all components of the
liners.
leachate collection and removal
system.
leak detection sYstem
and
final
cover
system, according to
~ermit
specifications
and aood engineering practices, and proper
installation of all components
(e.g.. ~i~es)
according to design specifications
QJ..
Conformity of all materials used with design
and other material specifications under 35
Ill. Adm. Code 724.321.
724.351 and 724.401.
21
The COA 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 35 Ill. Ada. Code
724.321(c) (1).
724.351(c) (1)
or 724.401(c) (1)
in
the field.
Compliance with the hydraulic
conductivity requirements must be verified by
using in-situ testing on the constructed test
fill.
The test fill requirement is waived where
data are sufficient to show that a constructed
~il
liner meets the hydraulic conductivity
requirements of 35 Ill.
Ada.
Code 724.321(c) (1).
724.354(c) (1) or 724.401(c) (1)
in
the
field.
~.J
Certification.
The owner or operator of units subject
to this Section must submit to the Aaency by certified
mail
or
hand
delivery,
at
least
30
days
prior
to
receiving
waste,
a
certification
signed
by
the
COA
officer that the CQA elan has been successfully carried
out and that the unit meets the requirements of
Sections 725.321(a).
725.354 or 725.401(a).
The owner
or operator may receive waste in the
unit
after 30 days
from the A~ency’sreceipt of the CQA certification
unless the A~encvdetermines in writing that the
0136-0673
142
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
uron reciuest.
~
Final Agency determinations pursuant to this Section
are deemed to be permit denials for ~ur~oses of appeal
to the Board pursuant to Section 40 of the
Environmental Protection Act.
(Source:
Added at 16 Ill.
Reg.
,
effective
)
SUBPART
E:
MANIFEST
SYSTEM,
RECORDKEEPING
AND
REPORTING
Section 725.173
Operating Record
a)
The owner or operator shall keep a written operating
record at the facility.
b)
The following information must be recorded as it
becomes available and maintained in the operating
record until closure of the facility.
1)
A description and the quantity of each hazardous
waste received and the method or methods and date
or dates of its treatment, storage or disposal at
the facility as required by Appendix A;
2)
The location of each hazardous waste within the
facility and the quantity at each location.
For
disposal facilities the location and quantity of
each hazardous waste must be recorded on a map or
diagram of each cell or disposal area.
For all
facilities this information must include cross-
references
to
specific
manifest
document
numbers
if the waste was accompanied by a manifest;
BOARD NOTE:
See Sections 725.219, 725.379
and 725.409 for related requirements.
3)
Records and results of waste analysis and trial
tests performed as specified in Sections 725.113,
725.300,
725.325,
725.352, 725.373,
725.414,
725.441,
725.475,
725.502,
725.934 and 725.963
and 35 Ill. Ada. Code 728.104(a)
and 728.107;
4)
Summary
reports and details of all incidents that
require implementing the contingency plan as
specified in Section 725.156(j);
0136-06Th
143
5)
Records and results of inspections as required by
Sections 725.115(d)
(except these data need be
kept only three years);
6)
Monitoring,
testing or analytical data ~
~corrective action data where required by
Sub~art-F
~
Sections 725.119. 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)
aii4 ~
725.964;
BOARD NOTE:
As required by Section 725.194,
monitoring data at disposal facilities must
be kept throughout the post-closure period.
7)
All closure cost estimates under Section 725.242
and, for disposal facilities,
all post—closure
cost estimates under Section 725.244;
8)
Records of the quantities (and date of placement)
for each shipment of hazardous waste placed in
land disposal units under an extension of the
effective date of any land disposal restriction
granted pursuant to 35 Ill.
Ada. Code 728
• 105,
a
petition pursuant to 35 Ill. Ada. Code 728.106 or
a certification under 35 Ill. Ada. Code 728.108,
and the applicable notice required of a generator
under
35 Ill. Ada.
Code 728.107(a);
9)
For
an
off-site
treatment
facility,
a copy of the
notice, and the certification and demonstration,
if applicable,
required of the generator or the
owner or operator under 35 Ill. Ada. Code 728.107
or 728.108;
10)
For an on-site treatment facility, the information
contained
in
the
notice
(except
the
manifest
number), and the certification and demonstration,
if applicable, required of the generator or the
owner or operator under 35 Ill. Ada. Code 728.107
or 728.108;
11)
For an off-site land disposal facility,
a copy of
the notice, and the certification and
demonstration,
if applicable,
required of the
generator or the owner or operator of a treatment
facility under 35 Ill. Ada. Code 728.107 or
728.108, whichever is applicable; and
12)
For an on—site land disposal facility, the
0136-0675
144
information contained in the notice required of
the generator or owner or operator of a treatment
facility under 35 Ill. Ada. Code 728.107, except
for the manifest number, and the certification and
demonstration,
if applicable,
required under 35
Ill. Ada. Code 728.108,-whichever is ---applicable.
13)
For an off—site storage facility, a copy of the
notice,
and
the
certification
and
demonstration
if
applicable, required of the generator or the owner
or
operator
under
35 Ill. Ada. Code 728.107 or
728.108; and,
14)
For an on-site storage facility, the information
contained in the notice
(except the manifest
number),
and the certification and demonstration
if applicable, required of the generator or the
owner or operator under 35 Ill. Ada.
Code 728.107
or 728.108.
(Source:
Amended at 16 Iii. Reg.
,
effective
)
SUBPART
K:
SURFACE
IMPOUNDMENTS
Section 725.321
Design and Operating Requirements
a)
Thc owncr or opcrator of a ourface impoundmcnt muot
4n~~z1~i11
two or morc lincro and
lcaohatc
--‘‘~‘-~“
oy3tem in accordanoc with 35 Ill. Ada. Code 724.321(o),
with rcopcot to each new unit, replaocmcnt of an
oxioting unit,
or lateral eupanaion of an exioting unit
that io within thc arca identificd in thc Part A permit
application, and with rcapcot to waote
rcocived
bcginning
May
C,
1~C5.
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 Iii. Adm. Code
724
•
321(c). unless exempted
under 35 Iii. Ada, Code 724.321(d).
(e) or
(f).
“Construction commences”
is as defined in 35 Ill. Ada.
Code 720.110 under “existing facility.”
b)
The owner or operator of each unit referred to in
subsection
(a) muat shall notify the Agency at least
sixty days prior to receiving waste. The owner or
0136-0676
145
operator of each facility submitting notice muot shall
file a Part B application within six months of the
receipt of such notice.
c)
Cuboeotion
(a) will not apply if thc owner or operator
dcmonotrateo to the Agency and
the
Agency
finda
for
ouch ourfaoc impoundacnt, that alternative dcoign and
operating practicca,
togcthcr with location
characteriotico, will prcvcnt the migration of any
hatardous oonotitucnt into the groundwater or aurtaoe
water at leaat ao effcctivcly ac ouch linera and
leachatc collection ayotcma. The owner or oPerator of
any replacement surface impoundment unit is exempt from
subsection
(a)
above
if:
~
The existing unit was constructed in compliance
with the design standards of
35 Ill. Adm. Code
724.321(c).
(d)
and
(e), as amended in R86—l.
at
10 Ill. Rea.
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 sea.).
21
There
is no reason to believe that the liner is
not functioning as designed.
d)
The double liner requirement Aaencv shall not reauire a
double liner as set forth in subsection
(a) may be
waived by thc Agency for any monofill,
if:
1)
The monofill contains only hazardous wastes from
foundry furnace emission controls or metal casting
molding sand, and such wastes do not contain
constituents which would render the wastes
hazardous
for
reasons other than the toxicity.
characteristic in 35 Ill. Ada. Code 721.124, with
USEPA hazardous waste numbers D004 through D017;
and
2)
No migration demonstration.
A)
Design and location requirements.
i)
The monofill has at least one liner for
which there is no evidence that such
liner is leaking. For the purposes of
this subsection the term “liner” means a
liner designed, constructed,
installed
and operated to prevent hazardous waste
0136-0677
146
from passing into the liner at any time
during the active life of the facility,
or a liner designed, constructed,
installed
and operated to prevent
hazardous waste from migrating beyond
the liner -to adjacent subsurface soil,
groundwater or surface water at any time
during the active life of the facility.
In the case of any surface impoundment
which has been exempted from the
requirements of subsection
(a)., of a
liner designed, constructed, installed
and operated to prevent hazardous waste
from passing beyond the liner,
at the
closure of such impoundment the owner or
operator muat shall remove or
decontaminate all waste residues, all
contaminated liner material and
contaminated soil to the extent
practicable. If all contaminated soil is
not removed or decontaminated, the owner
or operator of such impoundment
muot
shall comply with appropriate
post-closure requirements, including but
not limited to groundwater monitoring
and corrective action~
ii)
The monofill is located more than
one—quarter mile from an underground
source of drinking water
(as that term
is defined in 35 Ill. Ada. Code
702.110); and
iii) The monofill is in compliance with
generally applicable groundwater
monitoring requirements for facilities
with RCRA permits; or,
B)
The owner or operator demonstrates to the
Board that the monofill is located, designed
and operated so as to assure that there will
be
no
migration
of
any
hazardous
constituent
into
groundwater
or
surface
water
at
any
future time.
e)
In the case of any unit in which the liner and leachate
collection system ~ae have been installed pursuant to
the requirements of subsection
(a)~,and in good faith
compliance with subsection
(a) and with guidance
documents governing liners and leachate collection
systems under subsection
(a)~,
ne
the Agency shall not
reauire
a liner or leachate collection system which is
0
I 36-0678
147
different from that which was so installed pursuant to
subsection
(a)
will be required for ouch
unit
by the
Agency when issuing the first permit to such facility,
except that the Agency will not be is not precluded
from requiring installation of a new liner when the
Agency finds that any liner installed pursuant to the
requirements of subsection
(a)
is leaking.
A surface impoundment must maintain enouah freeboard to
prevent any overtopping of the dike by overfillina.
wave action or a storm.
Except as orovided in
subsection
(g),
below, there must be at least 60
centimeters
(2
feet)
of freeboard.
gj
A freeboard level less than 60 centimeters
(two feet)
may be maintained if the owner or operator obtains
certification by a qualified engineer that alternate
desian features or operatina clans will, to the best of
the engineer’s knowledae and opinion. prevent
overtopping of the dike.
The certification, along with
a written identification of alternate design features
or operatina plans preventing overtopping, must be
maintained at the facility.
BOARD
NOTE:
Any point source discharge from a
surface impoundment to waters of the State is
subiect to the requirements of Section 12 of the
Environmental Protection Act. Spills may be
subiect to Section
31.
of the Clean Water Act
(33
U.S.C.
125.
et sea.)
~)
Refusal to grant an exemption or waiver, or grant with
conditions,
may be appealed to the Board.
(Source:
Amended at 16
Ill. Reg.
,
effective
Section 725.322
Rcquircmciits Action Leakaae
Rate
a)
A ourfaoc impoundment muot maintain enough freeboard to
prevent any overtopping of the dike by ovorfilling,
wave action or a
citorm.
Exoept
pa
provided in paragraph
(-b), there must be at least 60 centimeters
(2 feet)
-at
freeboard.
b)
A freeboard level
lcac5 than 60 oontimctcro
(two feet)
may be maintained if the owner or oDerator obtaino
certification by a qualified engineer that alternate
de9ign foaturea or operating piano will,
to the be~t-o:
the cnginccr’o knowledge and opinion, prevent
overtopping of the dike.
The oertifioation, along with
01360679
148
.:Lon
a
~
r._GVC1.
~
maintained at the
facility.
BOARD
NOTEi
Any
point source discharge from a
eurfeoc impoundment to watero of the
state
is
—
requiromonto ~
~coti.....
12 of the
Illinois
Environmental
Protection
Apt,
as amended.
i~ni11n
~ir~v
hr~
oubjeot
~n
F~rnfinri
‘~11
nf
t~hr~C~1r~i~
—
A
Water Act.
~
The owner or operator of surface impoundment units
sub-ject to Section 725.321(p)
shall submit a proposed
action leakage rate to the Aaencv when submitting the
notice required under Section 725.321(b).
Within 60
days of receipt of the notification, the Agency 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 Agency before the
original
60 or extended 90 day review periods, the
action leakage rate will be approved as proposed by the
owner or operator.
~j
The Aaency shall approve an action leakage rate for
surface impoundment units sub-lect to Section
725.321(a).
The action leakaae rate is the maximum
desian flow rate that the leak detection system
(LDS)
can remove without the fluid h~adon
the
bottom
liner
exceeding
1 foot,
The action leakage rate must include
an adeauate safety margin to allow for uncertainties in
the design
(e.g..
slope, hydraulic conductivity.
thickness of drainage material),
construction.
operation and location of the LDS. waste and leachate
characteristics,
likelihood and amounts of other
sources of liquids in the LDS and proposed response
actions (e.g.. the action ieakaae rate must consider
decreases in the flow capacity of
the
system over time
resulting from siltation and cloagina. rib layover and
creep of synthetic components of the system.. overburden
pressures, etc.).
~j
To determine if the action leakaae 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 averaae daily
flow rate (aallons ~er acre per day) for each
sump.
The average daily flow rate for each sum~must be
calculated weekly during the active life and closure
period and,
if the unit is closed in accordance with
Section 725.328(a) (2). monthly during the post—closure
care period, unless the Agency approves a different
01360680
149
freauencv pursuant to Section
725.326(h).
~
Final
Agency
determinations
pursuant
to
this
Section
are deemed to be permit denials for purposes of arpeal
to the Board pursuant to Section 40 of the
Environmental
Protection
Act.
(Source:
Amended at 16
Ill. Reg.
,
effective
)
Section 725.323
Containment Cyatom Response Actions
A11 oartncn
a~n~e0
must nave
a
rn-otcotivo
cover,
auan
ao
grass,
shale
or
rock
to
minimi~o wind
and
water
erosion
and
to
preserve
their otructural integrity.
~j
The
owner
or
operator
of
surface
impoundment
units
subiect to Section 725.321(a)
shall submit a response
action ~1an to the Agency when submitting the proposed
action leakaae rate under Section 725.322.
The
response action elan must set forth the actions to be
taken
if the action leakaae rate has been exceeded.
At
a minimum, the response action plan must describe the
actions specified
in subsection
(b)
below.
~j
If the flow rate into the
LDS
exceeds the action
leakaae
rate
for
any
sump.
the owner or operator shall:
IL
Notify
the Agency in writina of the exceedence
within
7
days
of
the
determination
ZL
Submit a preliminary written assessment to the
Aaency
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
~J.
Determine
to the extent practicable the location.
size and cause of pny leak
41
Determine whether waste receiot 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
51
~ermine
any
other
short-term
and
lonaer-term
actions to be taken to mitigate or stop any leaks
~j
Within 30 days after the notification that the
action
leakage
rate
has
been
exceeded.
submit
to
the Agency the results of the determinations
0136_0681
150
specified
in
subsections
(b) (3).
(4)
and
(5)
above,
the results of actions taken,
and actions
planned.
?4onthly
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
report summarizing the results of any remed±al
actions taken and actions planned.
gj
To make the leak or remediation determinations in
subsections
(b)(3).
(4)
and
(5)
above, the owner or
operator
shall:
11.
Either:
~j
Assess
the
source
of
liquids
and
amounts
of
liquids by source
~j
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
~j
Assess the seriousness of any leaks in terms
of potential for escaping into the
environment; or
21
Document why such assessments are not needed.
~J
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.
(Source:
Amended at 16 Ill. Reg.
,
effective
)
Section
725.324
Containment
System
All earthen dikes must have
a
protective
cover,
such as arass.
shale
or
rock
to
minimize wind and water erosion and to preserve
their
structural
integrity.
BOARD
NOTE:
This Section is derived from 40
CFR
265.223. which
was inadvertently repealed at 57 Fed. Rea. 3486. January 29.
1992.
(Source:
Added
at
16
Ill.
Reg.
,
effective
)
Section 725.326
Monitoring and Inspections
0136-0682
151
~j
The owner or operator must shall inspect:
e
~3~)
The
freeboard
level
at
least once each operating
day to ensure compliance with 4 Section 725.3221
and
~)
The surface impoundment,
including dikes and
vegetation surrounding the dike,
at least once a
week to detect any leaks, deterioration or
failures in the impoundment.
COMMENT
BOARD NOTE:
As required by 4 Section
725.1l5(c)~the owner or operator must shall
remedy any deterioration or malfunction
~te
~
owner or oPerator finds.
~j
LDS.
fl
An
owner or operator required to have
a
LDS
under
Section 725.321(a)
shall record the amount of
liquids removed from each LDS sump at
least
once
each week during the active life and closure
period.
IL
After the final cover
is installed,
the amount of
liquids
removed
from
each
LDS
suinp must be
recorded at least monthly.
If the liquid level
in
the sump stays below the
pump
operatina
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 sum~smust be recorded at
1e~st
semi-annually.
If at any time during the
post-closure care period the rump operatina level
is exceeded at units on ~arterly
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
aaain
stays
below
the
~um~
o~eratina
level
for
two
consecutive months.
~j
“Pump
o~eratinalevel” is
a li~idlevel Proposed
by the owner or operator and a~~rovedby the
Aaencv based on pump activation level, sump
dimensions and level that avoids backup into the
drainage layer and minimizes head in the sum~.
The timing for submission and a~~roval
of the
Proposed
“pump
o~eratinalevel” will be in
accordance
with
Section
725.322(a).
gj
Final
Aaencv
determinations
pursuant
to
this
Section
0136-0683
152
are
deemed
to
be
permit
denials
for
purposes
of
appeal
to
the
Board
pursuant
to
Section
40
of
the
Environmental Protection Act.
(Source:
Amended at 16 Ill. Reg.
,
effective
)
Section 725.328
Closure and Post—closure Care
a)
At closure, the owner or operator shall:
1)
Remove or decontaminate all waste residues,
contaminated
containment
system
components
(liners,
etc.),
contaminated
subsoils
and
structures
and
equipment
contaminated
with
waste
or leachate, and manage them as hazardous waste
unless 35 Ill.
Ada. Code 721.103(d)
applies; or
2)
Close
the
impoundment
and
provide
post-closure
care
for
a
landfill
under
Subpart
G
and
Section
725.410,
including
the
following:
A)
Eliminate free liquids by removing liquid
wastes
or
solidifying
the remaining wastes
and waste residues;
B)
Stabilize remaining wastes to a bearing
capacity
sufficient
to
support
final
cover;
and
C)
Cover the surface impoundment with a final
cover
designed
and
constructed
to:
i)
Provide long-term minimization of the
migration of liquids through the closed
impoundment;
ii)
Function with minimum maintenance;
iii) Promote drainage and minimize erosion or
abrasion of the cover;
iv)
Accommodate settling and subsidence so
that the cover’s integrity is
maintained; and
v)
Have a permeability less than or equal
to
the
permeability
of
any
bottom
liner
system or natural subsoils present.
b)
In addition to the requirements of Subpart G and
Section 725.410, during the post-closure care period
0136-06814
153
the owner or operator of a surface impoundment in which
wastes,
waste residues or contaminated materials remain
after
closure
in
accordance
with
subsection
(a)
(2)
shall:
1)
Maintain the integrity and effectiveness -of the
final cover,
including making repairs to the cover
as necessary to correct the effects of settling,
subsidence, erosion or other events;
21
Maintain and monitor the
LDS
in accordance with 35
Ill._Ada. Code 724.321(c) (2) (D)
and (c)(3)
and
725.326(b) and comply with all other a~~licable
LDS requirements of this Part;
~)
Maintain and monitor the groundwater monitoring
system
and
comply
with
all
other
applicable
requirements
of
Subpart
F;
and
.3
~)
Prevent
run-on
and
run-off
from
eroding
or
damaging the final cover.
(Source:
Amended at 16
Ill. Reg.
,
effective
SUBPART L:
WASTE PILES
Section 725.354
Design and Operating Requirements
The owner or operator of a waste pile is
oubj
oat to the
requirements for liners and lcaohatc collection systems or
equivalent protection provided in 35 Ill. Ada.
Code
724.351, with
reopcct to each new unit,
replacement -of an existing unit,
or
lateral
expansion
of
an
existing
unit
that
is
within
the
area
idcntificd in the Part A permit application,
and with respect to
waste
received
beginning
May
8,
l~C5. each
new waste
pile
on
which construction commences after January 29.
1992. each lateral
expansion of a waste nile unit on which construction commences
after July 29. 1992. and each such replacement of an existing
waste pile unit that is to commence reuse after July 29.
1992,
shall install two or more liners and a leachate collection and
removal
system
above
and
between
such
liners
and
operate
the
leachate collection and removal systems.
in accordance with 35
Ill. Mm
•
Code 724.351(c),
unless exempted under 35 Ill. Ada.
Code 724.351 (d).
(e) or
(f); and shall com~lvwith the ~rocedures
of Section 725.321(b).
“Construction commences” is as defined in
35 Ill.
Ada. Code
720e
110 under “existing facility”.
The owner
or
operator
of
each
unit
referred to in this Section shall notify
the
Aaency
at
least
sixty
days
prior to receiving waste. The
owner or oPerator of each facility submittina notice shall file a
Part B application within six months of the receipt of such
notice.
0136-0685
154
(Source:
Amended at
16 Ill. Reg.
,
effective
)
Section
725.355
Action
Leakage
Rates
~j.
The
-owner
or -operator
of--waste
Dii-e---units
sa~bj-eet
to
Section
725.354 shall submit a proposed action leakage
rate to the Aaency when submittina the notice required
under
Section
725.354.
Within
60 days of receipt of
the notification, the Aaencv will:
Establish an action
leakage rate,
either as orooosed 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 Aaencv before the original
60 or extended 90 day review periods, the action
leakage
rate
will
be
aoproved as proposed by the owner
or operator.
ki
The Agency shall approve an action leakaae rate for
surface impoundment units subject to Section 725.354.
The action leakage rate is the maximum design flow rate
that the
LDS
can remove without the fluid head on the
bottom
liner
exceedina
1. foot.
The action leakage rate
must include an adequate safety margin to allow for
uncertainties in the design (e.g..
slope, hydraulic
conductivity,
thickness of drainage material).
construction, operation and location of the LDS. waste
and leachate characteristics, likelihood and amounts of
other sources of liquids in the LDS. and proposed
response actions
(e.g..
the action leakage rate must
consider decreases in the flow capacity of the
system
over time resulting from siltation and cloaging. rib
layover and creep of synthetic components of the
system, overburden pressures. etc.).
.g~
To determine if the action leakage rate has been
exceeded, the owner or operator shall convert the
weekly flow rate from the monitoring data obtained
under
Section 725.360, to an average daily flow rate
(aallons 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.
~j
Final Agency determinations pursuant to this Section
are deemed to be permit denials for ou~osesof ap~ea1
to the Board pursuant to Section
4.0 of the
Environmental Protection Act.
(Source:
Added at 16 Ill.
Reg.
,
effective
)
Section 725.359
Response Actions
0136-0686
155
~j
The
owner
or
operator
of waste pile units sublect to
Section
725.354
shall
submit
a respons~action plan to
the
Aaencv
when
submitting
the ~rooosed action leakage
rate
under
Section 725.355.
The response action plan
must
set
forth
the actions to be taken if the action
leakaae rate has been exceeded.
At aminimum, the
response action plan must describe the actions
specified in subsection
(b) below,
~J-
If the flow rate into the leak determination system
exceeds the action leakage rate for any
sum~,
the owner
or operator shall:
fl
Notify
the
Aaency
in
writing
of
the
exceedence
within
7 days of the determination
IL
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
fl
Determine to the extent practicable the location.
size and cause of any leak
.41
Determine whether waste receiots 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
,~j
Determine
any
other
short-term
and
longer-term
actions
to
be
taken
to
mitigate
or
stop
any
leaks
~j
Within 30 days after the notification that the
action leakaae rate has been exceeded. submit to
the Agency the results of the determinations
specified in subsections (bU3).
(4) and
(5)
above,
the
results of actions taken,
and actions
planned.
Monthly thereafter.
as lona as the flow
rate_in the
LDS
exceeds the action leakage rate.
the owner or operator shall submit to the Aaency a
report summarizina the results of any remedial
actions
taken
and actions planned.
~j
To make the leak or remediation determinations in
subsections
(bI (3).
(4) and
(5) above,
the owner or
oPerator shall:
il
Either:
~j
Assess
the
source
of
liquids
and
amounts
of
0~~360687
156
liquids
by
sources
~j
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
~j
Assess the seriousness of any leaks in terms
of potential for escaping into the
environment; or
21
Document why
such
assessments
are
not
needed.
~j
Final
Agency
determinations pursuant to this Section
are
deemed
to
be
permit
denials
for
purposes
of
a~~eal
to the Board pursuant to Section 40 of the
Environmental
Protection
Act.
(Source:
Added
at
16
Ill.
Reg.
)
Section 725.360
Monitoring and Inspection
An owner or operator required to have a
LDS
under
Section
725.354
shall record the amount of liquids removed from each LDS
sunip
at
least once each week during the active life and closure period.
(Source:
Added at 16 Ill. Reg.
)
,
effective
SUBPART
N:
LANDFILLS
Section 725.401
Design Requirements
——~——~
install two or
0136-0688
,
effective
a)
The owner or operator of a landfill
~
and loaohatc oollcation systems above and
between
ouch
liners
in
acoordance
with
35
Ill.
Ada.
Code 724.401, with rcopcot to each ncw unit,
~‘ep1aoemont
of
an
existing
unit
or
lateral
expansion
of
an existing unit that is within the area identified in
the Part A permit applioation, and with respect to
waotc reocived beginning May 8,
1985. each new landfill
unit
on
which
construction
commences
after
January
29.
1992, each lateral expansion of a landfill unit
on
which construction commences after July 29.
1992.
and
each replacement of an existing landfill unit that is
to commence reuse after July 29.
1992.
shall install
two or more liners and
a
leachate
collection
and
removal system above and between such liners, and
operate
the
leachate collection and removal systems.
in
accordance with 35 Ill. Ada. Code 724.401(c). unless
157
exempted by 35
Ill. Ada.
Code 724.401(d).
(e)
or
(f).
“Construction
commences”
is
as
defined
in
35
Ill.
Ada.
Code
720.110
under
“existing
facility”.
b)
The owner or operator of each unit referred to in
subsection
(a) must shall notify the Agency at least
sixty days prior to receiving waste. The owner or
operator
of each facility submitting notice must shall
file a Part B application within six months of the
receipt of such notice.
c)
Cubsootion
(a)
will
not
apply
if
thc
owner or operator
demonstrates to the Agency and the Agency finds for
such landfill, that alternative design and operating
practioco,
together with location oharaotoriotioa, will
prevent the migration of any ha~ardouoconstituent into
thr~arnunduptcr or surface water at least as
circctivt~1’~”as
oucn iinera and lcaohato collection
systems. The owner or operator of any replacement
landfill
unit
is
exempt
from
subsection
(a)
above
if:
fl
The existing unit was constructed in compliance
with the design standards of 35 Ill. Ada.
Code
724.401(c).
(d) and
(e). as
amended
in R86-1.
at
10 Iii.
Reg.
14119. effective Auaust 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.).
21
There
is
no
reason
to
believe
that
the
liner
is
not functioning as designed.
d)
The
double
liner
requirement
A~encv shall
not
require
a
double liner as set forth in subsection
(a) may be
waived
by
the
Agency
for
any
monofill,
if:
1)
The
monofill contains only hazardous wastes from
foundry furnace emission controls or metal casting
molding sand, and such wastes
do
waste
does
not
contain constituents which would render the wastes
hazardous for reasons other
the
EP toxicity
characteristics in 35 Ill. Ada. Code
721.124
toxicity characteristic in 35 Ill. Ada. Code
721.124. with hazardous waste number D004 through
D017;
and
2)
Alternative
demonstration.
A)
Liner and location requirements.
0136-0689
158
1)
The
monofill
has
at
least
one liner for
which
there
is
no
evidence that such
liner is leaking÷
.j..
ii)
The monofill is located more than
one—quarter mile from an underground
source of drinking water
(as that term
is defined in 35 Ill. Ada. Code
702.110); and
iii) The monofill is in compliance with
generally applicable groundwater
monitoring requirements for facilities
with
RCRA permits;
or
B)
The owner or operator demonstrates to the
Board
that
the
monofill
is
located,
designed
and operated so as to assure that there will
be
no
migration
of
any hazardous constituent
into
groundwater
e~ ~
surface
water
at
any
future time.
e)
In the case of any unit in which the liner and leachate
collection system hee have been installed pursuant to
the
requirements
of
subsection
(a).,..
and
in
good
faith
compliance with subsection
(a)
~jj~
with guidance
documents
governing
liners
and leachate collection
systems
under
subsection
(a),
~e
the
A~encv shall
not
require a liner or leachate collection system which is
different from that which was so installed pursuant to
subsection
(a) will be required for such unit by the
Agency when issuing the first permit to such facility,
except that the Agency will not be is not precluded
from
requiring
installation
of
a
new
liner
when the.
Agency finds that any liner installed pursuant to the
requirements of subsection
(a)
is leaking.
£1.
The
owner or operator shall design,
construct,
operate
and
maintain
a
run-on
control
system
ca~able
of
preventing
flow onto the active portion of the
landfill
during peak discharge from at least a 25-year storm.
gj..
The owner or operator shall design. construct
operate
and
maintain
a
run-off
management
system
to collect and
control
at
least
the
water
volume
resulting
from
a
24
hour.
25—year storm.
ilL
Collection
and
holding
facilities
(e.g..
tanks
or
basins)
associated
with
run-on
and
run-off
control
systems must be emptied or otherwise managed
expeditiously
after
storms
to
maintain
design
capacity
of
the
system.
0136-0690
159
il
The owner or oDerator of
a
landfill
containing
hazardous waste which is subiect to dispersal bY wind
shall cover or otherwise manaae the landfill so that
wind dispersal of
the
hazardous
waste
is
controlled.
BOARD
NOTE: As reauired
by
Section
725.1-13.
the
waste analysis plan must include analyses needed
to com~lvwith Sections 725.412. 725.413 and
725.414. As required by Section 725.173. the owner
or
operator
shall
place
the
results
of
these
analyses
in
the
o~eratina
record
of
the
facility.
j~)
Refusal
to
grant
an
exemption
or waiver, or grant with
conditions,
may
be
appealed
to
the
Board.
(Source:
Amended at 16 Ill. Reg.
,
effective
Section 725.402
Rate
—
ircincnts Action Leakage
F
—
4
...~e.
.
4
.
--
-
_i
_A_
-—----A-
.
.a
a
a a
during peak dioch
the
aotivc
par
n
of
the
landfill
b)
Tho owner or operator
and maintain a run off
~
...~
I
.~L.
~
~
system to collect and
c)
Collection
and
holding
facilities
(e.g.,
tanks
or
basins)
associated
with
run on and run-off control
systems
must
be
emptied
or
otherwise
managed
cxpcditioualy
aft
of the system.
A__
__i~._.a_._1_
~
~_,‘
—F
J~.___
~
—
I
_~3~.!
I
I
ha~ardouovaotewhioh is oubjcot to diøporcal by wind
must
cover
or
otherwise
manage
the
landfill
go that
wind -áisperaal of
the
hanardouc waste is ountrolled.
BOARD
NOTEi
As
required by Section 725.113, the
waste analysis plan must include analyses needed
to
comply
with
Sections 735.412,
735.413 and
725.414. As
required
by
Caption
725.173,
the
owner
or operator must place the results of
thase
analyses
in
the
operating
record
of
the
facility.
~j
The
owner
or
operator
of
landfill
units
subiect
to
Section
725.401(a)
shall
submit
a
~ro~osed
action
leakage
rate
to
the
Agency
when
submitting
the
notice
0136-0691
—a
~
.1
-
— - -
a
160
required under Section 725.401(b).
Within 60 days of
receipt of the notification, the Agency 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
u~ to
30
days.
If
no
action
is
taken
by-the
A~tencvbefore
the
original
60
or
extended
90
day
review
periods.
the
action
leakage rate will
be
approved
as
proposed by the
owner
or operator.
~j
The Agency shall approve an action leakage rate for
landfill_units sublect to Section 725.401(a).
The
action leakage rate is the
maximum
design
flow
rate
that
the
LDS
can
remove
without
the
fluid
head
on
the
bottom liner exceeding
1 foot.
The action leakage rate
must include an adequate safety margin to allow for
uncertainties
in
the
design
(e.g..
slope,
hydraulic
conductivity, thickness of drainage material).
construction, operation and location of the LDS. waste
and leachate characteristics,
likelihood and amounts of
other
sources
of
liquids
in
the
LDS. and proposed
response
actions
(e.g..
the
action leakage rate must
consider decreases in the flow
capacity
of
the
system
over time resulting from siltation and cloa~ing.rib
layover
and
creep
of
synthetic
components
of
the
system. overburden pressures. etc.).
~j
To
determine
if the action leakaae 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 sum~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)..
.c~j
Final Aaency determinations pursuant to this
Section are deemed to be permit denials for
purposes
of
aP~ea1 to
the Board pursuant to
Section 40 of the Environmental Protection Act.
(Source:
Amended at 16 Ill. Reg.
,
effective
)
Section 725.403
Response Actions
~j
The owner or operator of landfill units subiect
to
Section 725.401(a)
shall submit a response action plan
to
the
Agency
when
submitting
the
øroposed
action
leakage
rate
under
Section
725.402.
The
response
0 136-0692
161
action plan must set forth the actions to be taken if
the action leaka~erate has been exceeded.
At a
minimum, the response action plan must describe the
actions specified in subsection
(b) below.
~j.
If
the
flow
rate
into
the
LDS
exceeds
-the--action
1eaka~e rate
for
any
sump,
the
owner
or
operator
shall:
~J-
Notify the Agency in writing of the exceedence
within_7_dave
of
the
determination;
~J..
Submit
a
preliminary
written
assessment
to
the
A~encv 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
3j~
Determine
to
the
extent
practicable the location.
size
and
cause
of
any
leak
il
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
~j.
Determine
any
other
short—term
and
longer-term
actions
to
be
taken
to
mitigate or stop any leaks
and
~
Within
30
dave after the notification that the
action
leakaae
rate
has
been
exceeded,
submit
to
the
A~encv the
results
of
the
determinations
specified
in
subsections
(b)
(3)’.
(4)
and
(5)
above,
the
results
of
actions
taken,
and
actions
~1anned.
Monthly thereafter, as lona as the flow
rate in the LDS exceeds the action leakage rate,
the owner or operator shall submit
to
the Aaencv a
report summarizing
the
results
of
any
remedial
actions
taken
and
actions
planned.
çj
To
make
the
leak
or
remediation
determinations
in
subsections
(b)
(3)’,
(4)
and
(5)
above,
the
owner
or
operator
shall:
3J.
Either:
~j
Assess
the
source
of
liquids
and
amounts
of
liquids by source
~
Conduct a fingerprint, hazardous constituent
or
other
analyses
of
the
liquids
in
the
IJDS
to identify the source of liquids and
O’1360693
162
possible location of any leaks, and the
hazard
and
mobility
of
the
liquid;
and
~j
Assess the seriousness of any leaks in terms
of
potential
for
escapina
into
the
-environment; or
21
Document
why
such
assessments
are
not
needed.
~j
Final Aaency determinations oursuant 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.
(Source:
Added at 16 Ill. Reg.
,
effective
)
725.404
Monitoring and Inspection
~j
An owner or operator required to have an LDS
under
Section 725.401(a) shall record the amount of liquids
removed
from
each
LDS
sump
at
least
once
each
week
during
the
active
life
and
closure
period.
ki~
After the final cover is installed, the amount of
liguids removed from each LDS
suinp must be recorded at
least
monthly.
If
the
liquid
level
in
the
sump
stave
below
the
pump
operatina
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
~um~
operating
level
for
two
consecutive
quarters,
the
amount
of
liquids
in
the
suinns 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 aaain
stays below the pump operating level for two
consecutive months.
~j
“Pump operating level”
is a liquid level proDosed by
the
owner
or
operator
and
approved
by
the
Agency
based
on Dump activation level.
sum~
dimensions and level
that_avoids
backup
into
the drainage layer and
minimizes
head
in
the
sump.
The
timing
for
submission
and
a~~roval
of the ~ro~osed “Dump operating level”
wil.
be in accordance with Section 725.402(a).
~j.
Final Aaencv determinations pursuant to this
Section
are
deemed
to
be
permit
denials
for
purposes
of
appeal
to
the
Board
pursuant
to
0136-O69!~
163
Section
40
of
the
Environmental
Protection
Act.
(Source:
Added at 16 Ill.
Reg.
,
effective
Section
725.410
Closure
and
Post-closure
a)
-
At final closure of the landfill or upon closure of any
cell,
the owner or operator must shall cover the
landfill or cell with a final cover designed and
constructed to:
1)
Provide
long-term minimization of migration of
liquids
through
the
closed
landfill;
2)
Function
with
minimum
maintenance;
3)
Promote drainage and minimize erosion or abrasion
of
the
cover;
4)
Accommodate
settling
and
subsidence
so
that
the
cover’s integrity is maintained; and
5)
Have a permeability less than or equal to the
permeability of any bottom liner system or natural
subsoils
present.
b)
After
final
closure,
the
owner
or
operator
shall
comply
with
all
post—closure
requirements
contained
in
Section
725.217 through 725.220 including maintenance and
monitoring throughout the post-closure care period. The
owner or operator shall:
1)
Maintain the integrity and effectiveness of the
final
cover,
including
making
repairs
to
the
cover
as necessary to correct the effects of settling,
subsidence,
erosion
or
other
events;
~j.
Maintain and monitor the LDS in accordance with 35
Ill.
Adm.
Code
724.401(c)
(3) (DI
and
(c)(4)
and
Section
725.404(b).
and
comply
with
all
other
applicable
LDS
reauirements
of
this
Part
.2.
~)
Maintain and monitor the gz~ound—watcrgroundwater
monitoring
system
and
comply
with
all
other
applicable
requirements
of
Subpart
F;
a
j)
Prevent
run-on
and
run—off
from
eroding
or
otherwise damaging the final cover; and
4
~)
Protect and maintain surveyed benchmarks used in
0136-0695
164
complying
with
Section
725.409.
(Source:
Amended at
16 Ill. Reg.
,
effective
SUBPART W:
DRIP PADS
Section 725.543
Design and operating requirements
a)
Drip pads must:
1)
Not be constructed of earthen materials, wood or
asphalt,
unless
the
asphalt
is
structurally
supported;
2)
Be
sloped
to
free—drain
to
the
associated
collection
system
treated
wood
drippage, rain,
other waters, or solutions of drippage and water
or other wastes;
3)
Have a curb or berm around the perimeter;
4)
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;
and
BOARD
NOTE:
The requirement that existing drip
pads
be
impermeable.
e.g..
that
drip
Dads
be
sealed,
coated
or
covered
with
an
impermeable
material,
is administratively staved.
The stay
will
remain
in
effect
until
October
30.
1992.
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.
5)
Be of sufficient structural strength and thickness
to
prevent
failure
due
to
physical
contact,
climatic conditions,
the stress of installation
and the stress of daily operations,
e.g., variable
and moving loads such as vehicle traffic, movement
of
wood,
etc.
BOARD
NOTE:
In judging the structural integrity
requirement of
this
subsection,
the
Agency
should
0~36~0696
165
generally
consider
applicable
standards
established by professional organizations
generally
recognized
by
the
industry,
including
ACI
318
or
ASTM
C94,
incorporated
by
reference
in
35
Ill.
Adm.
Code 720.111.
b)
A new drip pad or an existing drip pad, after the
deadline
established
in
Section
725.541(b),
must
have:
1)
A synthetic liner installed below the drip pad
that
is
designed,
constructed
and
installed
to
prevent leakage from the drip pad into the
adjacent
subsurface
soil
or
groundwater
or
surface
water at any time during the active life
(including the closure period) of the drip pad.
The liner must be constructed of materials that
will
prevent
waste
from
being
absorbed
into
the
liner and prevent releases into the adjacent
subsurface
soil
or
groundwater
or
surface
water
during
the
active
life
of
the
facility.
The
liner
must be:
A)
Constructed
of
materials
that
have
appropriate
chemical
properties
and
sufficient
strength
and
thickness
to
prevent
failure
due
to
pressure
gradients
(including
static head and external hydrogeologic
forces),
physical
contact
with
the waste or
drip
pad
leakage
to
which they are exposed,
climatic
conditions,
the
stress
of
installation
and
the
stress
of
daily
operation
(including
stresses
from
vehicular
traffic on the drip pad);
B)
Placed upon a foundation or base capable of
providing
support
to
the
liner
and
resistance
to pressure gradients above and below the
liner
to
prevent
failure
of
the
liner
due
to
settlement,
compression
or
uplift;
and
C)
Installed
to
cover
all
surrounding
earth
that
could
come
in
contact
with
the
waste
or
leakage;
and
2)
A
leakage
detection
system
immediately
above
the
liner that is designed, constructed, maintained
and
operated
to
detect
leakage
from
the
drip
pad.
The
leakage
detection
system
must
be:
A)
Constructed
of
materials
that are:
i)
Chemically resistant to the waste
0136-0697
166
managed in the drip pad and the leakage
that
might
be
generated;
ii)
Designed and operated to function
without
clogging
through
the
scheduled
closure
of
the drip pad; and
iii) Of sufficient strength and thickness to
prevent
collapse
under
the
pressures
exerted by overlaying materials and by
any
equipment used at the drip pad; and
B)
Designed
so
that
it
will
detect
the
failure
of the drip pad or the presence of a release
of
hazardous
waste
or
accumulated
liquid
at
the earliest practicable time.
c)
Drip
pads
must
be
maintained
such
that
they
remain
free
of
cracks,
gaps,
corrosion
or
other deterioration that
could cause hazardous waste to be released from the
drip pad.
BOARD
NOTE:
See
subsection
(m)
for
remedial
action
required
if
deterioration
or
leakage
is
detected.
d)
The drip pad and associated collection system must be
designed
and
operated
to
convey,
drain
and
collect
liquid
resulting
from
drippage
or
precipitation
in
order to prevent run—off.
e)
Unless the drip pad is protected by a structure,
as
described in Section 725.540(b),
the owner or operator
shall design,
construct, operate and maintain a run—on
control system capable of preventing flow onto the drip
pad during peak discharge from at least a 24-hour,
25-
year
storm,
unless
the
system
has
sufficient
excess
capacity
to
contain
any
run-on
that
might
enter
the
system.
f)
Unless the drip pad is protected by a structure or
cover,
as
described
in
Section
725.540(b),
the
owner
or
operator
shall
design,
construct,
operate
and
maintain
a
run—off
management
system
to
collect
and
control
at
least
the
water
volume
resulting
from
a
24-hour
25-
year storm.
g)
The
drip
pad
must
be
evaluated
to
determine
that
it
meets the requirements of subsections
(a) through
(f).
The owner or operator shall obtain a statement from an
independent, qualified,
registered professional
engineer certifying that the drip pad design meets the
requirements
of
this
Section.
0136-0698
167
h)
-Drippage and accumulated precipitation must be removed
from the associated collection system as necessary to
prevent
overflow
onto
the
drip
pad.
i)
The drip pad surface must be cleaned thoroughly at
least
once
every
seven
days
such
that
accuinulated
residues
•of hazardous waste or other materials are
removed, using an appropriate and effective cleaning
technique,
including but not limited to, rinsing,
washing with detergents or other appropriate solvents,
or steam cleaning.
The owner or operator shall
document,
in
the
facility’s
operating
log,
the
date
and
time
of
each
cleaning
and
the
cleaning
procedure.
j)
Drip
pads
must
be
operated
and
maintained
in
a
manner
to minimize tracking of hazardous waste or hazardous
waste constituents off the drip pad as a result
of
activities
by
personnel
or
equipment.
k)
After being removed from the treatment vessel, treated
wood
from
pressure
and
non—pressure
processes
must
be
held on the drip pad until drippage has ceased.
The
owner or operator shall maintain records sufficient to
document that all treated wood is held on the pad,
in
accordance with this Section, following treatment.
1)
Collection and holding units associated with run-on and
run-off control systems must be emptied or otherwise
managed
as
soon
as
possible
after
storms
to
maintain
design
capacity
of
the
system.
m)
Throughout
the
active
life
of
the
drip
pad,
if
the
owner
or
operator
detects
a
condition
that
may
have
caused
or
has
caused
a
release
of
hazardous
waste,
the
condition
must
be
repaired
within
a
reasonably
prompt
period
of
time
following
discovery,
in
accordance
with
the following procedures:
1)
Upon detection of a condition that may have caused
or
has
caused
a
release
of
hazardous
waste
(e.g.,
upon detection of leakage in the leak detection
system), the owner or operator shall:
A)
Enter a record of the discovery in the
facility operating log;
B)
Immediately
remove
from
service
the
portion
of
the
drip
pad
affected
by
the condition;
C)
Determine what steps must be taken to repair
the drip pad, clean up any leakage from below
the drip
pad,
and
establish
a
schedule
for
0136-0699
168
accomplishing
the
clean
up
and
repairs;
D)
Within
24
hours
after
discovery
of
the
condition, notify the Agency of the condition
and, within 10 working days, provide written
notice to the Agency with a -description of
the steps that will be taken to repair the
drip
pad
and
clean
up
any
leakage,
and
the
schedule
for accomplishing this work.
2)
The
Agency
shall:
review the information
submitted; make a determination regarding whether
the
pad
must
be
removed
from
service
completely
or
partially
until
repairs
and
clean
up
are
complete;
and notify the owner or operator of the
determination
and
the
underlying
rationale
in
writing.
3)
Upon
completing
all
repairs
and
clean
up,
the
owner
or
operator shall notify the Agency in
writing
and
provide
a certification, signed by an
independent,
qualified,
registered
professional
engineer, that the repairs and clean up have been
completed
according
to
the
written plan submitted
in
accordance
with
subsection
(in)
(1) (D).
n)
The
owner
or
operator
shall
maintain,
as part of the
facility operating log, documentation of past operating
and waste handling practices.
This must include
identification of preservative formulations used in the
past,
a
description
of
drippage
management
practices
and a description of treated wood storage and handling
practices.
(Source:
Added at 16 Ill. Reg.
,
effective
)
0 136-0700
169
TITLE
35:
ENVIRONMENTAL PROTECTION
SUBTITLE G:
WASTE DISPOSAL
CHAPTER
I:
POLLUTION
CONTROL
BOARD
SUBCHAPTER
c:
HAZARDOUS
WASTE
OPERATING
REQUIREMENTS
-PART
726
STANDARDS
FOR THE
MANAGEMENT
OF
SPECIFIC
HAZARDOUS
WASTE
AND SPECIFIC TYPES OF HAZARDOUS WASTE
MANAGEMENT
FACILITIES
SUBPART
C:
RECYCLABLE
MATERIALS
USED
IN
A
MANNER
CONSTITUTING
DISPOSAL
Section
726.120
Applicability
726.121
Standards applicable to generators and transporters of
materials
used
in
a manner that constitutes disposal
726.122
Standards
applicable
to
storers,
who
are
not
the
ultimate
users,
of
materials
that
are
to
be
used
in
a
manner that constitutes disposal
726.123
Standards applicable to users of materials that are
used
in
a
manner
that
constitutes
disposal
SUBPART
D:
HAZARDOUS WASTE
BURNED
FOR
ENERGY
RECOVERY
Section
726.130
Applicability
(Repealed)
726.131
Prohibitions
(Repealed)
726.132
Standards applicable to generators of hazardous waste
fuel
(Repealed)
726.133
Standards applicable to transporters of hazardous waste
fuel
(Repealed)
726.134
Standards applicable to marketers of hazardous waste
fuel
(Repealed)
726.135
Standards applicable to burners of hazardous waste fuel
(Repealed)
726.136
Conditional exemption for spent materials and by-
products exhibiting
a characteristic of hazardous waste
(Repealed)
SUBPART
E:
USED OIL BURNED FOR ENERGY RECOVERY
Section
726.140
Applicability
726. 141
Prohibitions
726.142
Standards
applicable
to
generators
of
used
oil
burned
for energy recovery
726.143
Standards
applicable
to
marketers
of
used
oil
burned
for
energy
recovery
726.144
Standards
applicable
to
burners
of
used
oil
burned
for
energy recovery
SUBPART
F:
RECYCLABLE MATERIALS UTILIZED FOR PRECIOUS
METAL
RECOVERY
Section
726.170
Applicability
and
requirements
0136-0701
170
Section
726.180
Section
726.200
726.201
726.202
726. 203
726. 204
726.205
726. 206
726. 207
726.208
726.209
726.210
726.211
726. 212
726.219
AUTHORITY:
Implementing
Section
22.4
and
authorized
by
Section
27
of
the
Environmental
Protection
Act
(Ill.
Rev.
Stat.
1991,
ch.
111½, pars.
1022.4 and 1027).
SOURCE:
Adopted in R85-22 at 10 Ill. Reg.
1162, effective
January 2,
1986; amended
in
R86-l
at
10
Ill.
Reg.
14156,
0136-0702
SUBPART G:
SPENT LEAD-ACID
BATTERIES
BEING RECLAIMED
Applicability and requirements
SUBPART. H:
HAZARDOUS
WASTE
BURNED
IN
BOILERS
AND
INDUSTRIAL
FURNACES
Applicability
Management prior to Burning
Permit
standards
for
Burners
Interim
status
standards
for
Burners
Standards
to
control
Organic
Emissions
Standards
to
control
PM
Standards to control Metals Emissions
Standards to control HC1 and Chlorine Gas Emissions
Small quantity On-site Burner Exemption
Low
risk
waste
Exemption
Waiver of DRE trial burn for Boilers
Standards for direct Transfer
Regulation of Residues
Extensions of Time
Tier I and Tier II Feed Rate and Emissions
Screening
Limits
for
Metals
Tier I Feed Rate Screening Limits for Total
Chlorine
Tier II Emission Rate Screening Limits for Free
Chlorine and Hydrogen Chloride
D Reference Air Concentrations
E Risk Specific Doses
F
Stack
Plume
Rise
G Health—Based Limits for Exclusion of Waste-Derived
Residues
Potential PICs for Determination of Exclusion of
Waste-Derived Residues
I Methods Manual for Compliance with BIF Regulations
J
Guideline
on
Air Quality Models
K
Lead-Bearing
Materials
That
May
be
Processed
in
Exempt Lead Smelters
Nickel or Chromium-Bearing Materials that may be
Processed
in
Exempt
Nickel—Chromium
Recovery
Furnaces
Exempt Quantities for Small Quantity Burner
Exemption
726.Appendix A
726.Appendix
B
726.Appendix
C
726.Appendix
726.Appendix
726.Appendix
726.Appendix
726.Appendix H
726.Appendix
726.Appendix
726.Appendix
726.Appendix L
726Table
A
171
effective
August
12,
1986;
amended
in
R87-26
at
12
Ill.
Reg.
2900, effective January 15,
1988;
amended
in R89—l at
13 Ill.
Reg. 18606, effective November 13,
1989; amended in R90-2 at 14
Ill. Reg.
14533, effective August 22,
1990; amended in R90—ll at
15
Ill.
Reg.
9727,
effective
June
17,
1991;
amended
in
R91-13
at
-
16
Ill.
Reg.
9858,
-effective
June
9, -1992;
amended-in--R91—1O at
16
Ill. Reg.
,
effective
SUBPART H:
HAZARDOUS
WASTE
BURNED
IN
BOILERS
AND INDUSTRIAL FURNACES
Section 726.200
Applicability
a)
The regulations of this Subpart apply to hazardous
waste burned or processed in a boiler or industrial
furnace
(BIF)
(as defined in 35 Ill.
Athu. Code 720.110)
irrespective of the purpose of burning or processing,
except
as
provided
by
subsections
(b),
(c),
(d)
and
(f),
below.
In
this
Subpart,
the
term
“burn”
means
burning
for
energy
recovery
or
destruction,
or
processing for materials recovery or as an ingredient.
The emissions standards of Sections 726.204,
726.205,
726.206 and 726.207 apply to facilities operating under
interim status or under a RCRA permit as specified in
Sections 726.202 and 726.203.
uwuw NOTES
rnia provioion
ao-eo
not upp.Ly
to
ooac
ovoncs
pr000rn3ing
ookc
by-produot3
wastoa exhibiting the
toxicity
oharaotcriotio
identified
in
35
Ill.
Adm.
Code
721.124
pending oompletion of a rulemaking propoaed by
U6EPA
on
July
26,
1991
(56
Fed.
flog.
35787).
When
that
rulemaking iD oomtlcte, thio notc will be removed.
b)
The
following
hazardous
wastes
and facilities are not
subject to regulation under this Subpart:
1)
Used oil burned for energy recovery that is also a
hazardous
waste solely because it exhibits a
characteristic of hazardous waste identified in 35
Ill.
Adm.
Code
721.Subpart C.
Such used oil is
subject
to
regulation
under
Subpart
E
rather
than
this Subpart;
2)
Gas recovered from hazardous or solid waste
landfills when such gas is burned for energy
recovery;
3)
Hazardous wastes that are exempt from regulation
under 35 Ill.
Adm.
Code
721.104
and
721.106
(a) (3) (E) through
(H), and hazardous wastes
that are subject to the special requirements for
conditionally exempt small quantity generators
0136-0703
172
under 35 Ill.
Adm.
Code 721.105;
and
4)
Coke ovens,
if the only hazardous waste burned is
USEPA
Hazardous
Waste
No.
K087,
decanter
tank
tar
sludge
from
coking
operations.
c)
Owners
and
operators
of
smelting,
melting
and
refining
furnaces (including pyrometallurgical devices such as
cupolas,
sintering
machines,
roasters
and
foundry
furnaces, but not including cement kilns, aggregate
kilns
or
halogen
acid
furnaces
burning
hazardous
waste)
that
process
hazardous
waste
solely
for
metal
recovery
are conditionally exempt from regulation under this
Subpart,
except
for
Sections
726.201
and
726.212.
1)
To
be
exempt
from Sections 726.202 through
726.211,
an owner or operator of a metal recovery
furnace shall comply with the following
requirements,
except
that
an
owner
or
operator
of
a lead or a nickel-chromium recovery furnace, or a
metal recovery furnace that burns baghouse bags
used to capture metallic dust emitted by steel
manufacturing, shall comply with the requirements
of
subsection
(c)(3),
below:
A)
Provide
a
one-time
written
notice
to
the
Agency
indicating
the
following:
1)
The
owner
or
operator
claims
exemption
under
this
subsection;
ii)
The
hazardous
waste
is
burned
solely
for
metal
recovery
consistent
with
the
provisions of subsection
(c) (2), below;
iii)
The
hazardous
waste
contains
recoverable
levels
of
metals;
and
iv)
The
owner
or
operator
will comply with
the sampling and analysis and
recordkeeping requirements of this
subsection;
B)
Sample and analyze the hazardous waste and
other feedstocks as necessary to coeply with
the
requirements of this subsection
under
procedures specified by Test Methods for
Evaluating
Solid
Waste,
Physical/Chemical
Methods,
SW-846,
incorporated
by
reference
in
35
Ill.
Adm.
Code
720.111
or
alternative
methods
that
meet
or
exceed
the
SW-846
method
performance capabilities.
If SW-846 does not
0136-O7O~4
173
prescribe
a
method
for
a
particular
determination,
the
owner
or
operator
shall
use
the
best available method;
and
C)
Maintain
at
the
facility
for
at
least three
years
records
to
document
compliance
with
the
provisions
of
this subsection including
limits
on
levels of toxic organic
constituents
and
Btu
value
of
the waste, and
levels
of
recoverable metals in the hazardous
waste compared to normal nonhazardous waste
feedstocks.
2)
A hazardous waste meeting either of the following
criteria is not processed solely for metal
recovery:
A)
The hazardous waste has a total concentration
of
organic
compounds
listed
in
35
Ill.
Adm.
Code
721.Appendix
H,
exceeding
500
ppm by
weight, as fired, and so is considered to be
burned
for
destruction.
The
concentration
of
organic compounds in a waste as—generated may
be reduced to the
500
ppm
limit
by
bona
fide
treatment
that
removes
or
destroys
organic
constituents.
Blending for dilution to meet
the
500
ppm
limit
is
prohibited
and
documentation
that
the
waste
has
not
been
impermissibly diluted must be retained in the
records
required
by
subsection
(C)
(1) (C),
above;
or
B)
The
hazardous
waste
has
a
heating
value
of
5,000
Btu/lb
or
more,
as—fired,
and
is
so
considered
to
be
burned
as
fuel.
The
heating
value of a waste as—generated may be reduced
to
below
the
5,000
Btu/lb limit by bona fide
treatment that removes or destroys organic
constituents.
Blending
for
dilution
to
meet
the 5,000 Btu/lb limit is prohibited and
documentation
that
the
waste has not been
impermissibly diluted must be retained in the
records
required by subsection
(c) (1) (C),
above.
3)
To be exempt from Sections 726.202 through
726.211, an owner or operator of a lead or nickel—
chromium recovery furnace,
or a metal recovery
furnace that burns a baghouse bags used to capture
metallic
dusts
emitted
by
steel
manufacturing
must
provide
a
one-time
written
notice
to
the
Agency
identifying each hazardous waste burned and
0 136-0705
174
specifying
whether
the
owner
or
operator
claims
an
exemption for each waste under this subsection or
subsection
(c)
(1),
above.
The
owner
or
operator
shall comply with the requirements of subsection
(c) (1), above,
for those wastes claimed to be
exempt under that subsection and shall comply with
the requirements below for those wastes claimed to
be exempt under this subsection.
A)
The hazardous wastes listed in Appendices K
and L and baghouse bags used to capture
metallic
dusts
emitted
by steel manufacturing
are
exempt
from
the
requirements
of
subsection
(c) (1), above, provided that:
i)
A waste
listed
in
Appendix
K
must
contain recoverable levels of lead.
A
waste listed in Appendix L must contain
recoverable levels of nickel or chromium
and baghouse bags used to capture
metallic dusts emitted by steel
manufacturing must contain recoverable
levels
of
metal;
and
ii)
The waste does not exhibit the Toxicity
Characteristic
of
35
Ill.
Athu.
Code
721.124
for an organic constituent; and
iii) The waste
is- not a hazardous waste
listed
in
35
Ill.
Adm. Code 72l.Subpart
D
because
it
is
listed
for
an
organic
constituent
as
identified
in
35
Ill.
Adm. Code 721.Appendix G; and
iv)
The
owner
or
operator certifies in the
one—time notice that hazardous waste is
burned
under
the
provisions
of
subsection
(c)
(3),
above,
and
that
sampling
and
analysis
will
be
conducted
or
other
information
will
be
obtained
as
necessary
to
ensure
continued
compliance
with
these
requirements.
Sampling
and
analysis
must
be
conducted
according
to
subsection
(C)(1)(B),
above,
and records
to
document
compliance
with
subsection
(c)
(3),
above,
must
be
kept
for
at
least
three years.
B)
The
Agency
may decide on a case-by-case basis
that the toxic organic constituents in a
material listed in Appendix K or L that
contains a total concentration of more than
0 136-0706
175
500 ppm toxic organic compounds listed in 35
Ill.
Adiu.
Code 721.Appendix H may pose a
hazard
to
human
health
and
the
environment
when
burned
in
a
metal
recovery
furnace
exempt from the requirements of this Subpart.
In
that
situation,
after
adequate
notice
and
opportunity
for
comment,
the metal recovery
furnace
will
become
subject
to
the
requirements of this Subpart when burning
that material.
In making the hazard
determination, the Agency shall consider the
following factors:
i)
The concentration and toxicity of
organic constituents in the material;
and
ii)
The level of destruction of toxic
organic constituents provided by the
furnace;
and
iii)
Whether
the
acceptable ambient levels
established
in
Appendices
D or E will be
exceeded for any toxic organic compound
that may be emitted based on dispersion
modeling to predict the maximum annual
average off—site ground level
concentration.
d)
The standards for direct transfer operations under
Section 726.211 apply only to facilities subject to the
permit standards of Section 726.202 or the interim
status
standards
of
Section
726.203.
e)
The
management
standards
for
residues
under
Section
726.212
apply
to
any
BIF
burning
hazardous
waste.
f)
Owners and operators of smelting, melting and refining
furnaces
(including pyrometallurgical devices such as
cupolas,
sintering
machines,
roasters
and
foundry
furnaces)
that
process
hazardous
waste
for
recovery
of
economically
significant
amounts
of
the
precious
metals
gold,
silver,
platinum,
palladium,
iridium,
osmium,
rhodium
or
ruthenium,
or
any
combination
of
these,
are
conditionally
exempt
from
regulation
under
this
Subpart
except
for
Section
726.212.
To
be
exempt
from
Sections
726.202
through
726.211
an
owner
or
operator
shall:
1)
Provide a one-time written notice to the Agency
indicating
the
following:
A)
The
owner
or
operator
claims
exemption
under
0136-0707
176
this
e~ection;
B)
The hazardous waste
is
burned
for
legitimate
recovery of precious metal; and
C)
The
owner
or
operator
will
comply
with the
sampling
and
analysis
and
recordkeeping
requirements of this e~ection~
2)
Sample
and
analyze
the
hazardous
waste
as
necessary
to
document
that
the
waste
is
burned
for
recovery
of
economically
significant
amounts
of
precious
metal
using
procedures
specified
by
Test
Methods for Evaluating Solid Waste,
Physical/Chemical
Methods,
SW-846,
incorporated
by
reference
in
35
Ill.
Adm.
Code
720.111
or
alternative
methods
that
meet
or
exceed
the
SW-846
method
performance
capabilities.
If
SW—846
does
not prescribe a method for a particular
determination,
the
owner
or
operator
shall
use
the
best available method; and
3)
Maintain
at
the
facility
for
at
least three years
records
to
document
that
all
hazardous
wastes
burned
are
burned
for
recovery
of
economically
significant
amounts
of
precious
metal.
g)
Abbreviations
and
definitions.
The
following
definitions and abbreviations are used in this Subpart:
“APCS”
means
air
pollution
control system.
“BIF”
means
boiler
or
industrial furnace.
“Carcinogenic metals” means arsenic, beryllium,
cadmium
and
chromium.
“CO” means carbon monoxide.
“Continuous
monitor”
is
a
monitor
which
continuously
samples
the
regulated
parameter
without
interruption,
and
evaluates
the
detector
response
at
least
once
each
15
seconds,
and
computes and records the average value at least
every
60
seconds.
“DRE”
means
destruction
or
removal
efficiency.
“Cu
m”
means
cubic
meters.
“E”
means
“ten
to
the”.
For
example,
“XE—Y”
means
“X
times
ten
to
the
—Y
power”.
0 136-0708
177
“Feed rates” are measured as specified in Section
726.202(e) (6).
“Good
engineering
practice
stack
height”
is
as
defined
by
40
CFR
51.100(u),
incorporated by
reference
in
35
Ill.
Adm.
Code
720.111.
“HC”
means
hydrocarbon.
“I4e~
MCi”
means
hydrogen
chloride
gas.
“Hourly
rolling
average”
means
the
arithmetic
mean
of
the
60
most
recent
1—minute
average
values
recorded
by
the
continuous monitoring system.
“K” means Kelvin.
“kVA”
means
kilovolt
amperes.
“MEl” means maximum exposed individual.
“MEl
location”
means
the
point
with
the
maximum
annual average off—site (unless on—site is
required)
ground
level
concentration.
“Noncarcinogenic metals” means antimony, barium,
lead, mercury, thallium and silver.
“One hour block average” means the arithmetic mean
of the one minute averages recorded during the 60—
minute period beginning at one minute after the
beginning of preceding clock hour
“PlC” means product of incomplete combustion.
“PM” means particulate matter.
“POHC”
means principal organic hazardous
constituent.
“ppmv” means parts per million by volume.
“QA/QC” means quality assurance and quality
control.
“Rolling
average
for
the
selected
averaging
period”
means
the
arithmetic
mean
of
one
hour
block
averages
for
the
averaging
period.
“RAC”
means
reference
air
concentration,
the
acceptable ambient level for the noncarcinogenic
metals for purposes of this Subpart.
RACs are
0136-0709
178
specified in Appendix D.
“RSD”
means
risk—specific
dose,
the
acceptable
ambient level for the carcinogenic metals for
purposes of this Subpart.
RSDS are specified in
Appendix E.
“SSU”
means
“Saybolt
Seconds
Universal”,
a
unit
of
viscosity
measured
by
ASTM
D88
or
D2161,
incorporated
by
reference
in
35
Ill.
Adm.
Code
720.111.
“TCLP
test”
means
the
toxicity
characteristic
leaching
procedure
of
35
Ill.
Adm.
Code 721.124.
“TESH”
means
terrain—adjusted
effective
stack
height
(in meters).
“Tier
I”.
See
Section
726.206(b).
“Tier II”.
See Section 726.206(c).
“Tier III”.
See Section 726.206(d).
“Toxicity
equivalence”
is
estimated,
pursuant
to
Section 726.204(e),
using “Procedures for
Estimating
the
Toxicity
Equivalence of Chlorinated
Dibenzo-p-Dioxin
and
Dibenzofuran
Congeners”
in
Appendix I
(“eye”).
“ug”
means
microgram.
(Source:
Amended at 16
Ill.
Reg.
,
effective
)
0136-07 10
179
TITLE
35:
ENVIRONMENTAL
PROTECTION
SUBTITLE
G:
WASTE
DISPOSAL
CHAPTER
I:
POLLUTION
CONTROL
BOARD
SUBCHAPTER
c:
HAZARDOUS
WASTE OPERATING
REQUIREMENTS
PART
728
LAND
DISPOSAL RESTRICTIONS
SUBPART
A:
GENERAL
Purpose, Scope and Applicability
Definitions
Dilution
Prohibited
as
a
Substitute
for
Treatment
Treatment Surface Impoundment Exemption
Procedures
for
case—by—case
Extensions
to
an
Effective
Date
Petitions
to
Allow
Land
Disposal
of
a
Waste
Prohibited
under Subpart C
728.107
Waste
Analysis
and
Recordkeeping
728.108
Landfill and Surface Impoundment Disposal Restrictions
(Repealed)
728.109
Special Rules for Characteristic Wastes
SUBPART
B:
SCHEDULE
FOR
LAND
DISPOSAL PROHIBITION
AND
ESTABLISHMENT OF
TREATMENT STANDARDS
First
Third
Second
Third
Third Third
Newly Listed Wastes
SUBPART
C:
PROHIBITION
ON
LAND
DISPOSAL
Waste
Specific
Prohibitions
--
Solvent
Wastes
Waste Specific Prohibitions
--
Dioxin-Containing Wastes
Waste Specific Prohibitions
——
California List Wastes
Waste Specific Prohibitions
--
First Third Wastes
Waste
Specific
Prohibitions
-—
Second Third Wastes
Waste
Specific
Prohibitions
-—
Third
Third
Wastes
Statutory
Prohibitions
SUBPART
D:
TREATMENT
STANDARDS
Section
728.140
Applicability of Treatment Standards
728.141
Treatment
Standards
expressed
as
Concentrations
in
Waste
Extract
728.142
Treatment
Standards
expressed
as
Specified
Technologies
728.143
Treatment
Standards
expressed
as
Waste
Concentrations
728.144
Adjustment
of
Treatment
Standard
Section
728. 101
728.102
728.103
728.104
728.105
728.106
Section
728.110
728. 111
728.112
728
.
113
Section
728.130
728.131
728.132
728.133
728. 134
728.135
728.139
0136-0711
180
SUBPART
E:
PROHIBITIONS
ON STORAGE
Section
728.150
Prohibitions
on
Storage
of
Restricted
Wastes
728.Appendix
A
Toxicity
Characteristic
Leaching
Procedure
(TCLP)
728.Appendix
B
Treatment
Standards
(As
concentrations
in
the
Treatment Residual Extract)
C
List
of
Halogenated
Organic
Compounds
D
Organometallic
Lab
Packs
E
Organic
Lab
Packs
F
Technologies
to
Achieve
Deactivation
of
Characteristics
G Federal Effective Dates
H National Capacity
LDR
Variances for UIC Wastes
I EP Toxicity Test Method and Structural Integrity
Test
A
Constituent Concentrations in Waste Extract
(CCWE)
B
Constituent
Concentrations
in
Wastes
(CCW)
C
Technology
Codes
and
Description
of
Technology-
Based
Standards
Technology-Based
Standards
by
RCRA
Waste
Code
Standards
for
Radioactive
Mixed
Waste
Wastes Excluded from
CCW
Treatment
Standards
AUTHORITY:
Implementing Section 22.4
and
authorized
by
Section
27
of
the
Environmental
Protection
Act
(Ill.
Rev.
Stat.
1991,
ch.
111½,
pars.
1022.4
and
1027).
SOURCE:
Adopted in R87-5 at 11 Ill. Reg.
19354, effective
November 12,
1987;
amended in R87-39 at 12 Ill. Reg.
13046,
effective July 29,
1988; amended in R89—l at 13
Ill.
Reg.
18403,
effective November 13,
1989; amended in R89-9 at 14
Ill.
Reg.
6232,
effective
April
16,
1990;
amended
in
R90—2
at
14
Ill.
Reg.
14470,
effective
August
22,
1990;
amended in R90—lO at
14 Ill.
Reg.
16508,
effective
September
25,
1990;
amended
in
R90-11
at
15
Ill.
Reg.
9462,
effective
June
17,
1991;
amended in R90—ll at 15
Ill.
Reg.
11937,
effective
August
12,
1991;
amendment withdrawn
at
15
Ill.
Reg.
14716,
October
11,
1991;
amended
in
R9l—13
at
16
Ill. Reg.
9619, effective June 9, 1992;
amended in R92—lO at
16
Ill. Reg.
,
effective
SUBPART
A:
GENERAL
Section
728.103
Dilution Prohibited as a Substitute for
Treatment
a)
Except
as
provided
in
subsection
(b),
no
generator,
transporter, handler or owner or operator of a
treatment,
storage
or
disposal
facility
shall in any
way dilute a restricted waste or the residual from
treatment of a restricted waste as a substitute for
0136-0712
728
.Appendix
728 .Appendix
728
.Appendix
728.Appendix
728.Appendix
728.Appendix
728 .Appendix
728
.
Table
728.Table
728.Table
728.Table D
728.Table E
728.Table H
181
adequate
treatment
to
achieve
compliance
with
Subpart
D,
to
circumvent
the
effective
date
of
a
prohibition
in
Subpart
C, to otherwise avoid a prohibition in Subpart
C.
b)
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.
Adin.
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 reactive cyanide wastewater or
nonwastewater.
(Source:
Amended at 16 Ill. Reg.
,
effective
)
SUBPART
C:
PROHIBITION
ON
LAND
DISPOSAL
Section 728.135
Waste Specific Prohibitions--Third Third
wastes.
a)
The following wastes are prohibited from land disposal.
1)
The
wastes
specified
in
35
Ill.
Adm.
Code 721.131
as
EPA
Hazardous Waste Numbers:
F002
(1,1,
2-trichloroethane)
F005
(benzene)
F005
(2-ethoxyethanol)
F005
(2-nitropropane)
F006
(wastewaters),
F019
FO25
F039
(wastewaters);
2)
The
wastes
specified
in
35
Ill.
Adm.
Code
721.132
as
EPA
Hazardous
Waste
Numbers:
KO 02
KO 03
KO 04
(wastewaters)
K005
(wastewaters)
KO 06
KO 08
(wastewaters)
KO 11
(wastewaters)
K013
(wastewaters)
KO14
(wastewaters)
K015
(nonwastewaters)
0136-0713
182
KO 17
K021
(wastewaters)
K022
(wastewaters)
K025
(wastewaters)
K026
K029
(wastewaters)
K031 (wastewaters)
KO 32
KO 33
KO 34
KO 35
K04 1
KO 42
K046
(wastewaters,
reactive
nonwastewaters)
K048
(wastewaters)
K04 9
(wastewaters)
K050
(wastewaters)
K051
(wastewaters)
K052
(wastewaters)
K060 (wastewaters)
K06l (wastewaters) and
(high zinc subcategory
15
zinc)
K069 (wastewaters, calcium sulfate
nonwastewaters)
KO 73
K08 3
K084
(wastewaters)
K085
K095
(wastewaters)
K096
(wastewaters)
K097
KO 98
K10 0
(wastewaters)
KlOl
(wastewaters)
Kl02
(wastewaters)
KiDS
Kl06
(wastewaters)
3)
The wastes specified in
35
Ill.
Adiu.
Code
721.133(e)
as
EPA
Hazardous
Waste
Numbers:
POOl
P002
P003
P004
P005
P006
P007
P008
P009
POlO
(wastewaters)
P011
(wastewaters).
O136-071I~
183
P012
(wastewaters)
P014
P015
P016
P017
P018
P020
P022
P023
P024
P026
P027
P028
P031
P033
P034
P036
(wastewaters)
P037
P038
(wastewaters)
P042
P045
P046
P047
P048
P049
P050
P051
P054
P056
P057
P058
P059
P060
P064
P065
(wastewaters)
P066
P067
P068
P069
P070
P072
P073
P075
P076
P077
P078
P081
P082
P084
P088
P092
(wastewaters)
P093
0136-0715
184
P095
P096
P101
P102
P103
P105
P108
P110
P112
P113
P114
P115
P116
P118
P119
P120
P122
P123
4)
The wastes specified in 35 Ill.
Adm.
Code
721.133(f)
as
EPA
Hazardous
Waste
Numbers:
U001
U002
U003
U004
17005
U006
U007
U008
U009
UOlO
U011
U012
U014
U015
U016
U017
U0l8
U019
U020
U021
U022
U023
U024
U02 5
U02 6
U0 27
U029
U03 0
U031
0136-0716
185
U032
U033
U034
U035
U036
13037
U038
13039
U04 1
U042
U04 3
U044
U045
U04 6
U047
U048
U049
U050
U051
U052
U053
U055
U056
U057
U059
13060
U061
UO 62
U063
U064
U066
U067
U068
U0 70
U0 71
13072
U073
13074
U075
U076
U077
U078
U079
U080
13081
13082
13083
U084
13085
U08 6
U089
U090
0136-0717
186
U09 1
13092
U09 3
U094
U0 95
13096
13097
13098
U099
13101
13103
13105
U106
Ul 08
U109
13110
13111
13112
U113
Ul14
13115
Ul16
13117
13118
Ull9
13120
1312.
U122
13123
13124
U125
13126
U127
U128
13129
U130
U131
13132
13133
Ul34
Ul35
U136
(wastewaters)
13137
Ui 38
U140
13141
U142
Ul4 3
U144
13145
13146
U147
01360718
187
13148
U14 9
U150
U151
(wastewaters)
13152
U153
U154
U.
55
U156
13157
U158
13159
Ul60
U161
13162
13163
13164
13165
Ul66
U167
Ul68
13169
U170
U171
U172
Ul73
Ul74
U176
13177
Ul78
U179
13180
13181
13182
13183
13184
U185
U186
U. 87
U18 8
U189
U19 1
13192
13193
U194
U196
U197
U2 00
U2 01
U2 02
U2 03
13204
01360719
188
U205
U206
U207
U208
13209
U210
13211
U213
U214
13215
U2 16
U2 17
U2 18
U2 19
13220
U222
U225
13226
U227
U228
U234
U236
U2 37
U238
13239
U240
13243
U2 44
13246
13247
U248
U2 49
4)
The
following
wastes
identified
as
hazardous
based
on
a
characteristic
alone:
DO01
DO 02
DO 03
D004
(wastewaters)
DO 05
D006
DO07
D008
(except
for
lead
materials
stored
before
secondary
smelting)
D009
(wastewaters)
DO 10
DOll
DO 12
DO 13
DO 14
D0l5
0136-0720
189
DO16
D0l7
b)
The following wastes are prohibited from land disposal.
The wastes specified in 35 Ill. Adm.
Code
721.132
as
EPA
Hazardous
Waste
Numbers:
K048 (nonwastewaters)
K049 (nonwastewaters)
K050 (nonwastewaters)
K051 (nonwastewaters)
K052 (nonwastewaters)
c)
Effective
May
B,
1992,
the
following
wastes
are
prohibited from land disposal:
1)
The wastes specified in 35 Ill. Adm. Code 721.131
as EPA Hazardous Waste Numbers:
F039
(nonwastewaters)
2)
The wastes specified in
35
Ill.
Adm.
Code
721.132
as EPA Hazardous Waste Numbers:
KO 31
(nonwastewaters)
K084
(nonwastewaters)
K101
(nonwastewaters)
K1O2
(nonwastewaters)
K1O6 (nonwastewaters)
3)
The
wastes
specified
in
35
Ill.
Adm.
Code
721.133(e)
as
EPA
Hazardous
Waste
Numbers:
POlO
(nonwastewaters)
POll (nonwastewaters)
P012
(nonwastewaters)
P036
(nonwastewaters)
P038
(nonwastewaters)
P065 (nonwastewaters)
P087
P092
(nonwastewaters)
4)
The
wastes
specified
in
35
Ill.
Adm.
Code
721.133(f)
as
EPA
Hazardous
Waste
Numbers:
13136
(nonwastewaters)
U15l
(nonwastewaters)
5)
The
following
wastes
identified
as
hazardous
based
on a characteristic alone:
DOO4
(nonwastewaters)
0136-0721
190
DOOB
(lc3d
aatcrialo
atorcd
bcforc
ocoond3ry
omclting)
D009
(nonwastewaters);
6)
Inorganic
solide
debris
as
defined
in
35
Ill.
Adm.
Code
72-8.102
(which
also
applies
to
chromium
refractory
bricks
carrying
the
EPA
Hazardous
Waste
Numbers
KO48-K052);
and
7)
RCRA
hazardous
wastes
that
contain
naturally
occurring radioactive materials.
d)
Effective
May
8,
1992,
hazardous
wastes
listed
in
Sections
728.110,
728.111
or
728.112
that
are
mixed
radioactive/hazardous
wastes,
and
soil
or
debris
contaminated
with
hazardous
wastes listed in Sections
728.110,
728.111
or
728.112
that
are
mixed
radioactive/hazardous
wastes,
are
prohibited
from
land
disposal.
~c~atmcnt
~
‘-
Cubriar’
on
incino ration,
mercury rctorti.ny,
~
uw.u
icaching
followcd
by
chemical
precipitation
or
thermal
rccovcry
of
mctalo
and
whioh
arc
contaminated
~‘
ac~ria,
arc
pron~J.L.~ trom
~apoaa1.
Effective
Nay
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
Subpart
D.
are
prohibited
from
land
disposal.
h)
Between
May
8,
1990,
and
May
8,
1992,
wastes
included
in subsections
(c),
(d) and
(e),
above,
shall
be
disposed of in a landfill or surface impoundment only
if
such unit is in compliance with the requirements
specified
in
Section
728.105(h)
(2).
i)
The requirements of subsections
(a),
(b),
(C),
(d)
and
(e),
above,
do
not
apply
if:
1)
The
wastes
meet
the
applicable
standards
specified
in
Subpart
D;
2)
Persons
have
been
granted
an
exemption
from
a
prohibition
pursuant
to
a
petition
under
Section
728.106,
with
respect
to
those
wastes
and
units
covered
by
the
petition;
3)
The
wastes
meet
the
applicable
alternate
standards
established
pursuant
to
a
petition
granted
under
Section
728.144;
0136-0722
e)
Effective
May
8,
1902,
thc
Section
havi...,,
.Fr”i
n
c~f~rd
~
this
~
t~ba~od
19
4)
Persons
have
been
granted
an
extension
to
the
effective date of a prohibition pursuant to
Section
728.105,
with
respect
to
these
wastes
covered
by
the
extension.
j)
1ro
determine
whether
a
hazardous
waste
listed
in
Section
728.110,
728.111
or
728.112
exceeds
the
applicable
treatment
standards
specified
in
Sections
728.141
and
728.143,
the
initial
generator
shall
either
test
a
representative
sample
of
the
waste
extract
or
the
entire
waste,
depending
on
whether
the
treatment
standards
are
expressed
as
concentrations
in
the
waste
extract
or
the
waste,
or
use
knowledge
of
the
waste.
If the waste contains constituents in
excess
of
the
applicable
Subpart
D
levels,
the
waste
is
prohibited
from land disposal, and all
requirements
of
this
Part
are
applicable,
except
as
otherwise
specified.
j~çj
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
Qperator of each secondarY lead smelting facility shall
submit
to
the
Agency
the
following:
A
binding
contractual commitment to construct or otherwise
provide capacity for
storin~
such
D008
wastes
prior
to
smelting
which
complies
with
all
a~rn1icable
stora~e
standards;
documentation that the ca~acitvto 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 DOOB managed
by
that
facility
prohibited
from
land
disposal
effective
March
1.
1993.
In
addition,
no
later
than
July
27,
1992.
the
owner
or
operator
of
each
facility
shall
~1ace
in
the
facility
record
documentation
of
the
manner
and
location
in
which
such
wastes
will
be
manaaed
pending
completion
of
such
capacity.
demonstrating
that
such
manaaement
ca~acitv
will
be
adequate
and
complies
with
all
a~~1icable requirements
of 35 Ill. Adm. Code
720
through
728
(Source:
Amended
at
16
Ill.
Reg.
,
effective
SUBPART D:
TREATMENT STANDARDS
Section 728.141
Treatment Standards expressed as
Concentrations in Waste Extract
a)
Table
A
identifies
the
restricted
wastes
and
the
concentrations
of
their
associated
hagardoup
constituents
which
may
not
be
exceeded
by
the
extract
0 136-0723
192
of
a
waste
or
waste
treatment
residual
developed
using
the
test
method
in
Appendix
A
for
the
allowable
land
disposal
of
such
waste~,
with
the
exception
of
wastes
D004,
DOO8,
KO31 D031, K084,
KlOl,
K102,
POlO,
POll,
P012,
P036,
P038
and
Ui36.
Table
A
identifieD
the
.rcstr.iotod
wastes
D.004,
D00.C,
KOll,
.K084,
KlOl,.
X102,
POlO,
POll,
P012,
P036,
P038
and
U136
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
721.Appendix
A
or B for the
allowable
land
disposal
of
such
wastes.
(Appendix
B
gf
this
Part
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 ~on
grab
samples,
unless
otherwise
noted
in
Table
A.
b)
When
wastes
with
differing
treatment
standards
for
a
constituent
of
concern
are
combined
for purposes of
treatment,
the
treatment
residue
must
meet
the
lowest
treatment
standard
for
the
constituent
of
concern,
except
that
mixtures
of
high
and
low
zinc
nonwastewater
K061
are
subject
to
the
treatment
standard
for
high
zinc
K061.
(Source:
Amended
at
16
Ill.
Reg.
,
effective
)
Section 728.Table D Technology-Based Standards by
RCRA
Waste
Code
Waste See
CAS No.
Technolo- Technolo- Waste Descriptions
Codes
Also
gy
Code,
gy
Code,
and/or Treatment
Waste—
Nonwaste—
Subcategory
waters
waters
DOOl
NA
NA
DEACT
NA
Ignitable Liquids
based on 35 Ill.
Adm.
Code
721.121(a)
(1)—wastewaters
01 36-072~~
193
DOOl
NA
NA
NA
DEACT
Ignitable Liquids
based on 35 Ill.
Adm.
Code
721.121(a)
(1)-Low
TOC
Ignitable Liquids
Subcategory--Less
than 10
total
organic carbon
DOOl
NA
NA
NA
FSUBS;
Ignitable
Liquids
RORGS;
or
based
on
35
Ill.
INCIN
Adm. Code 721.121(a)
(1)-High TOC
Ignitable Liquids
Subcategory--Greater
than
or
equal
to
10
total
organic
carbon
DOOl
NA
NA
NA
DEACT
B
Ignitable
compressed
gases
based
on
35
Ill.
Adju.
Code
721.121(a)
(3)
DOOl
NA
NA
NA
DEACT
Ignitable
reactives
based on 35
Ill.
Adin. Code 721.121(a)
(2)
DOOl
NA
NA
DEACT
DEACT
Oxidizers
based
on
35
Ill.
Adm.
Code
721.121(a)
(4)
D002
NA
NA
DEACT
DEACT
Acid subcategory
based
on
35
Ill.
Adin.
Code
721.122(a)
(1)
D002
NA
NA
DEACT
DEACT
Alkaline subcategory
based
on
35
Ill.
Adm.
Code 721.122(a)
(1)
D002
NA
NA
DEACT
DEACT
Other
corrosives
based on 35 111.
Adm.
Code
721.122(a)
(2)
0136-0725
194
D003
N-A
NA
DEACT
DEACT
Reactive
sulf ides
(may
not
(may
not
based
on
35
Ill.
Adm.
Code
721.123(a)
diluted)
diluted)
(5)
but
not
but
not
including including
dilution
dilution
as
a
sub-
as
a
sub-
stitute
stitute
for
ade-
for
ade-
auate
quate
treat-
treat-
ment.
ment.
D003
NA
NA
DEACT
DEACT
Explosives based on
35 Ill.
Adin.
Code
721.123 (a) (6),
(7)
and
(8)
D003
NA
NA
NA
DEACT
Water reactives
based on 35
Ill.
Adm.
Code
721.123(a)
(2),
(3)
and
(4)
D003
NA
NA
DEACT
DEACT
Other
reactives
based on 35
Ill.
Adm.
Code
721.123(a)
(1)
D006
NA
7440-43-9
NA
RTHERM
Cadmium-containing
batteries
D008
NA
7439-92-1
NA
RLEAD
Lead
acid
batteries
(Note:
This
standard
only
applies
to
lead
acid
batteries
that
are
identified as
RCRA
hazardous
wastes
and
that are not
excluded elsewhere
from regulation
under the land
disposal
re-
strictions of this
Part or exempted
under other regula-
tions (see 35 Ill.
Adm. Code 726.180).)
0136-0726
195
D009
Tables
7439-97-6
NA
IMERC;
or
Mercury:
(High
A
&
B
RNERC
Mercury
Subcategory--greater
than
or
equal
to
260
mg/kg
total
Mercury——contains
mercury and organics
(and are not incin-
erator residues))
D009
Tables
7439-97-6
NA
RMERC
Mercury:
(High
A
&
B
Mercury
Subcategory--greater
than
or
equal
to
260
mg/kg
total
Mercury—--inorganics
(including
incinerator
residues
and residues from
RMERC))
D0l2
Table B 72-20-8
BIODG; or NA
Endriri
INCIN
D013
Table
B
58-89-9
CARBN;
or
NA
Lindane
INCIN
D014
Table B 72-43-5
WETOX; or NA
Methoxychior
INCIN
D015
Table
B 8001-35-1
BIODG;
or
NA
Toxaphene
INCIN
D016
Table B 94-75—7
CHOXD;
NA
2,4—D
BIODG;
or
INCIN
D017
Table B
93-72-1
CHOXD;
or
NA
2,4,5—TP
INCIN
F005
Tables
79-46-9
(WETOX
or
INCIN
2—Nitropropane
A
&
B
CHOXD)
fb
CARBN;
or
INCIN
F005
Tables
110-80-5
BIODG;
or
INCIN
2—Ethoxyethanol
A&B
INCIN
F024
Tables
NA
INCIN
INCIN
A&B
0 136-0727
196
K025
NA
NA
LLEXT
fb
INCIN
Distillation
bottoms
SSTRIP fb
from the production
CARBN;
or
of
nitrobenzene
by
INCIN
the
nitration
of
benzene
K026
NA
NA
INCIN
INCIN
Stripping still
tails from the pro-
duction
of
methyl
ethyl pyridines
K027
NA
NA
CARBN;
or
FSUBS;
or
Centrifuge
and
INCIN
INCIN
distillation
residues
from
toluene
diisocyanate
production
E039
NA
NA
CARBN;
or
FSUBS;
or
Filter
cake
from
the
INCIN
INCIN
filtration
of
di-
ethylphosphoro
-
dithioc
acid
in
the
production
of
phor-
ate
K044
NA
NA
DEACT
DEACT
Wastewater
treatment
sludges
from
the
manufacturing
and
processing
of
explosives
K045
NA
NA
DEACT
DEACT
Spent
carbon
from
the
treatment
of
wastewater con-
taining explosives
K047
NA
NA
DEACT
DEACT
Pink/red water from
TNT operations
K069
Tables
NA
NA
RLEAD
Emission
control
A
& B
dust/sludge from
secondary
lead
smelting:
Non—
Calcium Sulfate
Sub-
category
0136-0728
197
106
Tables
NA
NA
RNERC
Wastewater treatment
A
&
B
sludge
from
the
mercury
cell
process
in
chlorine
pro-
duction:
(High
Mercury
Subcategory-
greater
than
or
equal
to
260
mg/kg
total
mercury)
1(113
NA
NA
CARBN;
or
FSUBS;
or
Condensed
liquid
INCIN
INCIN
light
ends
from
the
purification
of
toluenediamine
in
the
production
of
toluenediamine
via
hydrogenation
of
di-
nitrotoluene
1(114
NA
NA
CARBN;
or
FSUBS;
or
Vicinals
from
the
INCIN
INCIN
purification
of
tol-
uenediamine
in
the
production
of
toluenediamine
via
hydrogenation
of
dinitrotoluene
1(115
NA
NA
CARBN;
or
FSUBS;
or
Heavy
ends
from
the
INCIN
INCIN
purification
of
toluenediamine
in
the
production
of
toluenediamine
via
hydrogenation
of
di-
nitrotoluene
1(116
NA
NA
CARBN;
or
FSUBS;
or
Organic
condensate
INCIN
INCIN
from the solvent
recovery
column in
the
production
of
toluene diisocyanate
via
phosgenation
of
toluenediamine
POOl
NA
81-81-2
(WETOX
or
FSUBS;
or
Warfarin
(0.3)
CHOXD)
fb
INCIN
CARBN;
or
INCIN
P002
NA
591-08-2
(WETOX
or
INCIN
1—Acetyl-2-thiourea
CHOXD)
fb
CARBN;
or
INCIN
0 136-0729
198
P003
NA
107-02-8
NA
FSUBS;
or
Acrolein
INCIN
P005
NA
107-18-6
(WETOX
or
FSUBS;
or
Allyl
alcohol
CHOXD)
Lb INCIN
CARBN;
or
INCIN
P006
NA
20859-73-8
CHOXD;
CHOXD;
Aluminum phosphide
CHRED;
or
CHRED;
or
INCIN
INCIN
P007
NA
2763—96-4
(WETOX
or
INCIN
5—Aminoethyl
3-
CHOXD)
Lb
isoxazolol
CARBN;
or
INCIN
P008
NA
504-24-5
(WETOX
or
INCIN
4-Aminopyridine
CHOXD)
Lb
CARBN;
or
INCIN
P009
NA
131-74-8
CHOXD;
FSUBS;
Ammonium
picrate
CHRED;
CHOXD;
CARBN;
CHRED;
or
BIODG;
or
INCIN
INCIN
P014
NA
108-95-5
(WETOX
or
INCIN
Thiophenol
(Benzene
CHOXD)
fb
thiol)
CARBN;
or
INCIN
P015
NA
7440-41-7
RNETL
or
RNETL;
or Beryllium dust
RTHRN
RTHRN
P016
NA
542-88-1
(WETOX
or
INCIN
Bis(chloromethyl)-
CHOXD)
fb
ether
CARBN;
or
INCIN
P017
NA
598-31-2
(WETOX
or
INCIN
Bromoacetone
CHOXD)
fb
CARBN;
or
INCIN
P018
NA
357-57-3
(WETOX
or
INCIN
Brucine
CHOXD)
fb
CARBN;
or
INCIN
P022
Table
B
75-15-0
NA
INCIN
Carbon
disulfide
01360730
199
P023
NA
107-20-0
(WETOX
or
INCIN
Chloroacetaldehyde
CHOXD)
fb
CARBN;
or
INCIN
P026
~A
5344-82-1
(WETOX
or INCIN
1-(o-Chiorophenyl)-
CHOXD)
Lb
thiourea
CARBN;
or
INCIN
P027
NA
542-76-7
(WETOX
or
INCIN
3-Chloropropio—
CHOXD)
fb
nitrile
CARBN;
or
INCIN
P028
NA
100-44-7
(WETOX
or
INCIN
Benzyl
chloride
CHOXD)
Lb
CARBN;
or
INCIN
P031
NA
460-19-5
CHOXD;
CHOXD;
Cyanogen
WETOX;
or
WETOX;
or
INCIN
INCIN
P033
NA
506-77-4
CHOXD;
CHOXD;
Cyanogen chloride
WETOX;
or
WETOX;
or
INCIN
INCIN
P034
NA
131-89-5
(WETOX
or
INCIN
2—Cyclohexyl—4,6-di-
CHOXD)
Lb
nitrophenol
CARBN;
or
INCIN
P040
NA
297-97-2
CARBN;
or
FSUBS;
or
O,O-Diethyl
0-
INCIN
INCIN
pyrazinyl phosphoro-
thioate
P041
NA
311-45-5
CARBN;
or
FSUBS;
or
Diethyl-p-nitro-
INCIN
INCIN
phenyl phosphate
P042
NA
51-43-4
(WETOX
or
INCIN
Epinephrine
CHOXD)
Lb
CARBN;
or
INCIN
P043
NA
55-91-4
CARBN;
or
FSUBS;
or
Diisopropylfluoro—
INCIN
INCIN
phosphate
(DFP)
P044
NA
60-51-5
CARBN;
or
FSUBS;
or
Dimethoate
INCIN
INCIN
0136-0731
200
P045
NA
39196-18-4
(WETOX
or
INCIN
Thiofanox
CHOXD)
Lb
CARBN;
or
INCIN
P046
NA
122-09-8
(WETOX or INCIN
alpha,alpha-Di-
CHOXD)
fb
methylphenethylamine
CARBN;
or
INCIN
P047
NA
534—52-1
(WETOX
or
INCIN
4,6—Dinitro-o-cresol
CHOXD)
Lb
salts
CARBN;
or
INCIN
P049
NA
541-53-7
(WETOX or INCIN
2,4—Dithiobiuret
CHOXD)
Lb
CARBN;
or
INCIN
P054
NA
151-56-4
(WETOX
or
INCIN
Aziridine
CHOXD)
Lb
CARBN;
or
INCIN
P056
Table
B
7782-41-4
NA
ADGAS
Lb
Fluorine
NEUTR
P057
NA
640-19-7
(WETOX
or
INCIN
Fluoroacetamide
CHOXD)
Lb
CARBN;
or
INCIN
P058
NA
62-74-8
(WETOX
or
INCIN
Fluoroacetic acid,
CHOXD)
fb
sodium
salt
CARBN; or
INCIN
P062
NA
757-58-4
CARBN;
or FSUBS or
Hexaethyltetra-
INCIN
INCIN
phosphate
P064
NA
624-83-9
(WETOX
or
INCIN
Isocyanic
acid,
CHOXD)
Lb
ethyl ester
CARBN;
or
INCIN
0136-0732
201
P065
Tables
628-86-4
NA
RNERC
Mercury
fulminate:
A
&
B
(High
Mercury
Sub-
category——greater
than
or
equal
to
260
mg/kg total
Mercury——either--in-
cinerator residues
or
residues
from
RNERC)
P065
Tables
62 8-86-4
NA
IMERC
Mercury
fulminate:
A
&
B
(All
nonwastewaters
that
are
not
incinerator
residues
or
are
not
residues
from
RMERC;
regard-
less of Mercury
Content)
P066
NA
16752-77-5
(WETOX
or
INCIN
Methomyl
CHOXD)
Lb
CARBN;
or
INCIN
P067
NA
75-55-8
(WETOX
or INCIN
2-Nethylaziridine
CHOXD)
Lb
CARBN;
or
INCIN
P068
NA
6034-4
CHOXD;
FSUBS;
Methyl hydrazine
CHRED;
CHOXD;
CARBN;
CHRED;
OR
BIODG;
or
INCIN
INCIN
P069
NA
75-86-5
(WETOX
or
INCIN
Methyllactonitrile
CHOXD)
Lb
CARBN;
or
INCIN
P070
NA
116-06-3
(WETOX
or
INCIN
Aldicarb
~HOXD) Lb
CARBN;
or
INCIN
P072
NA
86-88-4
(WETOX
or
INCIN
1-Naphthyl-2-thio—
CHOXD)
fb
urea
CARBN;
or
INCIN
0136-Q733
202
P075
NA
54-11-5
A
(WETOX
or
INCIN
Nicotine and salts
CHOXD)
fb
CARBN;
or
INCIN
P076
NA
10102-43—9
ADGAS
ADGAS
~Nitricoxide
P078
NA
10102-44-0
ADGAS
ADGAS
Nitrogen
dioxide
P081
NA
55-63-0
CHOXD;
FSUBS;
Nitroglycerin
CHRED;
CHOXD;
CARBN;
CHRED;
or
BIODG;
or
INCIN
INCIN
P082
Table
B
62-75-9
NA
INCIN
N-Nitrosodimethyl-
amine
P084
NA
4549-40-0
(WETOX
or
INCIN
N-Nitrosomethyl-
CHOXD)
fb
vinylamine
CARBN;
or
INCIN
P085
NA
152-16-9
CARBN;
or
FSUBS;
or
Octamethylpyro-
INCIN
INCIN
phosphoramide
P087
NA
20816-12-0
RMETL;
or
RMETL;
or Osmium
tetroxide
RTHRN
RTHBJ4
P088
NA
14 5-73-3
(WETOX
or
FSUBS;
or
Endothall
CHOXD)
fb INCIN
CARBN;
or
INCIN
P092
Tables
62-38-4
NA
RNERC
Phenyl
mercury
A
&
B
acetate:
(High
Mercury
Sub-
category——greater
than or equal to 260
ag/kg
total
Mercury——either
in-
cinerator
residues
or
residues
from
RMERC)
U136-073~
203
P092
Tables
62-38-4
NA
IMERC;
or
Phenyl
mercury
A
&
B
RNERC
acetate:
(All
nonwastewaters
that
are not incinerator
residues and are not
residues from
RMERC:
regardless
of
Mercury Content)
P093
NA
103-85-5
(WETOX or INCIN
N-Phenylthiourea
CHOXD)
fb
CARBN;
or
INCIN
P095
NA
75-44-5
(WETOX
or
INCIN
Phosgene
CHOXD)
Lb
CARBN;
or
INCIN
P096
NA
7803-51-2
CHOXD;
CHOXD;
Phosphine
CHRED;
or
CHRED;
or
INCIN
INCIN
P102
NA
107-19-7
(WETOX
or
FSUBS;
or
Propargyl
alcohol
CHOXD)
Lb
INCIN
CARBN;
or
INCIN
P105
NA
26628-22-8
CHOXD;
FSUBS;
Sodium
azide
CHRED;
CHOXD;
CARBN;
CHRED;
or
BIODG;
or
INCIN
INCIN
P108
NA
57-24-9
A
(WETOX
or
INCIN
Strychnine
and
salts
CHOXD)
Lb
CARBN;
or
INCIN
P109
NA
3689-24-5
CARBN;
or
FSUBS;
or
Tetraethyldithio-
INCIN
INCIN
pyrophosphate
P112
NA
509-14-8
CHOXD;
FSUBS;
Tetranitromethane
CHRED;
CHOXD;
CARBN;
CHRED;
or
BIODG;
or INCIN
INCIN
P113
Table
B
1314-32-5
NA
RTHRM;
or
Thallic
oxide
STABL
0136-0735
204
P115
Table B
7446-18-6
NA
RTHRN;
or
Thallium
(I)
sulfate
STABL
P116
NA
79-19-6
(WETOX
or
INCIN
Thiosemicarbazide
CHOXD)
Lb
CARBN;
or
INCIN
P118
NA
75-70-7
(WETOX
or
INCIN
Trichioromethane-
CHOXD)
Lb
thiol
CARBN;
or
INCIN
P119
Table
B
7803-55-6
NA
STABL
Ammonium
vanadate
P120
Table
B
1314-62-1
NA
STABL
Vanadium
pentoxide
P122
NA
1314-84-7
CHOXD;
CHOXD;
Zinc
Phosphide
CHRED;
or
CHRED;
or
(10)
INCIN
INCIN
UOO1
NA
75-07-0
(WETOX
or
INCIN
Acetaldehyde
CHOXD)
fb
CARBN;
or
INCIN
U003
Table B 75-05-8
NA
INCIN
Acetonitrile
U006
NA
75-36-5
(WETOX
or
INCIN
Acetyl
chloride
CHOXD)
Lb
CARBN;
or
INCIN
U007
NA
79-06-1
(WETOX
or
INCIN
Acrylamide
CHOXD)
Lb
CARBN;
or
INCIN
U008
NA
79-10-7
(WETOX
or
FSUBS;
or
Acrylic
acid
CHOXD)
Lb INCIN
CARBN;
or
INCIN
UO10
NA
50-07-7
(WETOX
or
INCIN
Mitomycin
C
CHOXD)
Lb
CARBN;
or
INCIN
UOll
NA
61-82-5
(WETOX
or
INCIN
Amitrole
CHOXD)
Lb
CARBN;
or
INCIN
0136-0736
205
t3014
NA
492-80-8
(WETOX
or
INCIN
Auramine
CHOXD)
Lb
CARBN;
or
INCIN
U0l5
NA
115-02-6
(WETOX
or
INCIN
Azaserine
CHOXD)
Lb
CARBN;
or
INCIN
U016
NA
225-51-4
(WETOX
or
FSUBS;
or
Benz(c)acridine
CHOXD)
Lb
INCIN
CARBN;
or
INCIN
U017
NA
98-87-3
(WETOX
or
INCIN
Benzal
chloride
CHOXD)
Lb
CARBN;
or
INCIN
iJO2O
NA
98-09-9
(WETOX
or
INCIN
Benzenesulfonyl
CHOXD)
Lb
chloride
CARBN;
or
INCIN
U021
NA
92-87-5
(WETOX
or
INCIN
Benzidine
CHOXD)
Lb
CARBN;
or
INCIN
U023
NA
98-07-7
CHOXD;
FSUBS;
Benzotrichloride
CHRED;
CHOXD;
CARBN;
CHRED;
or
BIODG;
or
INCIN
INCIN
U026
NA
494-03-1
(WETOX
or
INCIN
Chiornaphazin
CHOXD)
Lb
CARBN;
or
INCIN
U033
NA
353-50-4
(WETOX
or INCIN
Carbonyl fluoride
CHOXD)
Lb
CARBN;
or
INCIN
U034
NA
75-87-6
(WETOX
or
INCIN
Trichloro-
CHOXD)
Lb
acetaldehyde
CARBN;
or
(Chloral)
INCIN
0136-0737
206
U035
NA
305-03-3
(WETOX
or
INCIN
Chlorambucil
CHOXD)
Lb
CARBN;
or
INCIN
U038
Table
B
510-15-6
NA
INCIN
Chlorobenzilate
U041
NA
106-89-8
(WETOX
or
INCIN
l-Chloro-2,3—epoxy-
CHOXD)
Lb
propane (Epichloro-
CARBN;
or
hydrin)
INCIN
UO42
Table
B
110-75-8
NA
INCIN
2-Chloroethyl
vinyl
ether
U046
NA
107-30-2
(WETOX or INCIN
Chloromethyl methyl
CHOXD)
fb
ether
CARBN;
or
INCIN
UO49
NA
3165-93-3
(WETOX
or
INCIN
4—Chloro-o-toluidine
CHOXD)
fb
hydrochloride
CARBN;
or
INCIN
U053
NA
4170-30-3
(WETOX
or
FSUBS;
or
Crotonaldehyde
CHOXD)
fb
INCIN
CARBN;
or
INCIN
U055
NA
98-82-8
(WETOX
or
FSUBS;
or
Cumene
CHOXD)
Lb
INCIN
CARBN;
or
INCIN
U056
NA
110-82-7
(WETOX
or
FSUBS;
or
Cyclohexane
CHOXD)
Lb INCIN
CARBN;
or
INCIN
U057
Table B 108-94-1
NA
FSUBS;
or
Cyclohexanone
INCIN
U058
NA
50-18-0
CARBN;
or
FSUBS;
or
Cyclophosphamide
INCIN
INCIN
U059
NA
20830-81-3
(WETOX
or INCIN
Daunomycin
CHOXD)
fb
CARBN;
or
INCIN
0136-0738
207
U062
NA
2303-16-4
(WETOX
or
INCIN
Diallate
CHOXD)
Lb
CARBN;
or
INCIN
U064
NA
189-55-9
(WETOX
or
FSUBS;
or
1,2,7,S-Dibenzo-
CHOXD)
Lb
INCIN
pyrene
CARBN;
or
INCIN
U073
NA
91-94-1
(WETOX
or
INCIN
3,3’-Dichlorobenz-
CHOXD)
Lb
idine
CARBN;
or
INCIN
U074
NA
1476-11-5
(WETOX
or
INCIN
cis—1,4—Dichloro—2-
CHOXD)
Lb
butene;
trans-1,4-
CARBN;
or
Dichloro-2-butene
INCIN
U085
NA
1464-53-5
(WETOX
or
FSUBS;
or
1,2:3,4-Diepoxy-
CHOXD)
fb INCIN
butane
CARBN;
or
INCIN
U086
NA
1615-80-1
CHOXD;
FSUBS;
N,N—Diethylhydrazine
CHRED;
CHOXD;
cARBN;
CHRED;
or
BIODG;
or
INCIN
INCIN
U087
NA
3288-58-2
CARBN;
or
FSUBS;
or
0,0—Diethyl
S-
INCIN
INCIN
methyldithio-
phosphate
U089
NA
56-53-1
(WETOX
or
FSUBS;
or
Diethyl
stilbestrol
CHOXD)
Lb
INCIN
CARBN;
or
INCIN
U090
NA
94-58-6
(WETOX
or
FSUBS;
or
Dihydrosafrole
CHOXD)
Lb INCIN
CARBN;
or
INCIN
U091
NA
119-90-4
(WETOX
or
INCIN
3,3’—Dimethoxy-
CHOXD)
Lb
benzidine
CARBN;
or
INCIN
0136-0739
208
U092
NA
124-40-3
(WETOX
or
INCIN
Dimethylamine
CHOXD)
Lb
CARBN;
or
INCIN
U093
Table
B
621-90-9
NA
NCIN
p-Dimethylaminoazo-
benzene
U094
NA
57-97-6
(WETOX
or
FSUBS;
or
7,12-Dimethylbenz-
CHOXD)
Lb INCIN
(a)anthracene
CARBN;
or
INCIN
U095
NA
119-93-7
(WETOX or INCIN
3,3’-Diniethylbenz-
CHOXD)
Lb
idine
CARBN;
or
INCIN
U096
NA
80-15-9
CHOXD;
FSUBS;
alpha,alpha—
CHRED;
CHOXD;
Dimethyl-benzyl
CARBN;
CHRED;
or
hydroperoxide
BIODG;
or
INCIN
INCIN
U097
NA
79-44-7
(WETOX
or
INCIN
Dimethylcarbamoyl
CHOXD)
Lb
chloride
CARBN;
or
INCIN
U098
NA
57-14-7
CHOXD;
FSUBS;
1,1-Dimethyl-
CHRED;
CHOXD;
hydrazine
CARBN;
CHRED;
or
BIODG;
or
INCIN
INCIN
U099
NA
540-73-8
CHOXD;
FSUBS;
1,2-Dimethyl-
CHRED;
CHOXD;
hydrazine
CARBN;
CHRED;
or
BIODG;
or INCIN
INCIN
U103
NA
77-78-1
CHOXD;
FSUBS;
Dimethyl sulfate
CHRED;
CHOXD;
CARBN;
CHRED;
or
BIODG; or INCIN
INCIN
U109
NA
122-66-7
CHOXD;
FSUBS;
1,2-Diphenyl-
CHRED;
CHOXD;
hydrazine
CARBN;
CHRED;
or
BIODG;
or
INCIN
INCIN
0136_07t40
209
13110
NA
142-84-7
(WETOX
or
INCIN
Dipropylamine
CHOXD)
Lb
CARBN;
or
INCIN
U113
NA
14 0-88—5
(WETOX
or
FSUBS;
or
Ethyl
acrylate
CHOXD)
fb
INCIN
CARBN;
or
INCIN
13114
NA
111-54-6
(WETOX
or
INCIN
Ethylenebisdithio-
CHOXD)
Lb
carbamic
acid
CARBN;
or
INCIN
U115
NA
75-21-8
(WETOX or CHOXD; or Ethylene oxide
CHOXD)
Lb
INCIN
CARBN;
or
INCIN
13116
NA
96-45-7
(WETOX
or
INCIN
Ethylene
thiourea
CHOXD)
fb
CARBN;
or
INCIN
U1l9
NA
62-50-0
(WETOX
or
INCIN
Ethyl
methane-
CHOXD)
fb
sulfonate
CARBN;
or
INCIN
U122
NA
50-00-0
(WETOX
or
FSUBS;
or
Formaldehyde
CHOXD)
Lb INCIN
CARBN;
or
INCIN
13123
NA
64-18-6
(WETOX
or
FSUBS;
or
Formic
acid
CHOXD)
Lb INCIN
cARBN;
or
INCIN
U124
NA
110-00-9
(WETOX
or
FSUBS;
or
Furan
CHOXD)
Lb
INCIN
CARBN;
or
INCIN
U125
NA
98-01-1
(WETOX
or
FSUBS;
or
Furfural
CHOXD)
Lb INCIN
CARBN;
or
INCIN
0 136-0Th
I
210
U126
NA
765-34-4
(WETOX
or
FSUBS;
or Glycidylaldehyde
CHOXD)
Lb INCIN
CARBN;
or
INCIN
U132
NA
70-30-4
(WETOX
or
INCIN
Hexachlorophene
CHOXD)
fb
CARBN;
or
INCIN
U133
NA
302-01-2
cHOXD;
FSUBS;
Hydrazine
CHRED;
CHOXD;
CARBN;
CHRED;
or
BIODG;
or
INCIN
INCIN
13134
Table B
7664-39-3
NA
ADGAS
fb
Hydrogen
Fluoride
NEUTR;
or
NEUTR
U135
NA
7783-06-4
CHOXD;
CHOXD;
Hydrogen
Sulfide
CHRED;
or
CHRED;
or
INCIN
INCIN
U143
NA
303-34-4
(WETOX
or
INCIN
Lasiocarpine
CHOXD)
Lb
CARBN;
or
INCIN
13147
NA
108-31-6
(WETOX
or
FSUBS;
or
Maleic
anhydride
CHOXD)
Lb INCIN
CARBN;
or
INCIN
U148
NA
123-33-1
(WETOX
or INCIN
Maleic hydrazide
CHOXD)
Lb
CARBN;
or
INCIN
U149
NA
109-77-3
(WETOX
or
INCIN
I4alononitrile
CHOXD)
fb
CARBN;
or
INCIN
U150
NA
148-82-3
(WETOX
or
INCIN
Melphalan
CHOXD)
Lb
CARBN;
or
INCIN
oI36_07~2
211
U15l
Tables
7439-97-6
NA
RMERC
Mercury:
(High
A & B
Mercury Sub-
category—-greater
than
or
equal
to
260
mg/kg
total
Mercury)
U153
NA
74-93-1
(WETOX
or
INCIN
Nethanethiol
CHOXD)
Lb
CARBN;
or
INCIN
Ul54
NA
67-56-1
(WETOX
or
FSUBS;
or
Methanol
CHOXD)
Lb
INCIN
CARBN;
or
INCIN
13156
NA
79-22-1
(WETOX
or
INCIN
Methyl chioro—
CHOXD)
Lb
carbonate
CARBN;
or
INCIN
13160
NA
1338-23-4
CHOXD;
FSUBS;
Methyl ethyl ketone
CHRED;
CHOXD;
peroxide
CkRBN;
CHRED;
or
BIODG;
or
INCIN
INCIN
U163
NA
70-25-7
(WETOX
or
INCIN
N-Methyl-N’-nitro-N-
CHOXD)
Lb
Nitrosoguanidine
CARBN;
or
INCIN
Ul64
NA
56-04-2
(WETOX
or
INCIN
Methylthiouracil
CHOXD)
Lb
CARBN;
or
INCIN
13166
NA
130-15-4
(WETOX
or
FSUBS;
or
1,4-Naphthoquinone
CHOXD)
Lb
INCIN
CARBN;
or
INCIN
U167
NA
134-32-7
(WETOX
or
INCIN
1-Naphthylamine
~H0XD) Lb
CARBN;
or
INCIN
U168
Table B 91-59-8
NA
INCIN
2-Naphthylamine
212
13171
NA
79-46-9
(WETOX
or
INCIN
2-Nitropropane
CHOXD)
Lb
CARBN;
or
INCIN
13173
NA
1116-54-7
+WETOX or INCIN
N—Nitroso—diethanol—
CHOXD) fb
amine
CARBN;
or
INCIN
13176
NA
759-73-9
(WETOX
or
INCIN
N—Nitroso-N-ethyl-
CHOXD)
fb
urea
CARBN;
or
INCIN
13177
NA
684-93-5
(WETOX
or
INCIN
N-Nitroso-N-methyl-
CHOXD)
Lb
urea
CARBN;
or
INCIN
Ul78
NA
615-53-2
(WETOX
or
INCIN
N-Nitroso-N-methyl-
CHOXD)
Lb
urethane
CARBN;
or
INCIN
13182
NA
123-63-7
(WETOX
or
FSUBS;
or
Paraldehyde
CHOXD)
Lb INCIN
CARBN;
or
INCIN
U184
NA
76-01-7
(WETOX
or
INCIN
Pentachloroethane
CHOXD)
Lb
CARBN;
or
INCIN
U186
NA
504-60-9
(WETOX
or
FSUBS; or 1,3—Pentadiene
CHOXD)
Lb INCIN
CARBN;
or
INCIN
U189
NA
13 14-80-3
CHOXD;
cHOXD;
Phosphorus
sulfide
cHRED;
or
CHRED;
or
INCIN
INCIN
U191
NA
109-06-8
(WETOX
or INCIN
2-Picoline
CHOXD)
Lb
CARBN;
or
INCIN
0I36-07~
213
13193
NA
1120-71-4
(WETOX
or
INCIN
1,3-Propane
sultone
CHOXD)
Lb
CARBN;
or
INCIN
13194
NA
107-10-8
(WETOX or INCIN
n-Propylamine
CHOXD)
Lb
CARBN; or
INCIN
13197
NA
106-51-4
(WETOX
or
FSUBS;
or
p-Benzoguinone
CHOXD)
Lb INCIN
CARBN;
or
INCIN
13200
NA
50-55-5
(WETOX
or
INCIN
Reserpine
CHOXD)
Lb
CARBN;
or
INCIN
13201
NA
108-46-3
(WETOX
or
FSUBS;
or
Resorcinol
CHOXD)
Lb INCIN
CARBN;
or
INCIN
13202
NA
81-07-2
A
(WETOX
or
INCIN
Saccharin
and
salts
CHOXD)
fb
CARBN;
or
INCIN
U206
NA
18883-66-4
(WETOX
or
INCIN
Streptozatocin
CHOXD)
Lb
CARBN; or
INCIN
13213
NA
109-99-9
(WETOX
or
FSUBS;
or
Tetrahydrofuran
CHOXD)
Lb
INCIN
CARBN;
or
INCIN
U214
Table
B
563-68-8
NA
RTHRM;
or
Thallium
(I)
acetate
STABL
U215
Table
B
6533-73-9
NA
RTHRM;
or
Thallium
(I)
STABL
carbonate
U216
Table B 7791-12-0
NA
RThRM;
or Thallium
(I)
STABL
chloride
13217
Table B 10102-45-1 NA
RTHRM;
or
Thallium
(I)
nitrate
STABL
OI3607~~
214
13218
NA
62-55-5
(WETOX
or
INCIN
Thioacetamide
CHOXD)
Lb
CARBN;
or
INCIN
13219
NA
62-56-6
(WETOX
or
INCIN
Thiourea
CHOXD)
Lb
CARBN;
or
INCIN
13221
NA
25376-45-8
CARBN;
or
FSUBS;
or
Toluenediamine
INCIN
INCIN
U222
NA
636-21-5
(WETOX
or
INCIN
o-Toluidine
hydro-
CHOXD)
Lb
chloride
CARBN;
or
INCIN
U223
NA
26471-62-5
CARBN;
or
FSUBS;
or
Toluene
diisocyanate
INCIN
INCIN
U234
NA
99-35-4
(WETOX
or
INCIN
sym-Trinitrobenzene
CHOXD)
Lb
CARBN;
or
INCIN
13236
NA
72-57-1
(WETOX
or
INCIN
Trypan
Blue
CHOXD)
Lb
CARBN;
or
INCIN
13237
NA
66-75-1
(WETOX
or
INCIN
Uracil
mustard
CIOXD)
Lb
CARBN;
or
INCIN
13238
NA
51-79-6
(WETOX
or
INCIN
Ethyl
carbamate
CHOXD)
Lb
CARBN;
or
INCIN
U24O
NA
94-75-7
A
(WETOX
or
INCIN
2,4-Dichlorophenoxy-
CHOXD)
Lb
acetic acid (salts
CARBN;
or
and esters)
INCIN
13244
NA
137-26-8
(WETOX
or
INCIN
Thirain
CHOXD)
Lb
CARBN;
or
INCIN
01 36-0Th6
215
13246
NA
506-68-3
CHOXD;
CHOXD;
Cyanogen bromide
WETOX;
or
WETOX;
or
INCIN
INCIN
13248
NA
81-81-2
(WETOX or FSUBS; or Warfarin (0.3
or
CHOXD)
Lb INCIN
less)
CARBN; or
INCIN
U249
NA
1314-84-7
CHOXD;
CHOXD;
Zinc Phosphide
CHRED; or
CHRED;
or
(10)
INCIN
INCIN
A
CAS Number given for parent compound only.
B
This
waste
code
exists
in
gaseous
form
and
is
not
categorized
as
wastewater
or
nonwastewater
forms.
NA
Not
Applicable.
BOARD
NOTE:
When
a
combination
of
these
technologies (i.e.,
a
treatment
train)
is
specified
as
a
single
treatment
standard,
the
order
of
application is specified in this Table by indicating the
five
letter
technology
code
that
must
be
applied
first,
then the
designation
“fb”
(an
abbreviation
for
“Followed
by”), then the
five letter technology code for the technology that must be
applied
next,
and
so
on.
When
more
than one technology (or
treatment
train)
are
specified
a
alternative
treatment
standards,
the Live letter technology codes
(or
the
treatment trains) are
separated
by
a
semicolon
C;)
with the last technology
preceded
by
the
word
“or”.
This
indicates
that
any one of these BDAT
technologies
or
treatment
trains
can
be
used
for
compliance
with
the
standard.
See
Section
728
Table
C
for
a
listing
of
the
technology
codes
and
technology—based treatment standards.
Derived from
40
CFR
268.
42,
Table
2
(1990), aø amended at 56 Fed.
hog.
3876,
January 31,
1991
(1991).
as amended at 57 Fed. Reg.
8088.
March
6.
1992.
(Source:
Amended at 16 Ill.
Reg.
,
effective
)
01 36-O7L~7
