ILLINOIS POLLUTION CONTROL BOARD
June
1,
1995
IN THE MATTER OF:
R95—4
UIC UPDATE, USEPA REGULATIONS
)
(Identical—in-Substance Rules)
(7—1—94 THROUGH 12—31—94)
)
IN THE MATTER OF:
R95—6
RCRA UPDATE,
USEPA REGULATIONS
)
(Identical
in Substance Rules)
(7—1—94 THROUGH 12—31—94)
)
Adopted Rule.
Final Order.
ORDER OF THE BOARD
(by E.
Dunham):
Pursuant to Section 13(c)
and 22.4(a)
of the Environmental
Protection Act
(Act)
415
ILCS 5/13(c)
& 22.4(a)
(1992),
the
Board amends the
RCRA
Subtitle C hazardous waste
(RCRA)
and
underground injection control
(UIC)
regulations.
Section 22.4(a) provides for quick adoption of regulations
that are “identical
in
substance” to federal regulations adopted
by U.S. EPA to implement Sections 3001 through 3005 of the
Resource Conservation and Recovery Act of 1976
(RCRA,
42 U.S.C.
§~
6921—6925) and that Title VII of the Act and Section
5 of the
Administrative Procedure Act
(APA)
5
ILCS 10015-35
& 5-40
(1992))
shall not apply.
Section 13(c) similarly provides with
respect to underground injection control regulations adopted by
U.S. EPA pursuant to Section 1421 of the Safe Drinking Water Act
(SDWA;
42 U.S.C.
§
300h).
Because this rulemaking is not subject
to Section
5 of the APA,
it is not subject to first notice or to
second notice review by the Joint Committee on Administrative
Rules
(JCAR).
The federal RCRA Subtitle C regulations are found
at 40 CFR 260 through 268, 270 through 271, and, more recently,
279.
The federal UIC regulations are found at
40 CFR 144,
146,
and 148.
This order is supported by an opinion adopted on the same
day.
The Board will hold the adopted the amendments for 30 days
before filing them with the Secretary of State,
in order to allow
U.S. EPA to comment
on the adopted amendments before they are
filed.
After that time,
the Board will file them, they will
become effective, and Notices of Adopted Amendments will appear
in the Illinois Register.
The complete text of the adopted rules
follows.
IT IS SO ORDERED.
Board Member
)1. NcFawn concurred.
2
I, Dorothy M. Gunn,
Clerk of the Illinois Pollution Control
Board,
certify that
e above order was adopted by the Board on
the
/~
day of
____________,
1995,
by a vote of
7~)
Dorothy N. 9~nn, Clerk
Illinois P~3/LutionControl Board
3
Section
TITLE
35:
ENVIRONMENTAL PROTECTION
SUBTITLE G:
WASTE DISPOSAL
CHAPTER
I:
POLLUTION CONTROL BOARD
SUBCHAPTER a:
GENERAL PROVISIONS
PART 700
OUTLINE OF WASTE DISPOSAL REGULATIONS
(REPEALED)
700.102
Other flegulationo (Repcalcd)
700.103
Organization
(Rcpoalcd)
700.104
Intent and Purpooc (ncpcalcd)
700.105
Interim Statue
(Repealed)
700.106
700.107
7-00.108
I £~Q
Effective Datea
~--crability
(rkcpcaled)
rermito
Prior to Authorization
(Repealed)
SUBPART
B:
DEFINITIONS
Sect
ion
700.201
Dofinitiono
(Rcpcalcd)
7-00.205
Act
(Repealed)
700.210
Chapter
7 Operating Requircmcnte
(Repealed)
700.215
Chapter
7 Permite (Repealed)
700.220
Chapter 9 Operating Roquiremonto
(Repealed)
700.225
Chapter 9 Pormite (Repealed)
conflict
~ucpeaica~
F~-’1’
(Repealed)
7-0O.~
O~oratinaReauircmcnto ‘Renoa1~a
I
UU.
.~
~230
~4O.
~255
r2~
~9~-
~c,rm1r
riaguiromento
~tCpca.Lcp)
itciu’~
operating rLequiromentB
(Repealed)
~9-
RCRA Permit
(flcpcaled)
v-GO-.
RCFtZ~.Rube
(Repealed)
700.
subject To (Repealed)
SUBPART C:
CENERATORS
Scotion
700.301
Pormito
(Repealed)
7-00.302
Operating Requiremento
(Repealed)
Manifeoto
(Repealed)
7-00.303
700.304
EmaIl Quantity Exemptiono
(Repealed)
Section
SUBPART Dz
TRANSPORTERS
700.401
Permito
(Repealed)
700.402
Operating Roquiremento
(Repealed)
700.403
~anifcoto
(Repealed)-
700.404
Small Ouantity Exemptions
(Re~ea1ed)
Section
700.501
700. 502
Section
HWM
CITES
(Repealed
~tity E~ccmptiono (Repealed)
SUBPART Fi
HAZARDOUS
(INFECTIOUS-)-
HOSPITAL WASTE
ir~I
~..4
1
~4-..
1
~..A
700.503
-fl\a
ef~
4
700.601
Ha2ardouo
(InfeCtious) Hoopital Waste (Repealed)
700.602
General Rule
(Repealed)
700.603
Conorators
(Repealed)
700.604
Tranopertero
(Repealed)
700.605
Owners
and Operators
(Repealed)
,uy.Arrnendix A.
Applicability Proviu.Lono
(Repealed)
AUTHORITY:
Implementing Sections
13 and 22.4 and authorized by Section 27 of
the Environmental Protection Act
(415 ILCS 5/13,
22.4,
27).
SOURCE:
Adopted
in p81—22,
43 PCB
427,
at
5
Ill.
Peg.
9781, effective May
17,
1982;
amended and codified in rtSl-22,
45 POB 317,
at
6 Ill.
Reg.
4828,
effective M~y17,
1982;
amended in
P81 32,
47 POB 93,
at
6 Ill.
Peg.
12655,
effective Hay
17,
1982;
amended in P82—18,
51 PCB
3.1,
at
7
Ill.
Peg.
2518,
effective February 22,
1983;
amended
in P82—19,
at
7
Ill.
Reg.
14457,
effective October 12,
1983;
amended
in
fl83 24,
at 8
Ill,
flog.
200, effective
December 27,
1983;
amended in fl94-5 at
18
Ill.
rkeg.
18244, effective December
20,
l994Repealed
in P95—6
at
19
Ill. Req.
effective
SUBPART
Ai
CENERAL
ion 700.101
Applicability
(Repealed)
(Souroes
Repealed at
18
Iii.
Peg.
18244, effective December
20,
1994)
Section 700.102
Other Regulations
(Repealed)
(Soured
Repealed at
18
Ill.
Peg.
18244, effective
Organization (Repealed)
December 20,
1994)
Section 700.103
(Source.
Repealed at 18 Ill.
fleg.
18244,
effective December 20,
1994)
Section 700.104
Intent and Purpoce
(Repealed)
December 20,
1994)
(Source.
Repealed
at
18
Ill,
flog.
18244,
effective
Section 700.105
Interim Statue
(Repealed)
December 20,
1994)
(Source.
Repealed at
18
Ill,
flog.
18244,
effective
ion 700.106
Effective Datoc
a)
U.S. EPA granted interim authorization to the
Illinois
PCRA
Subtitle
C Program effective Hay
17,
1982,
at
47
Fed.
flog.
21043
5
(May
17,
1982).
U.S. EPA granted final authorization effective
January
31,
1986,
at
51 Fed.
flog.
3778 (January 30,
1986).
1)
The effective date of
35
III.
Mm.
Code 720,
721,
722,
723r
and 725 was May
17,
1962.
~2-)--The effective date of 35 Ill. Mm.
Code 702 and
705,
to the
extent they apply to the iocuanac of RCRA permito, was Hay
17,
1982;
however, RCRA
pcrmito
wcrc
not
issued prior to
January 31,
1986.
3)
The
effective date of 35
Ill. Mm.
Code 703 and
724
was
October
12, 1983~however, RCRA pcrmito were not
issued
prior to January 31,
1986.
b)
U.S. EPA authoricod the Illinoic UIC program of fectivo March—3-,-
1984,
at 49 Fed. Peg.
3991
(Feb.
1,
1964).
1)
The effective date of
~5
Ill.
Adxn.
Code 702,
704
and 705, to
the extent they apply to the iccuance of UIC
(Underground
Injcction Control)
permits, was March
3,
1984.
2)
The effective date of
35
111. Mm.
Code 730 wac March
3,
1984.
(Cou~ce:
Section
Amended
700.107
at 18
Ill,
flog.
18244, effective December
Severability
(Repealed)
20,
1994)
(Source:
Repealed
at 18 Ill,
flog.
18244, effective December 20,
1994)
Section 700.108
References to Federal Rules
(Repealed)
(Source.
Repealed
at
18
Ill.
Reg.
18244, effective December
20,
1994)
Section 700.109
Permits Prior to Authorization
(Repealed)
(Source.
Repealed at
18 Iii.
flog.
18244, effective December
SUBPART
B.
DEFINITIONS
Definitiono (Repealed)
20,
1994)
Section 700.201
(Source:
Repealed
at
18
Iii.
fleg.
18244, effective December 20,
1994)
6
-,,~r’.
~
,~_.&.
(Seuree.
Repealed at 18
Ill. Rag.
18244,
effective December 20,
1994)
Section 700.210
Chapter
7 Operating Requiremento
(Repealed)
(Seuree.
Repealed at 18
Ill.
Peg. 18244,
effective Deeember
20,
1994)
Section 700.215
Chapter
7
Permits (Repealed)
(Source.
Repealed at 18
Ill.
Peg. 18244,
cffective December
20,
1994)
Section 700.220
Chapter
9 Operating Requirements
(Repealed)
(Sources
Repealed at 18
Ill.
flog.
18244, effective December
20,
1994)
Section 700.225
Chapter 9 Permits
(Repealed)
December 20,
1994)
(Source.
Repealed at 18
Ill.
Peg.
18244, effective
Section 700.230
Conflict (Repealed)
(Sources
Repealed at 18
Ill.
Reg.
18244,
effective December
20,
1994)
Section 700.235
HWM
(Repealed)
I
~OUECOI
t(L!U1~1.LUU
comber
20,
1994)
‘~~‘i
at 18
Ill.
fleg.
18244,
effective
Section 700.240
Operating floquiremento
(Repealed)
7
~~ourcet
i~cpeaicaat
~
iii.
iteg.
~
errcctivc
ucccmlD-er
700.245
Permit Requirements
(Ropealod)
~U,
L~t’4)
Soation
(Source:
Repealed at 18
Iii. Peg.
18244, effective
December
20,
1994)
Section 700.250
RCPA Operating Rcquircmonto (Repealed)
(Source.
Repealed at
18
Ill.
flog.
18244, effective December
20,
1994)
Seotion 700.255
RCRA Permit
(Repealed)
(Source:
Repealed at
18
Ill.
Rag.
18244, effective December
20,
1994)
Ecotion 700.a60
RCRA Rules
(Repealed)
(Source:
Repealed at
18 Ill.
fleg.
18244, effective December
700.265
Subject To (Repealed)
20,
1994)
Section
(Source:
Repealed at 18
Ill.
Peg.
18244, effective December
SUBPART
C:
CENERATORS
700.301
Permits
(Repealed)
20,
1994)
Section
(Source,
Repealed
at
18
Ill.
Peg.
18244,
effective
December
20,
1994)
Section
700.302
Operating
Requirements
(Repealed)
•1tin
.~
~
•t
—
—
I
—
—
,~~urcje:
itCpC~
co
~
ill.
ncg.
i
It’i,
orrectiv-e ucocmocr
.~u,
i~iq~
8
(Source.
Repealed at 18
Ill,
flog.
18244, effective December 20,
1994)
Section 700.304
Small Quantity Exemptions
(Repealed)
20,
1994)
(Source:
Repealed at 18
Ill,
flog.
18244,
effective December
SUBPART
Di
TRANSPORTERS
700.401
Permits
(Repealed)
Section
(Source.
Repealed
at
18
Ill.
Peg.
18244, effective December 20,
1994)
Section 700.402
Operating Requirements
(Repealed)
(Source:
Repealed at 18
Ill. Peg.
18244, effective December
20,
1994)
Section 700.403
Manifesto
(Repealed)
(Source:
Repealed at 18
Ill.
Peg.
18244, effective December 20,
1994)
Section 700.404
Small Quantity Exemptionc (Repealed)
Repealed at
18
Ill.
Peg.
18244, effective December
SUBPART E,
OWNERS
AND OPERATORS
OF
HWM
SITES
20,
1994)
(Source.
Section 700.501
Permito (flepcaled~
(Sources
~
--
.
r.
1
A
—
.è_
I O~
1
Peg.
A
~
Section 700.502
Operating flequiremonto
(Repealed)
December
20,
1994)
9
-(Source:
Section
Repealed at
18
Ill.
flog.
18244, effective December 20,
1994)
700.503
Manifests
(Repealed)
Repealed at
18
Ill.
flog.
18244, effective December 20,
1994)
(Source:
Section 700.504
Small Quantity Exemptionc
(flopoaled)
-~&ourcez Repealed at
18
Ill.
flog.
18244, effective December 20~, 1994)
Section
SUBPART
F.
HAZARDOUS
(INFECTIOUS) HOSPITAL WASTE
700.601
Hazardous
(Infectious) Hospital Waste
(Repealed)
(Sourco:
Repealed at
18 Ill. Peg. 18244,
effective December 20,
1994)
Section 700.602
Cencral Rule (Repealed)
Repealed at
18 Ill. Peg.
18244, effective December 20,
1994)
(Source:
Section 700.603
Cenerators
(Repealed)
(Sourco:
Repealed at 18 Ill. Peg. 18244,
effective December 20,
1994)
gection 700.604
Transporters
(Repealed)
(Sources
Ronea~......
I
— .3
~_
I
ti
r I
I
,..
c~
-~
.
.Lp..g
.
CL~
I
(ItI
a
~
-?r
~ecti~
1
...4i
.v~
Llccember 20.
1994)
10
(Source:
Repealed at
18
Ill,
flog. 18244, effective December 20,
1994)
700.Appendiu A
Applicability Provisions (Repealed)
(Sources
Repealed at
18
Ill,
flog.
18244, effective December
20,
1994)
TITLE
35:
ENVIRONMENTAL
PROTECTION
SUBTITLE
G:
WASTE DISPOSAL
CHAPTER
I:
POLLUTION CONTROL
BOARD
SUBCHAPTER
b:
PERMITS
PART
702
RCRA
AND
UIC
PERMIT PROGRAMS
SUBPART
A:
GENERAL
PROVISIONS
Section
702.101
Purpose,
Scope,
and
Applicability
702.102
Purpose
and
Scope
(Repealed)
702.103
Confidentiality
of
Information
Submitted
to
the
Agency
or
Board
702.104
References
702. 105
Rulemaking
702.106
Adoption
of
Agency
Criteria
702.107
Permit
Appeals
and
Review
of
Agency
Determinations
702.108
Variances
and
Adjusted
Standards
702.109
Enforcement
Actions
702.110
Definitions
SUBPART
B:
PERMIT
APPLICATIONS
Sect ion
702.120
Permit
Application
702.121
Who
Applies
702. 122
Completeness
702.123
Information
Requirements
702.
124
Recordkeeping
702.125
Continuation of Expiring Permits
702.126
Signatories to Permit Applications and Reports
SUBPART
C:
PERMIT CONDITIONS
Section
702.140
Conditions Applicable to all Permits
702.141
Duty to Comply
702.142
Duty to Reapply
702.143
Need to Halt or Reduce Activity Not
a Defense
702.144
Duty to Mitigate
702.145
Proper Operation and Maintenance
702.146
Permit Actions
702.147
Property Rights
702.148
Duty to Provide Information
702.149
Inspection and Entry
702.150
Monitoring and Records
702.151
Signature Requirements
702.152
Reporting Requirements
702.160
Establishing Permit Conditions
702.161
Duration of Permits
702.162
Schedules of Compliance
702.163
Alternative Schedules of Compliance
702.164
Recording and Reporting
11
SUBPART D:
ISSUED PERMITS
Section
702.181
Effect of
a Permit
702.182
Transfer
702.183
Modification
702.184
Causes for Modification
702.185
Facility Siting
702. 186
Revocation
702.187
Minor Modifications
AUTHORITY:
Implementing Section
13 and 22.4 and authorized by Section 27
of
the Environmental Protection Act
(415 ILCS 5/13,
22.4 and 27).
SOURCE:
Adopted
in P81—32,
47 PCB
93,
at
6
Ill.. Peg.
12479,
effective May 17,
1982; amended in R82—19,
at
53 PCB 131,
7
Ill. Peg.
14352, effective May 17,
1982;
amended in P84—9 at
9
Ill. Peg.
11926, effective July 24,
1985; amended
in P85—23 at
10
Ill. Peg.
13274,
effective July 29,
1986;
amended in P86—1 at
10
111. Peg.
14083, effective August
12,
1986;
amended in P86—28
at
11
Ill.
Peg.
6131,
effective March 24,
1987;
amended in P87—S at 11
111.
Peg.
19376,
effective November
12,
1987;
amended
in P87—26 at
12 Ill. Peg.
2579,
effective
January 15,
1988;
amended in P87—29 at
12 Ill.
Reg. 6673, effective March 28,
1988; amended in P87—39
at
12 Ill.
Peg.
13083, effective July 29,
1988;
amended in R89-1 at
13
Ill. Peg.
18452, effective November
13,
1989;
amended
in P89—2
at
14
Ill. Peg.
3089, effective February 20,
1990;
amended in P89—9
at
14
Ill. Peg.
6273, effective April
16,
1990; amended in P92—10 at
17
Ill.
Peg.
5769,
effective March 26,
1993;
amended
in R93—16 at
18
Ill. Peg.
6918,
effective April
26,
1994;
amended
in R94—5 at
18
Ill. Peg.
18284,
effective
December
20,
1994;
amended in P95—6 at
19
Iii.
Reg.
________,
effective
SUBPART
D:
ISSUED PERMITS
Section 702.181
Effect of
a Permit
a)
The existence of a RCRA or UIC permit does not constitute a
defense to a violation of the Environmental Protection Act or this
Subtitle, except for development, modification, or operation
without a permit.
However,
a permit may be modified,
reissued,
or
revoked during its term for cause as set forth in 35
Ill.
Adm.
Code 703.270 through 703.273
(PCPA) or 35 Ill. Adm. Code 704.261
through 704.263
(UIC)
and Section 702.186.
BOARD NOTE:
40 CFR 270.4(a)
differs from thia subsection
(a)
in
two significant
aspects:
(1)
it states that compliance with the
permit
is compliance with federal law,
and
(2)
it enumerates
exceptions when compliance with the permit can violate federal
law.
The exceptions are intervening
(1) statutory requirements;
(2)
40 CFR 268 land disposal restrictions;
(3)
40 CFR 264 leak
detection requirements;
and
(4)
40 CFR 266, subparts AR,
BB, and
CC air emissions limitations.
BY not codifying the federal
exceptions,
since they are not necessary in the Illinois program
to accomplish the intended
purpose.
the Board does not
intend to
imply that compliance with
a RCRA permit obviates immediate
compliance with any of the events included in the federal
exceptions.
b)
The issuance of
a permit does not convey any property rights of
any sort,
or any exclusive privilege.
c)
The issuance of
a permit does not authorize any injury to persons
or property or invasion of other private rights,
or any
12
infringement of State or local law or regulations,
except as noted
in subsection
(a)
above.
BOARD NOTE:
Derived from 40 CFP 144.35 (199~4) and 40 CFP 270.4
(199Q4),
as
amended at
59 Fed. Peg.
62952
(Dec.
6,
1994).
(Source:
Amended at
19
Ill.
Reg.
________,
effective
_____________________
TITLE 35: ENVIRONMENTAL PROTECTION
SUBTITLE G:
WASTE DISPOSAL
CHAPTER
I: POLLUTION CONTROL BOARD
SUBCHAPTER
b:
PERMITS
PART 703
RCRA
PERMIT
PROGRAM
SUBPART
A:
GENERAL PROVISIONS
Scope and Relation to Other Parts
Purpose
References
SUBPART B:
PROHIBITIONS
Prohibitions in General
RCPA 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
Purpose and Scope
Permits by Rule
Application by Existing HWM Facilities
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
Section
703. 100
703.
101
703.110
Section
703.120
703. 121
703.
122
703.123
703. 124
703.125
703. 126
703.127
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
703. 188
and Interim Status
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
Other Information
13
703.200
Specific
Part
B
Application
Information
703 .201
Containers
703.202
Tank
Systems
703.203
Surface
Impoundments
703.204
Waste
Piles
703.205
Incinerators
that
Burn
Hazardous
Waste
703.206
Land
Treatment
703.207
Landfills
703.208
Boilers
and
Industrial
Furnaces
Burning
Hazardous Waste
703.209
Miscellaneous Units
703.210
Process Vents
703.211
Equipment
703.212
Drip Pads
703.213
Air Emission Controla for Tanks,
Surface Impoundments,
and
Containers
SUBPART E:
SHORT TERM
AND PHASED PERMITS
Section
703.221
Emergency Permits
703.222
Incinerator Conditions Prior to Trial Burn
703.223
Incinerator Conditions During Trial Burn
703.224
Incinerator Conditions After Trial Burn
703.225
Trial Burns for Existing Incinerators
703.230
Land Treatment Demonstration
703.231
Research,
Development and Demonstration Permits
703.232
Permits for Boilers and Industrial Furnaces Burning Hazardous
Waste
SUBPART F: PERMIT
CONDITIONS OR DENIAL
Section
703.240
Permit Denial
703.241
Establishing Permit Conditions
703.242
Noncompliance Pursuant to Emergency Permit
703.243
Monitoring
703.244
Notice of Planned Changes (Repealed)
703.245
Twenty—four Hour Reporting
703.246
Reporting Requirements
703.247
Anticipated Noncompliance
SUBPART G: CHANGES TO PERMITS
Section
703.260
Transfer
703.270
Modification
703.271
Causes for Modification
703.272
Causes
for
Modification or Reissuance
703.273
Facility
Siting
703.280
Permit Modification at the Request of the Permittee
703.281
Class
1 Modifications
703.282
Class
2 Modifications
703.283
Class 3 Modifications
703.Appendix A
Classification of Permit Modifications
AUTHORITY:
Implementing Section 22.4 and authorized by Section
27 of the
Environmental Protection Act
(415 ILCS 5/22.4 and 27.
SOURCE: Adopted in P82-19,
53 PCB 131,
at 7 Ill. Peg.
14289, effective October
12,
1983; amended in P83—24
at
8
Ill.
Peg. 206, effective December 27,
1983;
amended in P84—9
at
9
Ill. Peg.
11899,
effective July
24,
1985;
amended
in
P85—22 at 10
Ill.
Peg.
1110,
effective January
2,
1986;
amended in R85—23 at
10
Ill. Peg.
13284, effective July
28,
1986;
amended
in P86—i at
10 Ill. Peg.
14093, effective August
12,
1986;
amended in R86—19 at
10 Ill. Peg.
20702,
14
effective December
2,
1986;
amended in P86—28 at 11
Ill.
Peg.
6121,
effective
March 24,
1987;
amended in P86-46 at
11
Ill. Peg.
13543,
effective August
4,
1987; amended in R87—5 at 11
Ill.
Peg.
19383, effective November
12,
1987;
amended in R87-26 at
12
Ill. Peg.
2584,
effective January 15,
1988;
amended in
R87—39 at 12
Ill. Peg.
13069,
effective July
29,
1988;
amended in P88—16 at
13
Ill.
Peg.
447, effective December 27,
1988; amended
in R89—1 at
13
Ill.
Peg.
18477,
effective November 13,
1989; amended in P89—9 at
14
Ill. Peg.
6278,
effective April
16,
1990;
amended
in P90—2
at
14
Ill.
Peg.
14492, effective
August
22,
1990;
amended in P90—li at
15
Ill. Reg.
9616,
effective June
17,
1991;
amended
in P91—i at 15
Ill.
Peg.
14554, effective September 30,
1991;
amended in P91—13
at
16 Ill Peg.
9767, effective June 9,
1992; amended in R92—
10 at
17
Ill. Peg.
5774, effective March
26,
1993;
amended in P93—4 at
17 Ill.
Peg.
20794,
effective November 22,
1993;
amended in P93—16 at
18
Ill. Peg.
6898,
effective April 26, 1994;
amended in P94—7
at 18 Ill. Peg.
12392,
effective July 29,
1994;
amended in P94—S
at
18
Ill.
Peg.
18316, effective
December 20,
1994;
amended in P95—6 at
19
Ill.
Peg.
________,
effective
SUBPART D: APPLICATIONS
Section 703.183
General Information
The following information is required in the Part B application for all HWM
facilities,
except as 35 Ill. Adm. Code 724.101 provides otherwise:
a)
A general description of the facility;
b)
Chemical and physical analyses of the hazardous wastes and
hazardous debris to be handled at the facility.
At
a minimum,
these analyses must contain all the information which must be
known to treat,
store or dispose of the wastes properly in
accordance with 35
Ill.
Adm.
Code 724;
C)
A copy of the waste analysis plan required by
35
Ill.
Adm. Code
724.113(b)
and,
if applicable,
35
Ill. Adm. Code 724.113(c);
d)
A description of the security procedures and equipment required by
35
Ill.
Adm.
Code 724.114, or
a justification demonstrating the
reasons for requesting
a waiver of this requirement;
e)
A copy of the general inspection schedule required by 35
Ill.
Adm.
Code 724.115(b).
Include where applicable,
as part of the
inspection schedule,
specific requirements
in 35
Ill.
Adm. Code
724.274,
724.293(i),
724.295,
724.326,
724.354,
724.373,
724.403,
724.702,
724.933,
724.952, ~724.953~ and 724.958,
724.988,
and
724.991
f)
A
justification
of
any
request
for a waiver of the preparedness
and
prevention
requirements
of
35
Ill. Adm. Code 724.Subpart C;
g)
A copy of the contingency plan required by 35
Ill.
Adm. Code
724.Subpart
D;
BOARD NOTE:
Include, where applicable,
as part of the contingency
plan,
specific requirements
in 35
Ill.
Adm.
Code 724.327 and
724.355.
35 Ill. Adm. Code 724.355 has not yet been adopted.
h)
A description of procedures, etructures~or equipment used at the
facility to:
1)
Prevent hazards
in unloading operations
(for example,
ramps,
15
~special
forklifts);
2)
Prevent
runoff
from
hazardous waste handling areas to other
areas of the facility or environment, or to prevent flooding
(for example,
berms,
dikes, ~.trenches);
3)
Prevent contamination of water supplies;
4)
Mitigate effects of equipment failure and power outages;
5)
Prevent undue exposure of personnel to hazardous waste
(for
example, protective clothing); and
6)
Prevent releases to the atmosphere.
i)
A description of precautions to prevent accidental ignition or
reaction of ignitable, reactive.~~
or incompatible wastes~as
required to demonstrate compliance with 35
Ill.
Adm. Code 724.117~~
including documentation demonstrating compliance with 35 Ill.
Adm.
Code 724.117(c);
j)
Traffic pattern, estimated volume
(number,- and types of vehicles)~
and control
(for example,
show turns across traffic lanes and
stacking lanes~+if appropriate); describe access road surfacing
and load bearing capacity;
and show traffic control
signals.)-;
k)
Facility location information~.as required by Section 703.184;
1)
An outline of both the introductory and continuing training
programs by the owners or operatore to prepare persons to operate
or maintain the HWM facility in
a safe manner1, as required to
demonstrate compliance with 35
Ill.
Adm.
Code 724.116.
A brief
description of
how training will be designed to meet actual
job
tasks
in accordance with requirements in 35
Ill.
Adm. Code
724. 116 (a)
(3)
m)
A copy of the closure plan and,
where applicable,
the post—closure
plan required by
35 Ill.
Adm.
Code
724.212,
724.2i8~, and
724.297.
Include where applicable,
as part of the plans,
specific
requirements in 35
Ill.
Adm.
Code 724.278,
724.297, 724.328,
724.358,
724.380,
724.410,
724.451,
724.70l~.and 724.703;
n)
For hazardous waste disposal units that have been closed,
documentation that notices required under
35
Ill. Adm Code 724.219
have been filed;
0)
The most recent closure cost estimate for the facility1, prepared
in accordance with
35 Iii. Adm. Code
724~242.L
and a copy of the
documentation
required to demonstrate financial assurance under
35
Ill. Adm. Code 724.243.
For
a new facility,
a copy of the
required documentation may be submitted
60 days prior to the
initial receipt of hazardous wastes,
if
it
is later than the
submission of the Part
B permit application
p)
Where applicable,
the most recent post-closure cost estimate for
the facility1, prepared in accordance with 35 Ill. Adm. Code
724.2441, plus a copy of the documentation required to demonstrate
financial assurance under 35
Iii.
Adm.
Code 724.24S-p-.
For a new
facility,
a copy of the required documentation may be submitted
60
days prior to the initial receipt of hazardous wastes,
if
it
is
later than the submission of the Part
B permit application
16
q)
Where applicable,
a copy of the insurance policy or other
documentation
which
comprises
compliance with the requirements of
35
Ill. Adm. Code 724.247.
For a
new
facility,
documentation
showing the amount of insurance meeting the specification of 35
Ill.
Adm.
Code 724.247(a)
and,
if applicable,
35 Ill.
Adm. Code
724.247(b),- that the owner or operator plans to have in
effect
before initial receipt of hazardous waste for treatment,
storage1,
or disposal.
A request for an alternative
level of required
coverage, for
a new or existing
facility,- may be submitted
as
specified in
35
Ill.
Adm.
Code 724.247(c);
r)
A topographic map showing
a distance of 1000 feet around the
facility at
a scale of 2.5 centimeters
(1 inch)
equal to not more
than 61.0 meters
(200 feet).
Contours must be shown on the map.
The contour interval must be sufficient to clearly show the
pattern of surface water flow in the vicinity of and from each
operational unit of the facility.
For example,
contours with an
interval of
1.5 meters
(5 feet),
if relief
is greater than 6.1
meters
(20 feet),
or an interval of 0.6 meters
(2 feet),
if relief
is less than 6.1 meters (20 feet).
Owners and operators of HWM
facilities
located in mountainous areas shall use larger contour
intervals to adequately show topographic profiles of facilities.
The map must clearly show the following:
1)
Map scale and date;
2)
100-year floodplain area;
3)
Surface waters including intermittent streams;
4)
Surrounding land uses
(e.g.,
residential,
commercial,
agricultural,
recreational,_etc.);
5)
A wind rose
(i.e., prevailing windspeed and direction);
6)
Orientation of the map (north arrow);
7)
Legal boundaries of the
HWM
facility site;
8)
Access
control
(e.g.,
fences,
gates,
etc.);
9)
Injection
and
withdrawal
wells both on—site and off—site;
10)
Buildings; treatment,
storage1, or disposal operations;
or
other structures (e.g.,
recreation areas,
runoff control
systems,
access and internal roads,
storm,
sanitary
and
process sewage systems,
loading and unloading areas,
fire
control
facilities,
etc.);
11)
Barriers for drainage or flood control;
12)
Location of operational units within the
HWM
facility site,
where hazardous waste
is (or will be)
treated,
stored1, or
disposed (include equipment cleanup areas);
BOARD NOTE:
For large HWM facilities,
the Agency shall
allow the use of other scales on a case by case basis.
a)
Applicants shall submit
such information as the Agency determines
is necessary for it to determine whether to issue
a permit and
what conditions to impose
in any permit issued--;
and
17
t)
For land disposal facilities,
if
a case—by—case extension has been
approved under
35
Ill.
Adm.
Code 728.105,- or
if
a petition has
been approved under 35 Ill.
Adxn.
Code 728.106,
a copy of the
notice of approval of the extension or of approval of the petition
is required.
BOARD
NOTE:
Derived from 40 CFP 270.14(b)
(198894),
as amended at
5~ Fed. Peg.
37281,
August
18,
199262952
(Dec.
6.
1994).
(Source:
Amended at 19 Ill.
Peg.
________,
effective
______________________
Section 703.201
Containers
For facilities that
store containers of hazardous waste, except as otherwise
provided in 35
Ill.
Adm. Code 724.270, the Part B application must include:
a)
A description of the containment system to demonstrate compliance
with
35
Ill. Adm.
Code 724.275.
Show at least the following:
1)
Basic design parameters,
dimensions,
and materials
of
construction;
2)
How
the
design
promotes
drainage or how containers are kept
from
contact
with
standing
liquids
in
the
containment
system;
3)
Capacity of the containment system relative to the number
and volume of containers to be stored;
4)
Provisions for preventing or managing run—on;
and
5)
How accumulated liquids can be analyzed and removed to
prevent overflow~,~
b)
For storage areas that store containers holding wastes that do not
contain free liquids,
a demonstration of compliance with
35 Ill.
Adm.
Code 724.275(c),
including:
1)
Test procedures and results or other documentation or
information to show
that
the wastes do not contain free
liquids;
and
2)
A description of how the storage area is designed or
operated to drain and remove liquids or how containers are
kept from contact with standing liquidst~,
C)
Sketches,
drawings,
or data demonstrating compliance with 35 Ill.
Adm.
Code 724.276
(location of buffer zone and containers holding
ignitable or reactive wastes)
and Section 724.277(c)
(location of
incompatible wastes), where applicable.
d)
Where incompatible wastes are stored or otherwise managed in
containers,
a description of the procedures used to ensure
compliance with 35
Ill.
Adm.
Code 724.117(b)
and
(c)
and
724.277(a) and
(b).
~.
Information on air emission control equipment,
as required in
Section 703.213.
BOARD NOTE:
Derived from 40 CFR 270.15
(19924), as amended
at
59
Fed.
Rep.
62952
(Dec.
6.
1994).
18
(Source:
Amended
at
19
Ill. Reg.
________,
effective
Section 703.202
Tank Systems
Except as otherwise provided in 35
Ill.
Adm.
Code 724.290,
owners and
operators of
facilities that use tanks to store or treat hazardous waste shall
provide the following additional linformation:
a)
A written assessment that is reviewed and certified by an
independent, qualified, registered professional engineer as to the
structural integrity and suitability for handling hazardous waste
of each tank system,
as required under 35
Ill. Adm. Code 724.291
and 724.292;
b)
Dimensions and capacity of each tank;
c)
Description
of feed systems,
safety cutoff, bypass systems1, and
pressure controls
(e.g., vents);
d)
A diagram of piping,
instrumentation1, and process flow for each
tank system;
e)
A description of materials and equipment used to provide external
corrosion protection,
as required under 35
Ill.
Adm. Code
724.292(a) (3)(~B);
f)
For
new
tank
systems,
a detailed descriptions of how the tank
system(s)
will be installed in compliance with
35
Ill. Adm.
Code
724.292(b),
(c),
(d)1, and
(e);
g)
Detailed plans and description of how the secondary containment
system for each tank system is or will be designed, constructed
and operated to meet the requirements of
35
Ill.
Adm.
Code
724.293(a),
(b),
(c),
(d),
(e)1, and
(f);
h)
For
tank
systems
for
which alternative design and operating
practices
are
sought
pursuant
to
35
Ill.
Adm.
Code
724.293(g):
1)
Detailed plans and engineering and hydrogeologic reports,
as
appropriate, describing alternate design and operating
practices that will,
in conjunction
with
location
aspects,
prevent the migration of any hazardous waste or hazardous
constituents into the groundwater or surface water during
the life of the facility, or
2)
A detailed assessment of the substantial present or
potential hazards posed to human health or the environment
should a release enter the environment.
3)
A copy of the petition for alternative design and operating
practices or,
if such have already been granted,
a copy of
the
Board Order granting alternative design and operating
pract ices-~-j
i)
Description of controls and practices to prevent spills and
overflows,
as required under
35
Ill.
Adm.
Code 724.294(b);
and
j)
For tank systems in which ignitable, reactive or incompatible
wastes are to be stored or treated,
a description of how operating
procedures and tank system and facility design will achieve
compliance with the requirements of
35
Ill.
Adm. Code 724.298 and
724.299,’-;
and
19
~cJ,
Information on air emission control equipment,
as required in
Section 703.213.
(-Board N0tOBOARD NOTE:
See 40 CFR 270.16
(198694),
as amended at
5&~Fed.
Reg.
25471,
July
14,
198662952
(Dec.
6,
1994).-)-
(Source:
Amended at
19
Ill.
Peg.
________,
effective
______________________
Section 703.203
Surface Impoundments
For facilities that store,
treat1, or dispose
of hazardous waste in surface
impoundments, except as otherwise provided in 35 Ill.
Adm.
Code 724.101, the
Part
B application must
include:
a)
A list of the hazardous wastes placed or to be placed
in each
surface impoundmentf1,
b)
Detailed plans and an engineering report describing how the
surface impoundment
is designed and is or will be constructed,
operated1, and maintained to meet the requirements
of 35
Ill.
Adm.
Code 724.119,
724.321,
724.322 and 724.323, 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
sought1, as provided by
35
Ill.
Adm.
Code
724.321(b),
submit
a copy of the Board order granting an
adjusted standard pursuant to 35
Ill.
Adm. Code 724.321(b);
2)
The
double
liner
and leak (leachate) detection,
collection1,
and removal
system,
if the surface impoundment must meet the
requirements of
35
Ill.
Adm.
Code 724.321(c).
If an
exemption from the requirements for double liners and a leak
detection,
collection1, and removal system or alternative
design is sought as provided by 35
Ill. Adm. Code
724.321(d),
(e)1, or
(f),
submit appropriate information;
3)
If the leak detection system
is located in a saturated zone,
submit detailed plans and an engineering report explaining
the leak detection system design and operation-,- and the
location of the saturated zone in relation to the leak
detection system;
4)
The construction quality assurance
(CQA) plan if required
under
35
Ill.
Adxn. Code 724.119; and
5)
Proposed action leakage rate, with rationale,
if required
under 35
Ill.
Adm. Code 724.322,-i response action plan,
if
required under
35
Ill.
Adm. Code
724.323-,-.~and a proposed
pump operating level,
if
required under
35
111.
Adm. Code
724.326(d) (3);
6)
Prevention of overtopping; and
7)
Structural
integrity of dikes~~,
c)
A description of how each surface impoundment,
including the
double liner system, leak detection system, cover system and
appurtenances for control of
overtopping-,- will be inspected in
order to meet the requirements of
35
Ill. Adm. Code 724.326(a),
(b)1, and
(d).
This information must be included
in the inspection
plan submitted under Section 703.183(e)t1,
20
d)
A certification by
a qualified engineer which attests to the
structural integrity of each dike,
as required under
35
Ill.
Adxn.
Code 724.326(c).
For new units, the owner or operator shall
submit a statement by a qualified engineer that the engineer will
provide such a certification upon completion of construction in
accordance with the plans and apecificationsj-1,
e)
A description of the procedure to be used for removing a surface
impoundment from service,
as required under 35
Ill. Acm. Code
724.327(b) and
(C).
This information must be included in the
contingency plan submitted under Section 703.183(g)j..
f)
A description of how hazardous waste residues and contaminated
materials will be removed from the unit at closure,
as required
under 35 Ill.
Adm. Code 724.328(a)(1).
For any wastes not to be
removed from the unit upon closure,
the owner or operator shall
submit detailed plans and an engineering report describing how 35
Ill.
Adm. Code 724.328(a)(2)
and
(b)
will be complied with.
This
information must be included in the closure plan and, where
applicable,
the
post—closure
plan
submitted
under
Section
703.183(m)-i-.
g)
If ignitable or reactive wastes are to be placed
in a surface
impoundment,
an explanation of how 35
Ill. Adm.
Code 724.329 will
be complied withj-1,
h)
If incompatible wastes,
or incompatible wastes and materials,
will
be placed in
a surface impoundment,
an explanation
of how 35 Ill.
Adm. Code 724.330 will be complied with;
and,1,
i)
A waste management plan for hazardous waste numbers FO2O,
F021,
F022,
F023,
F0261, and FO27 describing how the surface impoundment
is or will be designed,
constructed, operated1, and maintained to
meet the requirements of 35
Ill.
Adm.
Code 724.331.
This
submission must address the following items as specified
in that
Section:
1)
The volume,
physical1, 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.
jj
Information on air emission control equipment,
as required
in
Section 703.213.
BOARD NOTE: Derived
from 40 CFR 270.17 (199~4),as amended at 5~
Fed.
Peg.
3486,
January
29,
199262952
(Dec.
6,
1994).
(Source:
Amended at
19
Ill.
Peg.
________,
effective
______________________
Section 703.213
Air Emieaion Controla for Tanka,
Surface Im~oundmante,and
Containers
Except
as otherwise provided
in 35
Ill.
Adm. code 724.101, owners and
21
operators
of tanks, surface
impoundments,
or containers that use air emission
controls in accordance with the requirements of
35
Ill. Adm. Code 724.Subpart
CC
shall
provide
the
following
additional
information:
~j,
Documentation
for
each
cover installed on
a tank subject to 35
Ill.
Adnh.
Code 724.984(b) (2) or 724.984(b) (3) that includes
information ~re~ared by the owner or operator or provided by the
cover manufacturer or vendor describing the cover design,
and
certification by the owner or operator that the cover meets the
applicable design
Bpecifications as listed in 35
Ill.
Adin.
Code
725.991(c).
~
Identification of
each container area subiect to the requirements
of
35 Ill.
Adxn.
Code 724.Subpart CC and certification by the owner
or operator that the requirements of this Subpart are met.
~j.
Documentation for each enclosure used to control air emissions
from containers
in accordance with the requirements of
35
Ill.
Adm. Code 724.986(b)(2)(A) that includes information prepared by
the owner or operator or provided by the manufacturer or vendor
describing the enclosure design, and certification by the owner or
operator that the enclosure meets the specifications listed in
35
Ill. Adm. Code 725.987(b)2)(B).
~j.
Documentation for each floating membrane cover installed on a
surface impoundment in accordance with the requirements of
35
Ill.
Adm. Code 724.985(c) that includes information prepared by the
owner or operator or provided by the cover manufacturer or vendor
describing the cover design, and certification by the owner or
operator that the cover meets the specifications listed
in
35 Ill.
Adm. Code 725.986(e).
~j.
Documentation for each closed-vent system and control device
installed
in accordance with the requirements of
35
Ill.
Adm. Code
724.987 that includes design and performance information as
specified in
703.24(c)
and
(d).
~
An emission monitoring plan
for
both
Method
21
and control device
monitoring methods.
This plan must include the following
information: monitoring
points,
monitoring methods for control
devices, monitoring frequency, procedures
for documenting
exceedances,
and procedures
for mitigating noncompliances.
gJ.
When an owner or operator of a facility sub~jectto
35
Ill. Adm.
Code 725.Subpart
CC cannot comply with
35
Ill. Adm. Code
724.Subpart
CC by the date of permit
issuance, the schedule of
implementation required under
35
Ill.
Adm.
Code 725.982.
BOARD NOTE:
Derived from 40 CFR 270.27, added at
59 Fed. Req.
62952
(Dec.
6,
1994).
(Source:
Added at
19
Ill.
Peg.
________,
effective
_____
TITLE 35:
ENVIRONMENTAL PROTECTION
SUBTITLE G:
WASTE DISPOSAL
CHAPTER
I:
POLLUTION CONTROL BOARD
SUBCHAPTER
b:
PERMITS
PART
705
PROCEDURES
FOR
PERMIT
ISSUANCE
22
SUBPART A:
GENERAL PROVISIONS
Section
705.101
Scope and Applicability
705.102
Definitions
705.103
Computation of Time
SUBPART B:
PERMIT APPLICATIONS
Section
705.121
Permit Application
705.122
Completeness
705.123
Incomplete Applications
705.124
Site Visit
705.125
Effective Date
705.126
Decision Schedule
705.127
Consolidation of Permit Processing
705.128
Modification of Permits
SUBPART C:
APPLICATION REVIEW
Section
705.141
Draft Permits
705.142
Statement of Basis
705.143
Fact Sheet
705.144
Administrative
Record
for
Draft
Permits or Notices of
Intent to
Deny
SUBPART D:
PUBLIC NOTICE
Section
705.161
When Public Notice Must Be Given
705.162
Timing of Public Notice
705.163
Methods of Public Notice
705.164
Contents of PubLic Notice
705.165
Distribution of Other Materials
SUBPART E:
PUBLIC COMMENT
Section
705.181
Public
Comments
and
Requests for Public Hearings
705.182
Public Hearings
705.183
Obligation to Raise Issues and Provide Information
705.184
Reopening of Public Comment Period
SUBPART F:
PERMIT ISSUANCE
Section
705.201
Final Permit Decision
705.202
Stay
upon Timely Application for Renewal
705.203
Stay for New Application or upon Untimely Application for Renewal
705.204
Stay upon Reapplication or for Modification
705.205
Stay Following Interim
Status
705.210
Agency Response to Comments
705.211
Administrative
Record
for Final Permits or Letters of Denial
705.212
Appeal of Agency Permit Determinations
Appendix A:
Procedures for Permit Issuance
Appendix B: Modification Process
Appendix
C:
Application
Process
Appendix D: Application Review Process
Appendix E:
Public Comment Process
Appendix F:
Permit Issuance or Denial
AUTHORITY:
Implementing Sections
13 and 22.4 and authorized by Section 27 of
the Environmental Protection Act (415 ILCS 5/13,
22.4 and 27).
SOURCE:
Adopted in R81—32,
47 PCB
93,
at 6
Ill.
Peg.
12479,
effective May 17,
23
1982;
amended in R82—l9,
at
7
Ill.
Peg.
14352,
effective
May
17,
1982;
amended
in
P84—9,
at
9
Ill.
Peg.
11894, effective July 24,
1985;
amended in P89—2 at
14
Ill. Peg.
3082, effective February 20,
1990; amended in P94—S at
18
Ill.
Peg.
18265, effective December 20,
1994;
amended in P95—6
at
19
Ill.
Peg.
effective
_____________________
SUBPART
B:
PERMIT APPLICATIONS
Section 705.128
Modification of Permits
a)
The Agency may modify a
pPermite may
be modified either at the
request of
any interested person
(including the permittee) or
t*~on
the Agcncy’oits own initiative.
However, the Agency may only
modify a permits may only be modified for the reasons specified in
35
Ill.
Adm. Code 704.261 through 704.263 or
35
Ill.
Adin. Code
703.270 through 703.273. A~ requeste for permit modification
ehallmust be made in writing1, must be addressed to the Agency
(Division of Land Pollution Control)1, and chalimust contain facts
or reasons
supporting the request.
b)
If
the Agency decidesdetermines that ~4’~e~request
for modification
is not justified,
it shall send the requester a brief written
response
giving
a reason
for the decisiondetermination.
~
~Deniale of ~requeste
for
modification
a~ej~not subject to
public notice,
comment1, or public hearinge requirements.
The
requester may appeal
a d~enialof a request to modify a permitmay
be
appealed
to
the
Board
pursuant
to
35
Ill.
Adm. Code 105.
C)
Agency Modification Procedures
1)
If the Agency tentatively decides to initiate steps to
modify a permit under this e~ectionand 35
ILl. Adm. Code
704.261 through 704.263 or 35
Ill.
Adm.
Code 703.270 through
703.273,
it shall,
after giving public notice pursuant to
Section 705.161(a) (1),
as though an application had been
received
(Ccc.
705.161(a)(1)),
it shall prepare a draft
permit under Sec-~-tion705.141 incorporating the proposed
changes.
The Agency may request additional information and
may require the submission of an updated permit application.
For reissued permits, the Agency shall require the
submission of
a new application.
2)
In
a permit modification proceeding under this e~ection,
only those conditions to be modified
shall be reopened when
a new draft permit
is prepared.
During any modification
proceeding,
including any appeale if anyto the Board,
the
permittee
shall
comply
with
all
conditions
of
t4~ej~,g
existing
permit
until
a
new
final
permit
is
reissued.
3)
“Minor modifications”1, as defined
in 35 Ill.
Adm. Code
704.2641, and “Class
1 and
2 modifications,”
as defined in 35
Ill.
Adm.
Code 703.281 and 703.282, are not subject to the
requirements of this e~ection.
If the Agency makes
a minor
modification,
the modified permit must be accompanied by a
letter stating the reasons for the minor modification.
d)
To the extent that the Agency has authority to terminate or
reissue permits,
if
it dooidos to do
so,
it must prepare
a draft
permit or notice of intent to deny in accordance with Section
705.141
if
it decides to do so.
24
e)
The
Agency or any person may seek the revocation of a permit in
accordance with Title VIII of the Environmental Protection Act and
in
aooordanoo
~iththe
procedure of
35
Ill.
Adm.
Code
103.
Revocation
may
only
be sought only for those reasons specified in
35
Ill. Adm. Code 702.186(a) through
(d).
(Board N0tQBOARD NOTE:
Derived from 40 CFP 124.5
(1986~j),
amended at
53
Fed.
flog.
3793~1, September 26,
1988).
(Source:
Amended at 19
Ill. Peg.
________,
effective
_____________________
TITLE 35:
ENVIRONMENTAL PROTECTION
SUBTITLE G:
WASTE DISPOSAL
CHAPTER
I:
POLLUTION
CONTROL
BOARD
SUBCHAPTER
C:
HAZARDOUS WASTE OPERATING REQUIREMENTS
PART 720
HAZARDOUS WASTE MANAGEMENT SYSTEM:
GENERAL
SUBPART A:
GENERAL PROVISIONS
Section
720.101
Purpose,
Scope and Applicability
720.102
Availability
of
Information;
Confidentiality
of
Information
720.103
Use
of
Number
and
Gender
SUBPART
B:
DEFINITIONS
Section
720.110
Definitions
720.111
References
SUBPART C:
RULEMAKING PETITIONS AND OTHER PROCEDURES
Section
720.120
Rulemaking
720.121
Alternative Equivalent Testing Methods
720.122
Waste
Delisting
720.130
Procedures for Solid Waste Determinations
720.131
Solid
Waste
Determinations
720.132
Boiler Determinations
720.133
Procedures for Determinations
720.140
Additional regulation of certain hazardous waste Recycling
Activities on a case—by-case Basis
720.141
Procedures for case—by—case regulation of hazardous waste
Recycling Activities
720.Appendix A
Overview
of
40
CFR,
Subtitle
C
Regulations
AUTHORITY:
Implementing Section 22.4 and authorized by Section 27
of the
Environmental Protection Act
(415 ILCS 5/22.4 and 27).
SOURCE:
Adopted
in P81-22,
43 PCB
427,
at
5 Ill.
Peg.
9781,
effective
as
noted
in 36 Ill. Adm. Code 700.iO6May
17, 1982
amended and codified in P81—
22,
45
PCB 317,
at 6
Ill. Peg.
4828,
effective ac noted
in
35
Ill.
Adm.
Code
700.lOGMay
17, 1982
amended in P82—19 at
7
Ill.
Peg.
14015, effective October
12,
1983;
amended
in R84—9,
53
PCB
131
at
9
Ill. Peg.
11819, effective July
24,
1985; amended
in P85—22
at
10
Ill.
Peg.
968, effective January 2,
1986;
amended in P86—i at
10
Ill.
Peg.
13998, effective August 12,
1986; amended in
P86—19 at 10 Ill.
Reg.
20630, effective December
2,
1986; amended in P86—28 at
11 Ill.
Peg. 6017,
effective March 24,
1987; amended in R86—46 at
11 Ill. Peg.
13435, effective August
4,
1987;
amended
in R87—5 at
11
Ill.
Peg.
19280,
effective November 12,
1987;
amended in P87—26 at 12
Ill.
Peg.
2450, effective
January 15,
1988;
amended in R87—39 at
12 Ill. Reg.
12999, effective July 29,
25
1988;
amended
in P88—16 at
13
Ill. Reg.
362, effective December 27,
1988;
amended
in
P89—i
at
13
Ill.
Reg.
18278, effective November
13,
1989;
amended
in P89-2
at 14
Ill.
Peg.
3075,
effective February 20,
1990;
amended in P89—9
at 14
Ill. Peg.
6225, effective April
16,
1990;
amended in R90—10 at
14
Ill.
Peg.
16450, effective September 25,
1990;
amended in R90—17
at
15
Ill. Reg.
7934,
effective May 9, 1991;
amended in P90—11 at
15
Ill.
Peg.
9323,
effective
June 17,
1991;
amended in P91—i at
15
Ill. Peg.
14446,
effective September 30,
1991;
amended in P91—13 at
16
Ill. Peg.
9489, effective June
9,
1992;
amended
in P92—i at 16
Ill. Peg.
17636, effective November
6,
1992;
amended in P92—10
at
17
Ill. Peg.
5625, effective March 26,
1993;
amended in P93—4 at
17
Ill.
Peg.
20545, effective November 22,
1993; amended in P93—16 at 18
Ill. Peg.
6720,
effective April 26,
1994; amended in P94—7 at
18 Ill. Peg.
12160,
effective July 29,
1994; amended in R94-l7
at
18 Ill. Peg.
17480, effective
November
23,
1994;
amended in P95-6 at 19
Ill.
Req.
________,
effective
SUBPART
B:
DEFINITIONS
Section
720.111
References
a)
The
following
publications
are
incorporated
by
reference:
ANSI.
Available
from
the
American
National
Standards
Institute,
1430
Broadway,
New
York,
New
York
10018,
212—
354-3300:
ANSI
B3l.3 and B31.4.
See ASME/ANSI
B31.3 and B31.4
Ad.
Available from the American Concrete Institute, Box
19150,
Redford
Station,
Detroit,
Michigan
48219:
ACI
318—83:
“Building
Code
Requirements
for
Reinforced Concrete”, adopted September,
1983.
API.
Available
from
the
American
Petroleum
Institute,
1220
L
Street,
N.W.,
Washington,
D.C.
20005,
202—682—8000;
“Cathodic Protection of Underground Petroleum Storage
Tanks
and
Piping
Systems”,
API
Recommended
Practice
1632,
Second
Edition,
December,
1987.
“Evaporative Loss from External Floating—Roof Tanks”,
API
Publication 2517,
Third Edition,
February,
1989.
“Guide for Inspection of Refinery Equipment,
Chapter
XIII,
Atmospheric and Low Pressure Storage Tanks,” 4th
Edition,
1981,
reaffirmed
December,
1987.
“catnoa~i.c
Tanks
and
rrotcction
Piping
Syst
or
unaergrounci
ictroicum
storage
ems,”
API
Recommended
Practise
December,
1987.
1632,
Second
Edition,
“Installation of Underground Petroleum Storage
Systems,” API Recommended Practice 1615,
Fourth
Edition,
November,
1987.
APTI.
Available from the Air and Waste Management
Association,
Box 2861,
Pittsburgh,
PA
15230, 412—232—3444:
APTI Course 415:
Control of Gaseous Emissions, U.S.
EPA Publication EPA—450/2—81—O05,
December,
1981.
26
ASME.
Available from the American Society of Mechanical
Engineers, 345 East 47th Street, New York,
NY
10017,
212—
705—7722:
“Chemical Plant and Petroleum Refinery Piping”, ASME/
ANSI
B31.3—1987,
as supplemented by B3i.3a—1988 and
B31.3b-1988.
Also available from ANSI.
“Liquid Transportation Systems for Hydrocarbons,
Liquid Petroleum Gas, Anhydrous Ammonia,
and
Alcohols”, ASME/ANSI B31.4—1986,
as supplemented by
B3l.4a-1987.
Also available from ANSI.
ASTM.
Available from American Society for Testing and
Materials,
1916 Race Street,
Philadelphia,
PA 19103,
215—
299—5400:
ASTM C_94—90, Standard Specification for Ready—Mixed
Concrete,
approved March 30,
1990.
ASTM
D_88—87,
Standard
Test Method for Saybolt
Viscosity, April 24,
1981, reapproved January,
1987.
ASTM D_93—85,
Standard Test Methods for Flash Point by
Pensky—Martens Closed Tester, approved October 25,
1985.
ASTM D_1946—90,
Standard Practice for Analysis of
Reformed Gas by Gas Chromatography, Approved March
30,
1990.
ASTM D_2161-87,
Standard Practice for Conversion of
Kinematic Viscosity to Saybolt Universal or to Saybolt
Furol Viscosity, March 27,
1987.
ASTM D_2267-88,
Standard Test Method for Aromatics in
Light Naphthas and Aviation Gasolines by Gas
Chromatography, approved November
17,
1988.
ASTM D_2382-88,
Standard Test Method for Heat of
Combustion of Hydrocarbon Fuels by Bomb Calorimeter
(High
Precision
Method),
approved
October
31,
1988.
ASTM
D_2879—86,
Standard
Test
Method
for
Vapor
Pressure—Temperature Relationship and Initial
Decomposition Temperature of Liquids by Isoteniscope,
approved October
31,
1986.
ASTM
D
2879-92, Standard Test Method for Vapor
Pressure—Temperature Relationship and Initial
Decomposition Temperature of Liquids by Isoteniscope,
approved
1992.
ASTM D_3828—87, Standard
Test
Methods
for
Flash
Point
of Liquids by Setaflash Closed Tester, approved
December
14,
1988.
ASTM E_168—88,
Standard Practices for General
Techniques of Infrared Quantitative Analysis, approved
May 27,
1988.
ASTM
E_169—87,
Standard
Practices
for
General
27
Techniques of Ultraviolet—Visible Quantitative
Analysis,
approved February
1,
1987.
ASTM E_260—85,
Standard Practice for Packed Column Gas
Chromatography, approved June 28,
1985.
ASTM
E_926—88
C,
Standard
Test
Methods
for
Preparing
Refuse-Derived
Fuel
(RDF)
Samples
for
Analysis
of
Metals,
Bomb—Acid Digestion Method, approved March 25,
1988.
ASTM Method G_21—70
(1984a)
--
Standard
Practice
for
Determining Resistance of Synthetic Polymer Materials
to Fungi
ASTM Method G_22—76
(1984b)
-—
Standard Practice for
Determining Resistance of Plastics to Bacteria.
GPO.
Available from the Superintendent of Documents, U.S.
Government Printing Office,
Washington,
D.C.
20402,
202—
783—3238:
Standard
Industrial
Classification
Manual
(1972),
and
1977 Supplement,
republished
in 1983
“Test
Methods
for
Evaluating
Solid
Waste,
Physical!
Chemical Methods,” U.S. EPA Publication number SW—846
(Third Edition,
November,
1986),
as amended by Updates
I
and
IIA
(Document
Number
955—001—00000—1)
(contact
U.S. EPA, Office of Solid Waste,
or MICE,
as indicated
below,
for Update hA).
MICE.
Available from Methods Information Communication
Service,
at 703—821—4789:
“Test Methods for Evaluating Solid Waste,
Physical/
Chemical Methods,” U.S. EPA Publication number SW—846
(Third Edition,
November,
1986),
Update
IIA
(Document
Number 955—001—00000—1)
(contact GPO,
as indicated
above,
for SW—846 and Update I).
NACE.
Available from the National Association of Corrosion
Engineers,
1400
South Creek Dr., Houston, TX
77084,
713—
492—0535:
“Control of External Corrosion on Metallic Buried,
Partially
Buried,
or
Submerged
Liquid
Storage
Systems”,
NACE Recommended Practice RP0285-85,
approved March,
1985.
NFPA.
Available from the National Fire Protection
Association, Batterymarch Park,
Boston, MA
02269,
617-770—
3000 or 800—344—3555:
‘Flammable and Combustible Liquids Code” NFPA 30,
issued
July
17,
1987.
Also available from ANSI.
NTIS.
Available
from the U.S. Department of Commerce,
National
Technical
Information
Service,
5285
Fort
Royal
Road,
SpringfieLd,
VA
22161,
703—487—4600:
“Generic Quality Assurance Project Plan for Land
28
Disposal Restrictions Program”, EPA/530—SW—87—011,
March
15,
1987.
(Document number PB 88—170766.)
“Guidance on Air Quality Models”, Revised 1986.
(Document number PB86-245—248
(Guideline)
and PB88—
150-958
(Supplement)).
“Methods for Chemical Analysis of Water and Wastes”,
Third Edition, March,
1983.
(Document number PB 84—
128677).
“Methods Manual for Compliance with BIF Regulations”,
December,
1990.
(Document number PB91—120—006).
“Petitions to Delist Hazardous Wastes
——
A Guidance
Manual”, EPA/530—SW—85—003, April,
1985.
(Document
Number PB 85—194488).
“Procedures Manual for Ground Water Monitoring at
Solid Waste Disposal Facilities”,
EPA—530/SW—611,
1977,
(Document number PB 84—174820).
“Screening Procedures for Estimating the Air Quality
Impact of Stationary Sources”, October,
1992,
Publication
Number
EPA—450/R—92—019.
STI.
Available from the Steel Tank Institute, 728 Anthony
Trail, Northbrook,
IL
60062,
708—498—1980:
“Standard for Dual Wall Underground Steel Storage
Tanks”
(1986).
U.S. EPA.
Available from United States Environmental
Protection Agency, Office of Drinking Water,
State Programs
Division, WH 550 E, Washington,
D.C.
20460:
“Technical Assistance Document:
Corrosion,
Its
Detection and Control in Injection Wells”, EPA 570/9—
87—002,
August,
1987.
U.S. EPA.
Available from U.S.
EPA, Office of Solid Waste
(Mail Code 5304),
401
14 Street
SW, Washington,
D.C.
20460:
“Test Methods for Evaluating Solid Waste,
Phyeical/
Chemical Methods,” U.S. EPA Publication number SW—846
(Third Edition, November,
1986), Update hA
(Document
Number 955—001-00000-1)
(contact GPO,
as indicated
above,
for SW—846 and Update I).
U.S.
EPA.
Available from U.S. EPA, Number F-90-WPWF-FFFFF,
Room M2427,
401 M Street SW, Washington,
D.C.
20460,
202—
475—9327:
“Test Method 8290:
Procedures for the Detection and
Measurement of PCDD5 and PCDF5”, EPA/530—SW—91-019
(January,
1991)
U.S. EPA.
Available from Receptor Analysis Branch,
U.S. EPA
(MD—14),
Research Triangle Park, NC
27711:
“Screening Procedures for Estimating the Air Quality
Impact of Stationary Sources,
Revised”, October,
1992,
29
Publication Number EPA—450/R—92—019.
b)
Code
of Federal Regulations.
Available from the Superintendent of
Documents,
U.S.
Government Printing Office,
Washington,
D.C.
20401,
202—783—3238:
10 CFR 20,
Appendix B (19934)
40 CFP 51.100(u)
(1993k)
40 CFP 51,
Subpart W,
as added at
58 Fed.
Peg.
38822
(July
20,
1993)-
(1994)
40 CFR 60
(19934),
as amended at 59 Fed.
Peg.
62924
(Dec.
6,
1994)
40 CFR 61,
Subpart V
(19934)
40 CFR 136 (l993~)
40 CFR 142
(19934)
40 CFR 220
(19924)
40 CFR 260.20 (199)
40 CFR 264
(19924)
40
CFR 268.Appendix IX
(19934)
40 CFR 302.4,
302.5
and 302.6
(19924)
40 CFP 761 (19934)
49 CFR 178
(1994)
c)
Federal Statutes
Section 3004 of the Resource Conservation and Recovery Act
(42
U.S.C.
6901 et
seq.),
as amended through December
31,
1987.
d)
This Section incorporates no later editions or amendments.
(Source:
Amended at
19
Ill. Peg.
________,
effective
______________________
SUBPART
C:
RULEMAKING PETITIONS AND OTHER PROCEDURES
Section 720.121
Alternative Equivalent Testing Methods
a)
The Agency has
rio
authority to alter the universe of regulated
wastes.
Modification of testing methods whichthat are stated in
Part3S
Ill.
Adxn.
Code 721 requires rulemaking pursuant to Section
720.120.
However, deviation from these methods is allowed under
the c~prcooprovisions of Part3S
Ill. Adm.
Code 721,
as for
example in Sootionby 35
Ill. Adm. Code 721.120(c).
b)
The Agency may approve alternative equivalent testing methods te
befor a
particular person’s used by
a certain person to determine
whether specified types of waste streams are subject to these
regulations.
This
shall be done by permit condition or by a
letter directed to the
person.
30
c)
The Board does
riot intend to require that either the testing
methods specified in Part3S
Ill.
Adm.
Code 721 or the alternative
equivalent testing methods approved by the Agency shouldneed not
be applied to identify or distinguish waste streams whichthat are
known,
admitted1, or assumed to be subject to these regulations.
In this case,
any method may be used,
subject to the Agency’s
authority over testing procedures
(Section 725.113).
d)
Any petition to the Board or request to the Agency concerning
alternative equivalent testing methods ohallmust include the
information required by 40 CFR Section 260.2ljj2J~.
e~
Alternative equivalent testing methods will not be approved if the
result of the aPproval would make the Illinois
RCR.A
Subtitle C
program less than substantially equivalent to the federal.
(Source:
Amended at
19
Iii.
Peg.
________,
effective
_____________________
Section 720.130
Procedures
for Solid Waste Determinations
In accordance with the standards and criteria in Section 720.131 and the
procedures in Section 720.133,
the Board will determine on a case—by—case
basis that the following recycled materials are not
solid wastes:
a)
Materials that are accumulated speculatively without sufficient
amounts being recycled
(as defined in Section 721.101(c)(8))i-~
b)
Materials that are reclaimed and then reused within the original
primary production process
in which they were generated;
and
c)
Materials that have been reclaimed but must be reclaimed further
before the materials are completely recovered.
(Source:
Amended
at
19
Ill. Peg.
________,
effective
______________________)
Section 720.131
Solid Waste Determinations
a)
The Board will determine that those materials that are accumulated
speculatively without sufficient
amounts being recycled are not
solid wastes if the applicant demonstrates that sufficient amounts
of the material will be recycled or transferred for recycling in
the following year.
Such a determination
is valid only for the
following year,
but can be renewed,
on an annual basis,
by filing
a new application.
This determination will be based on the
following criteria:
1)
The manner in which the material
is expected to be recycled,
when the material is expected to be recycled,
and whether
this expected disposition
is likely to occur
(for example,
because
of past practice, market
factors, the nature of the
material or contractual arrangements for recycling);
2)
The reason that the applicant has accumulated the material
for one or more years without recycling
75 percent of the
volume accumulated at the beginning of the year;
3)
The quantity of material already accumulated and the
quantity expected to be generated and accumulated before the
material
is recycled;
4)
The extent to which the material
is handled to minimize
loss;
and
31
5)
Other relevant factors.
b)
The Board will determine that those materials that are reclaimed
and then reused as feedstock within the original primary
production process in which the materials were generated are not
solid wastes
if the reclamation operation
is an essential part of
the
production
process.
This
determination
will
be
based
on
the
following criteria:
1)
How economically viable the production process would be
if
it were to use virgin materials, rather than reclaimed
materials;
2)
The prevalence of the practice on an industry—wide basis;
3)
The extent to which the material is handled before
reclamation to minimize loss;
4)
The time periods between generating the material and its
reclamation,
and
between
reclamation
and
return
to
the
original primary production process;
5)
The location of the reclamation operation in relation to the
production process;
6)
Whether the reclaimed material
is used for the purpose for
which
it was originally produced when
it
is returned to the
original process,
and whether it is returned to the process
in substantially its original form;
7)
Whether the person whethat generates the material also
reclaims it; and
8)
Other relevant factors.
C)
The
Board
will determine that those materials that have been
reclaimed but must be reclaimed further before recovery
is
completed are not solid wastes
if,
after initial reclamation,
the
resulting material
is commodity-like
(even though
it
is not yet a
commercial product,
and has to be reclaimed further).
This
determination will be based on the following criteria:
1)
The degree of processing the material has undergone and the
degree of
further processing that is required;
2)
The value of the material after it has been reclaimed;
3)
The degree to which the reclaimed material is like an
analogous raw material;
4)
The extent to which an end market for the reclaimed material
is guaranteed;
5)
The extent to which the reclaimed material
is handled to
minimize loss; and
6)
Other relevant factors.
(Source:
Amended
at
19
Ill.
Reg.
________,
effective
—
TITLE
35:
ENVIRONMENTAL
PROTECTION
32
SUBTITLE G:
WASTE DISPOSAL
CHAPTER
I:
POLLUTION CONTROL BOARD
SUBCHAPTER
c:
HAZARDOUS WASTE OPERATING REQUIREMENTS
PART 721
IDENTIFICATION AND LISTING OF HAZARDOUS WASTE
SUBPART A:
GENERAL PROVISIONS
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
Criteria for
Identifying the Characteristics of Hazardous Waste
Criteria
for
Listing
Hazardous
Waste
SUBPART C:
CHARACTERISTICS OF HAZARDOUS WASTE
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
Wood Preserving Wastes
72l.Appendix A
721.Appendix B
72l.Appendix C
Table A
Table B
Table C
721.Appendix G
721.Appendix H
721.Appendix
I
Table A
Table B
Table
C
Representative Sampling Methods
Method 1311 Toxicity Characteristic Leaching Procedure
(TCLP)
Chemical Analysis Test Methods
Analytical Characteristics of Organic Chemicals
(Repealed)
Analytical Characteristics of Inorganic Species
(Repealed)
Sample Preparation/Sample Introduction Techniques
(Repealed)
Basis for Listing Hazardous Wastes
Hazardous Constituents
Wastes Excluded under Ceotion
720. 120 and 72O.122~y
Administrative Action
Wastes Excluded by U.S. EPA under 40 CFR 260.20 and 260.22
from Non—Specific Sources
Wastes Excluded bY U.S. EPA under 40 CFR 260.20 and 260.22
from Specific Sources
Wastes Excluded by U.S. EPA under 40 CFR 260.20
and 260.22
f~romCommercial Chemical Products, Off-Specification
Species, Container Residues,
and Soil Residues Thereof
Wastes Excluded by the Board by Adjusted Standard
Method of Analysis for Chlorinated Dibenzo-p—Dioxins and
Section
721. 101
721.
102
721.
103
721.104
721. 105
721.
106
721. 107
721. 108
Section
721. 110
721.111
Section
721.120
721.121
721.122
721. 123
721. 124
Section
721. 130
721. 131
721.132
721. 133
721. 135
General
Characteristic of
Ignitability
Characteristic of Corrosivity
Characteristic of Reactivity
Toxicity Characteristic
Table D
721.Appendix J
33
Dibenzofurans (Repealed)
721.Appendix
Z
Table to Section 721.102
AUTHORITY:
Implementing Section 22.4 and authorized by Section 27 of the
Environmental Protection Act
(415 ILCS
5/22.4 and 27.
SOURCE:
Adopted in P81—22,
43 PCB 427,
at
5 Ill.
Peg. 9781, effective ae
noted
in
35 Ill.
1idm.
Code 700.lO6May
17,
1982
amended and codified in P81-
22,
45 PCB 317,
at 6 Ill. Reg. 4828,
effective as noted in 35 Ill. Adm.
Code
as noted
in
35
Ill. Mm.
Code 700.1O6May
17, 1982 amended in P82-18,
51 PCB
31,
at
7
Ill.
Reg.
2518, effective February 22,
1983;
amended in R82—19,
53
PCB 131,
at
7
IlL. Peg.
13999, effective October 12,
1983; amended in P84—34,
61 PCB 247,
at
8
Ill. Peg.
24562, effective December
11,
1984;
amended in P84—
9,
at 9
Ill. Reg.
11834,
effective July 24,
1985; amended in P85—22 at
10 Ill.
Reg.
998, effective January
2,
1986;
amended
in P85—2 at 10
Ill.
Reg.
8112,
effective May
2,
1986;
amended in P86—i
at
10 Ill.
Reg.
14002, effective
August
12,
1986;
amended
in R86—19 at 10 Ill.
Reg.
20647, effective December
2,
1986;
amended in P86—28 at
11
Ill. Reg.
6035,
effective March 24,
1987;
amended in P86-46 at 11
Ill. Peg.
13466, effective August
4,
1987;
amended in
P87—32 at
11 Ill. Peg.
16698, effective September 30,
1987;
amended in P87—S
at
11
Ill. Peg.
19303,
effective November
12,
1987;
amended in P87—26 at
12
Ill.
Peg.
2456,
effective January
15,
1988;
amended in P87—30 at
12 Ill. Peg.
12070, effective July 12,
1988; amended in P87—39
at
12
Iii.
Peg.
13006,
effective July 29,
1988;
amended
in P88—16
at
13
Ill.
Reg. 382,
effective
December 27,
1988;
amended in P89-i
at
13
Ill.
Peg.
18300, effective November
13,
1989;
amended in P90—2
at
14
Ill. Reg.
14401, effective August 22,
1990;
amended in P90—10
at
14
Ill. Peg.
16472, effective September
25,
1990;
amended
in P90—17 at
15
Ill. Peg.
7950, effective May
9,
1991;
amended in P90—il at
15
Ill.
Peg.
9332,
effective June
17,
1991;
amended
in P91—i
at
15
Ill. Peg.
14473, effective September 30,
1991;
amended
in P91—12
at 16 Ill.
Peg.
2155,
effective January 27,
1992;
amended in P91—26 at
16 Ill. Reg.
2600,
effective
February
3,
1992;
amended in P91—13 at
16
Ill.
Reg.
9519,
effective June
9,
1992;
amended in P92—i at
16
Ill.
Peg.
17666, effective November
6,
1992;
amended in P92—10
at
17
Ill. Peg.
5650,
effective March 26,
1993;
amended in
P93—4
at
17 Ill. Peg.
20568, effective November
22,
1993;
amended
in P93—16 at
18
Ill. Peg.
6741, effective April
26,
1994;
amended
in P94—7
at
18
Ill.
Peg.
12175, effective July 29,
1994;
amended in R94—17
at
18 Ill. Peg.
17490,
effective November 23,
1994;
amended in P95-6 at
19
Ill. Peg.
________
effective
______________________
SUBPART A: GENERAL PROVISIONS
Section 721.102
Definition of Solid Waste
a)
Solid waste.
1)
A solid waste
is any discarded material that is not excluded
by Section 721.104(a)
or that
is not excluded pursuant to 35
Ill.
Adm.
Code 720.130 and 720.131.
2)
A discarded material
is any material whichthat
is:
A)
Abandoned,
as explained in subsection
(b)T below; or
B)
Recycled,
as explained in subsection
(c).r below; or
C)
Considered inherently waste—like,
as explained in
subsection
(d).,. below.
b)
Materials are solid waste
if they are abandoned by being:
34
1)
Disposed of; or
2)
Burned or incinerated; or
3)
Accumulated,
stored or treated
(but not recycled) before or
in lieu of being abandoned by being disposed of, burned or
incinerated.
c)
Materials are solid wastes
if they are recycled——or accumulated,
stored or treated before recycling——as specified in subsections
(c) (1) through j.~j.(4)Tbelow,, if they are:
1)
Used in
a manner constituting disposal.
A)
Materials noted with a “yes” in column 1 of table in
Section 721.Appendix
Z are solid wastes when they are:
i)
Applied to or placed on the land in
a manner
that constitutes disposal; or
ii)
Used to produce products that are applied to or
placed on the land or are otherwise contained in
products that are applied to or placed on the
land (in which cases the product itself remains
a solid waste).
B)
However, commercial chemical products listed in
Section 721.133 are not solid wastes
if they are
applied to the land and that is their ordinary manner
of use.
2)
Burned for energy recovery.
A)
Materials noted with
a “yes”
in column 2 of table in
Section 721.Appendix
Z are solid wastes when they
are:
i)
burned to recover energy;
ii)
Used to produce a fuel or are otherwise
contained in fuels
(in which case the fuel
itself remains
a solid waste);
iii)
Contained in fuels
(in which case the fuel
itself
remains
a
solid
waste).
B)
However, commercial chemical products
listed in
Section 721.133 are not solid wastes
if they are
themselves fuels.
3)
Reclaimed.
Materials noted with
a “yes” in column 3 of
table in Section 721.Appendix
Z are solid wastes when
reclaimed.
4)
Accumulated speculatively.
Materials noted with “yes”
in
column 4 of table
in Section 721.Appendix
Z are solid wastes
when accumulated speculatively.
d)
Inherently waste—like materials.
The following materials are
solid wastes when they are recycled in any manner:
1)
Hazardous waste numbers F020,
F021
(unless used as an
ingredient to make a product at the site of generation),
35
F022,
F023,
F0261, and F028.
2)
Secondary materials fed to
a halogen acid furnace that
exhibit a characteristic of a hazardous waste or are listed
as
a hazardous waste as defined
in 72l.Subparts C or
D,
except for brominated material whichthat meets the following
criteria:
A)
The material must contain
a bromine concentration of
at
least 45;
and
B)
The material must contain less than a total of
1
of
toxic organic compounds listed in Section 721.Appendix
H;
and
C)
The material
is processed continually on—site in the
halogen acid furnace via direct conveyance
(hard
piping).
3)
The following criteria are used to add wastes to the list:
A)
Disposal method or toxicity.
i)
The materials are ordinarily disposed of,
burned1, or incinerated;
or
ii)
The materials contain toxic constituents listed
in Section 721.Appendix H and these constituents
are not ordinarily found
in raw materials or
products for which the materials
substitute (or
are found in raw materials or products
in
smaller concentrations) and are not used or
reused during the recycling process; and
B)
The material may pose
a substantial hazard to human
health and the environment when recycled.
e)
Materials that are not solid waste when recycled.
1)
Materials are not solid wastes when they can be shown to be
recycled by being:
A)
Used or reused as ingredients
in an industrial process
to make a product, provided the materials are not
being reclaimed; or
B)
Used or reused as effective substitutes for commercial
products; or
C)
Returned to the original process from which they are
generated,. without first being reclaimed.
The
materials must be returned as
a substitute for ~aw
materials feedstock materials,
and the process muot
usc raw materials as principal
fcedotocka.
In cases
where the original process to which the material is
returned
is
a secondary process, the materials must be
mana~ed so there
is no placement on the land.
2)
The following materials are solid wastes, even if the
recycling involves use,
reuse1, or return to the original
process
(described
in subsections
(e)(l)(A)
—through
(e)(1j(C),- abovej:
36
A)
Materials used in a manner constituting disposal’,- or
used to produce products that are applied to the land;
or
B)
Materials burned for energy recovery,
used to produce
a
fuel1, or contained
in fuels;
or
C)
Materials accumulated speculatively; or
D)
Materials listed
in subsections
(d)(1)
and
(d)(2)’~-
above.
f)
Documentation of claims that materials are not solid wastes or are
conditionally exempt from regulation.
Respondents in actions to
enforce regulations implementing Subtitle C of the Resource
Conservation Recovery Act or Section 21 of the Environmental
Protection Act whethat raise
a claim that a certain material
is
not a solid waste,- or that the material
is conditionally exempt
from regulation must demonstrate that there
is
a known market or
disposition for the material-,- and that they meet the terms of the
exclusion or exemption.
In doing
so,
they person must provide
appropriate documentation (such as contracts showing that
a second
person uses the material as
an ingredient
in
a production process)
to demonstrate that the material
is not
a waste,- or that the
material
is exempt from regulation.
In addition,
owners or
operators of facilities claiming that they actually are recycling
materials must show that they have the necessary equipment to do
so.
(Source:
Amended at
19
Ill.
Peg.
________,
effective
______________________
Section 721.103
Definition of Hazardous Waste
a)
A solid waste,
as defined in Section 721.102,
is
a hazardous waste
if:
1)
It
is not excluded from regulation as
a hazardous waste
under Section 721.104(b); and
2)
It meets any of the following criteria:
A)
It exhibits any of the characteristics of hazardous
waste identified in 721.Subpart C of this Part.
jj
Except that any mixture of
a waste from the
extraction,
beneficiation1, or processing of ores
or minerals excluded under Section 721.104(b) (7)
and any other solid waste exhibiting a
characteristic of hazardous waste under
721.Subpart C of this Part
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 occurredi-1,
or’,- if
it continues to exhibit any of the
characteristics exhibited by the non—excluded
wastes prior to mixture.
jfl
Further,
for the purposes of applying the
toxicity characteristic to such mixtures under
subsection (aH2)(A)(i)
above, the mixture
is
also a hazardous waste:
if
it exceeds the
maximum concentration for any contaminant listed
37
in Section 721.124 that would not have been
exceeded by the excluded waste alone
if the
mixture had not occurred*1,
or-,--
if
it continues
to exceed the maximum concentration for any
contaminant exceeded by the nonexenipt waste
prior to mixture.
B)
It
is listed in 721.Subpart D of this Part and has not
been excluded from the lists in 721.Subpart
D e~-thie
Part under 35
Ill. Adm. Code 720.120 and 720.122.
C)
It
is
a mixture of
a solid waste and a hazardous waste
that is listed in 721.Subpart D of this Part solely
because it exhibits one or more of the characteristics
of hazardous waste identified in 721.Subpart C of this
P-art, unless~
fl
the resultant mixture no longer exhibits any
characteristic
of
hazardous
waste
identified
in
721.Subpart C
of this Part,
or unless
j~fl.
the solid
wastei-
is excluded from regulation
under Section 721.104(b)(7)-~-and-,- the resultant
mixture no longer exhibits any characteristic of
hazardous waste identified in 721.Subpart
C—e4~
this Part for which the hazardous waste listed
in 721.Subpart D of this Part was listed.
iii)
~tIowcver,nNonwastewater mixtures are still
subject to the requirements of
35
Ill.
Adni.
Code
728, even
if they no longer exhibit a
characteristic at the point of
land disposal.)-.
D)
It
is
a mixture of solid waste and one or more
hazardous wastes listed in 72l.Subpart D of this
P-art
and has not
been excluded from this subsection
(a)(2)
under
35
Ill.
Adm.
Code 720.120 and 720.122;
however,
the following mixtures of solid wastes and hazardous
wastes listed
in 721.Subpart D of this Part are not
hazardous wastes
(except by application
of subsection
(a)(2)(A)
or
(a)(2)(B)
above)
if the generator
demonstrates that the mixture consists of wastewater
the discharge of which
is subject
to regulation under
either 35 Ill.
Adrn.
Code 309 or 310 (including
wastewater at facilities ~hichthat have eliminated the
discharge of wastewater)
and:
i)
One or more of the following solvents listed in
Section 721.131:
—
carbon tetrachloride, tetra-
chioroethylene,
trichloroethylene1, —provided
that the maximum total weekly usage of these
solvents
(other than the amounts that can be
demonstrated not to be discharged to wastewater)
divided by the average weekly flow of wastewater
into the headworks of the facility’s wastewater
treatment or pretreatment system does not exceed
1 part per million;
or
ii)
One or more of the following spent solvents
listed in Section 72l.131~
—
methylene chloride,
1,1,1
—
trichloroethane, chlorobenzene,
o—dichlorobenzene,
cresols,
cresylic acid,
38
nitrobenzene,
toluene, methyl ethyl ketone,
carbon disulfide,
isobutanol,
pyridine,
spent
chiorofluorocarbon solvents1, —provided that the
maximum total weekly usage of these solvents
(other than the amounts that can be demonstrated
not to be discharged to wastewater)
divided by
the average weekly flow of wastewater into the
headworks of the facility’s wastewater treatment
or pretreatment system does not exceed 25
parts
per million; or
Lii)
One of the following wastes listed in Section
72l.132~
—
heat exchanger bundle cleaning sludge
from the petroleum refining industry
(U.S. EPA
Mhazardous Wwaste Nno.
K050); or
iv)
A discarded commercial chemical product-,- or
chemical intermediate listed in Section 721.133-,-
arising from de minimis losses of these
materials from manufacturing operations
in which
these materials are used as raw materials or are
produced in the manufacturing process.
For
purposes of this subsection,
“de minimis” losses
include those from normal material handling
operations
(e.g.,
spills from the unloading or
transfer of materials
from bins or other
containers,
leaks from pipes,
valves1, or other
devices used to transfer materials);
minor leaks
of process equipment,
storage tanks1, or
containers;
leaks from well—maintained pump
packings and seals; sample purgings;
relief
device discharges; discharges from safety
showers and rinsing and cleaning of personal
safety equipment; and rinsate from empty
containers or from containers that are rendered
empty by that rinsing;
or
v)
Wastewater resulting from laboratory operations
containing toxic
(T) wastes listed in
721.Subpart D of this Part,
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 pretreatment
system-, or
provided that
the wastes combined annualized
average concentration does not exceed one part
per million in the headworks of the facility’s
wastewater treatment or pretreatment facility.
Toxic
(T) wastes used in laboratories that are
demonstrated not to be discharged to wastewater
are not to be included in this calculation.
E)
Rebuttable presumption for used oil.
Used oil
containing more than 1,000 ppm total halogens is
presumed to be a hazardous waste because
it has been
mixed with halogenated hazardous waste listed in
721.Subpart
D
of this Part.
Persons may rebut this
presumption by demonstrating that the used oil does
not contain hazardous waste
(for example, by using an
analytical method from SW-846,
3d cd., incorporated by
reference at 35
Ill.
Adm. Code 720.111,
to show that
the used oil does not contain significant
39
concentrations
of
halogenated
hazardous
constituents
listed in 72l.Appendix H).
i)
The rebuttable presumption does not apply to
metalworking oils or fluids containing
chlorinated paraff ins-i- if they are processed-,-
through a tolling arrangement
as described in 35
Ill.
Adm.
Code
739.124(c)-,- to reclaim
metalworking oils or fluids.
The presumption
does apply to metalworking oils or fluids
if
such oils or fluids are recycled in any other
manner, or disposed.
ii)
The rebuttable presumption does not apply to
used oils contaminated with chlorofluorocarbons
(CFCs) removed from refrigeration units where
the CFC5 are destined for reclamation.
The
rebuttable
presumption
does
apply
to
used
oils
contaminated
with
CFCs
that
have
been
mixed
with
used
oil
from
sources
other
than
refrigeration
units.
b)
A solid waste whichthat
is not excluded from regulation under
subsection (a)(1)
above becomes a hazardous waste when any of the
following events occur:
1)
In the case of
a waste listed in 721.Subpart D of this Part,
when the waste first meets the listing description set forth
in 721.Subpart
D of this Part.
2)
In the case of
a mixture of solid waste and one or more
listed hazardous wastes, when a hazardous waste listed in
721.Subpart D of this Part is
first added to the solid
waste.
3)
In the case of any other waste
(including a waste mixture),
when the waste exhibits any of the characteristics
identified in 721.Subpart
C of this Par-~.
c)
Unless and until
it meets the criteria of subsection
(d) below÷~
hazardous waste will remain
a hazardous waste.
BOARD
NOTE:
This subsection corresponds with 40 CFP 261.3(c)(1).
The Board has codified 40 CFR 261.3(c~(2) at subsection
(e)
below.
~
i..~.ardouswaste will remain a ha~ardouo
wuu..C.
2)
Spcci~c inclusions
and oxoluci,,...~.
A)
Except as otherwise provided in subsection (c)(2)(B)
below,
any solid waste generated from the treatment,
storage or disposal
of
a hasardous waste,
including
any sludge,
spill
residue,
ash, emission control dust
or loachata
(but not including precipitation run off),
is
a hasardous waste.
(However, materials that are
reclaimed from solid wastes and that are used
beneficially arc not solid wastes and hence
arc net
hazardous wastes under this provision unless the
reclaimed material
is burned
for energy recovery or
used in a manner constituting disposal.)
—---i-
t_.___
40
tnougn
tncy
or disposal
arc
gcn
of
a ha
one or more of t-hc
,ste,
unleo
sties of
h
-~~-~i;i;~
i)
Waste pickle liquor sludge generated by U~me
atabili~ationof spent pickle liquor from the
iron and stool industry
(SIC Codes 331 and
3-32)
(Standard Industrial Codes,
as defined and
incorporat~dby reference
in
3~ Ill.
Adm.
Cnd~
ii)
Wastes
from
burning any
exempted from regulatio
721.106ts~(3~1E.
(ri.
Nonwastcwater
from
high tcmn~
processing
at
xwti,
iwo
identified, that
arc-
di
hasardous waste
~
~
residues meet the generic
idcn~~
~‘
-
rotar-
-
~1C~B
—-I
fu-rn
.a~
4L~4~~
to that dofiniti
-
:dbythc
facilit1
3clf imp’
~r’n
tsr~c~tcanalysis plan or a generator”
.Lemcntirlg
waste analysis plans at
u
ucimuo~itp
samples
of residues must bo
nonwa
.Pcrsonsclairningthia
exoluDton
in
an
mont
action will have the burden of
by clear and convincing evidence that
al meets all of the exclusion
cnts.
gencr~.exclusion
comp-o~itc ~J~inpiC
t
mn’
——
,
—----.,
—
_c___.___.
~
~
~
Antimony
0.10
Arsenic
0.50
Barium
7.6
Beryllium
Cadmium
0.010
0.050
Chromium
(total)
0.23
Load
0.15
Mercury
0.009
N1c~1rr’~1
1fl
iii)
residues,
ouch as slag,
reoulti
ccovcry
(HTMR)
C
4
ded
ti”’-
~Lr.L~U
Ifl
~I1~
L~D1C5
~fl
EfliS
DUflflC~1Ofl
for
ai.i.
of
constituents,
hazardous
and exhibit
no onaraatcrictioe
waste.
The
types
of units arce
-
reactors,
electric furnaces.
-—.---.--.~----.-...
kilno,
ph...na
arc
furn
,
-
#h—~
“
-
-
rurnaae,eieotria
Lurr1~LoQ
pc~mnLnprLonp
or
me
mitotrina
1-~vru’rt
of
jndustripj.
rurnacoc
(pp
-
dcfi~”~‘~—~-P~dm. ~
720.110)
furnaces,
smelting, melting and refining
-a———
———
proving
the materi.
4- 1~.
Maximum for any
singic
s—--~,
—,
Celenium
•
0.16
Silver
•
0.30
Thallium
•
0.020
Vanadium
1.26
2ino
70.
Generic exclusion Levels for F006 nonwaotewatcr
HTMR
residues
Antimony
0,10
l~rsonio
0.50
Barium
7.6
Beryllium
0.010
Cadmium
-0.050
Chromium (total)
Cyan~~-f4-”’)
(mg/kg)
Lead-
-,-
zicr~ury
Nickel
£-.
Selenium
0.16
Cilver
0.30
Thallium
0.020
Zinc
70
A one time notification and certification must
be placed in the
facility’s files and sent to
the Agency
(er,
for out-of State shipments,
to
the appropriate Regional Administrator of USEPA
or state agency authorized to implement
40
CFR
268 requirements)
for K061,
K062
-or
F-006
HTMR
residuco that meet the generic exclusion levels
for all constituents and do not exhibit any
eharactoriotics that are sent to
IlOflA
Subtitle D
followi
the rtonhaEardo
the waste chip:
number and tn
,~
~-
41
-0.33
0.15
—
units.
-The
notificati---
--.-~
4-~~-4-~
is placed- in the goner
generating tnc waste cnangeo or
3.t
tflC iiuw~
Cubtitle D unit receiving the waste changes.
However, the generator or treater need
only
notify the Agency on an annual basis if ouch
changes occur.
Cuch notification and
certification should be sent to the T~gencyby
the end of the calendar year,
but
no-
later than
December
31.
The notification mu~otinclude the
.,._.
informatione
The name and address of
waste manasement unit receiving
~Thc
U&EP2\
haz
:~itziDiiitygroup at tnc
M~ir,nr
Th~~
tr
+~ment~
r’t
point of
gene:
applicable to the waste at
the-
initial point of
generation.
The certification must be signed by
an authorized representative and must state as
followo-e-
“I certify under penalty of law that the generic
exclusion levels
for all constituento have been
met without impermiosible dilution and that no
characteristic of hazardous waste is exhibitcd.
I am aware that there are significant penalties
for submitting a false certification,
including
the possibility
of fine and imprisonment.”
42
t7I~?flt,
-
fl,t_._,
-
—
4
1
~__~1
—
UQAIW
~
..~
generic exOLuD
arsenic and zinc arc higher than the HTHR based
alternative treatment standards for K062 and
F006,
and HT~1based treatment standards for
K061,
specified in
35
Ill. Mm.
Code 728.141.
However,
the HTMrL residues must meet the
applicable treatment standards prior to generic
exclusion.
Therefore, to be eligible for a
generic exclusion, the treated residues must
meet the lower
of either the treatment standards
or the generic exclusion levels
for each
constituent.
d)
Any solid waste described in subsection
(c)
above
is not
a
hazardous waste if
it meets the following criteria:
1)
In the case
of any solid waste,
it does not exhibit any of
the characteristics of hazardous waste identified in
721.Subpart
C ef this Part.
(However, wastes whiohthat
exhibit
a characteristic
at the point of generation may
still be subject to the requirements of 35
Ill.
Adm.
Code
728, even if they no longer exhibit a characteristic at the
point of land disposal.)
2)
In the case of a waste whichthat
is
a listed waste under
721.Subpart D of this Part,
a waste that contains
a waste
listed under 721.Subpart
0
of this
Part1, or
a waste that
is
derived from a waste listed
in 72l.Subpart
D of this Part,
it also has been excluded from subsection
(c)
above under 35
Ill.
Adm.
Code 720.120 and 720.122.
e)
This subocotion oorrespondo with
40 CFR 261.3(e),
a oubooction
which has bean deleted from the federal regulations.
This
statement maintains structural
consistency with UCEPA
rulceSpecific inclusions and exclusions.
jj~
Except as otherwise provided in subsection (e)(2)
below, any
solid waste generated from the treatment,
storage, or
disposal of
a hazardous waste,
including any sludge.
spill
residue,
ash, emission control dust,
or leachate
(but not
including precipitation run-off),
is
a hazardous waste.
(However, materials that are reclaimed
from solid wastes and
that are used beneficially are not solid wastes and hence
are not hazardous wastes under this provision unless the
reclaimed material
is burned for energy recovery or used
in
a manner constituting disposal.)
21
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:
~J,
Waste pickle liquor sludge generated by lime
stabilization of spent pickle liguor from the iron and
steel
industry
(SIC Codes
331 and 332).
~j
Wastes from burning any of the materials exempted from
regulation by any of Section 721.106(a)(3UD) through
(a~(3) (F).
Qj
Nonwastewater residues,
such as slag, resulting from
high temperature metal recovery (HTMR) processing of
43
K061, K062,
or F006 waste in the units
identified in
this subsection that are disposed of in non—hazardous
waste_units, provided that these residues meet the
generic exclusion levels
identified in the tables
in
this subsection for
all constituents and the residues
exhibit no characteristics of hazardous waste.
The
types of units identified are rotary kilns,
flame
reactors,
electric furnaces, plasma arc furnaces,
slag
reactors,
rotary hearth furnace/electric furnace
combinations, or the following types of industrial
furnaces
(as defined
in
35 111. Mm.
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.
LLJ
Testing requirements must be incorporated in a
facility’s waste analysis ~1an or
a generator’s
self—implementing waste analysis plan;
at a
minimum, composite samples of residues must be
collected and analyzed quarterly and when the
process
or
operation
generating
the
waste
changes.
(ii)
Persons claiming this exclusion in an
enforcement
action will have the burden of
proving by clear
and convincing evidence that
the material meets all
of the exclusion
requirements.
The generic exclusion levels are:
Constituent
Maximum for any single
composite
sample
(ma/t)
Generic exclusion levels for 1(061 and 1(062
nonwastewater
HTMR
residues.
Antimony
.
.
Arsenic
Barium
Beryllium
.
.
Cadmium
Chromium
(total)
Lead
Mercury
Nickel
Selenium
.
.
Silver
Thallium
.
.
Vanadium
.
.
Zinc
0.10
0.50
7.6
0.010
0.050
0.33
0.15
0.009
1.0
0.16
0.30
0.020
1.26
70.
Generic exclusion
HTMR residues
levels for F006
Antimony
.
.
Arsenic
Barium
Beryllium
.
,
Cadmium
Chromium
(total)
•
0.10
0.50
7.6
0.01.
0.050
0.33
1.8
Cyanide
(total)
(mg/kg
)
44
Lead
.
.
.
0.15
Mercury
.
0.009
Nickel
.
1.0
Selenium
0.16
Silver
.
0.30
Thallium
0.020
Zinc
.
.
70.
(iii) A one—time notification and certification must
be
~1aced in the facility’s files and sent to
the Aaencv
(or, for out—of-State shipments, to
the appropriate Regional Administrator of U.S.
EPA or the state agency authorized to implement
40 CFR 268 requirements)
for 1(061,
1(062, or F006
HTMR
residues that meet the generic exclusion
levels for all constituents and do not exhibit
any characteristics and which are sent to RCRA
Subtitle D
(municipal solid waste landfill)
units.
The notification and certification that
is placed in the generator’s or treater’s
files
must be updated if the process or operation
generating the waste changes or
if the RCRA
Subtitle D unit receiving the waste changes.
However, the generator or treater need only
notify the Agency on an annual basis
if
such
changes occur.
Such notification and
certification should be sent to the Agency by
the end of the calendar year,
but no later than
December
31.
The
notification
must
include
the
following information:
the name and address of
the nonhazardous waste management unit receiving
the waste shipment; the U.S.
EPA hazardous waste
number and treatability group at the initial
point
of generation;
and the treatment standards
applicable to the waste at the initial
point
of
generation.
The certification must be signed by
an authorized representative and must state as
follows:
“I certify under ~enaltv of law that the
generic exclusion
levels for all
constituents have been met without
impermissible
dilution
and
that
no
characteristic of hazardous waste
is
exhibited.
I am aware that there are
significant penalties for submitting a
false certification,
including the
possibility
of fine
and imprisonment.”
BOARD
NOTE:
This
subsection
would
normally
correspond
with
40
CFR
261.3(e),
a
subsection
which
has
been
deleted
and
marked “reserved” by U.S.
EPA.
Rather,
this
subsection
corresponds
with
40
CFR
26l.3(c)(2). which the Board codified here
to
comport
with
codification
requirements
and enhance clarity.
f)
Notwithstanding subsections
(a) through (4~)above and provided
the
debris1, as defined in 35
Ill.
Adm. Code 728.102,
does not
exhibit
a characteristic identified at 721.Subpart C of this Part,
the following materials are not subject to regulation under
35
45
Ill. Adm.
Code 720,
721 to
726,
728,
or
730:
1)
Hazardous
debris
as
defined
in
35
Ill.
Adm.
Code
728.102
that
has
been
treated
using
one
of
the
required
extraction
or destruction technologies specified in Table A of
35 Ill,
Adm.
Code 728.446-Table_F; persons claiming this exclusion in
an enforcement action will have the burden of proving by
clear and convincing evidence that the material meets all of
the exclusion requirements;
or
2)
Debris as defined in 35
Ill.
Adm.
Code 728.102 that
the
Agency, considering the extent of contamination, has
determined is no longer contaminated with hazardous waste.
(Source:
Amended at
19
Ill.
Reg.
________,
effective
______________________
Section 721.104
Exclusions
a)
Materials that are not solid wastes.
The following materials are
not
solid wastes for the purpose of this Part:
1)
Sewage:
A)
Domestic sewage; and
B)
Any
mixture
of
domestic
sewage
and
other
waste
that
passes
through
a
sewer
system
to
publicly—owned
treatment works
for treatment.
Q.).
“Domestic sewage” means untreated sanitary wastes that
pass through a sewer system.
2)
Industrial wastewater discharges that are point source
discharges with NPDES permits issued by the Agency pursuant
to Section 12(f)
of the Environmental Protection Act and 35
Ill.
Adm.
Code 309.
BOARD NOTE:
This exclusion applies only to the actual point
source discharge.
It does not exclude industrial
wastewaters while they are being collected,
stored,
or
treated before discharge,
nor does
it exclude sludges that
are generated by industrial wastewater treatment.
3)
Irrigation return flows.
4)
Source,
special nuclear,
or by—product material as defined
by the Atomic Energy Act of 1954,
as amended
(42 U.S.C.
2011
et seq.)
5)
Materials
subjected
to
in-situ
mining
techniques
that
are
not
removed
from
the
ground
as
part
of
the
extraction
process.
6)
Pulping
liquors
(i.e.,
black
liquor)
that
are
reclaimed
in
a
pulping liquor recovery furnace and then reused in the
pulping
process,
unless
accumulated
speculatively1,
as
defined in Section 721.101(c).
7)
Spent
sulfuric
acid
used
to
produce
virgin
sulfuric
acid.,-
unless
it
is
accumulated
speculative1y~
as
defined
in
Section 721.101(c),
46
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;
3)
Reclamation does not involve
controlled
flame
combustion (such as occurs in boilers,
industrial
furnaces or incinerators);
C)
The
secondary
materials
are
never
accumulated
in
such
tanks
for
over
twelve
months
without
being
reclaimed;
and
D)
The reclaimed material
is not used to produce
a fuel-,
or used to produce
products
that
are
used
in
a
manner
constituting disposal.
9)
Wood
preserving
wastes.
A)
Spent
wood
preserving
solutions
that
have
been
used
and
which
are
reclaimed
and
reused
for
their
original
intended
purpose;
and
B)
Wastewaters from the wood preserving process that have
been
reclaimed
and
which
are
reused
to
treat
wood.
10)
Hazardous
waste
numbers
K060,
1(087,
1(141,
K142,
1(143,
1(144,
K145,
1(147,
and
1(148,
and
any
wastes
from
the
coke
by-
products processes that are hazardous only because they
exhibit the toxicity characteristic specified in Section
721.124,
when-, subsequent to generation-, these materials are
recycled to coke ovens, to the tar recovery process as a
feedstock
to
produce
coal
tar,
or
are
mixed
with
coal
tar
prior
to
the
tar’s
sale
or
refining.
This
exclusion
is
conditioned
on
there
being
no
land
disposal
of
the
wastee
from
the
point
thcyJ~ a~ej~generated
to
the
point
thcyj~
a~ej~recycled
to
coke
ovens,
to
e-~--tarrecovery,
to e*—the
tar refining processes,
or prior to when
it
is mixed with
coal.
11)
Nonwastewater splash condenser dross residue from the
treatment of hazardous waste
number 1(061 in high temperature
metals
recovery
units,
provided
it
is
shipped
in
drums
(if
shipped) and not land disposed before recovery.
~j_
Recovered
oil
from
petroleum
refining,
exploration,
and
production and from transportation incident thereto that
is
to be inserted into the petroleum refining process
(SIC Code
2911)
alona
with
normal
process
streams
prior
to
crude
distillation
or
catalytic
cracking.
This
exclusion
applies
to
recovered
oil
stored
or
transported
prior
to
insertion,
except
that
the
oil
must
not
be
stored
in
a
manner
involving
placement
on
the
land
and
the
oil
must
not
be
accumulated
speculatively
before
being
recycled.
Recovered
oil
is
oil
that
has
been reclaimed from secondary materials
(such as
wastewater)
generated from normal petroleum refining,
exploration
and
production,
and
transportation
practices.
Recovered
oil
includes
oil
that
is recovered from refinery
47
wastewater
collection
and
treatment
systems,
oil
recovered
from
gil and
gas
drilling
operations,
and
oil
recovered
from
wastes removed from crude oil storage tanks.
Recovered oil
does
not
include
(among
other
things)
oil—bearing
hazardous
wastes
listed
in
721.Subpart
D
(e.g.,
1(048
through
1(052.
F037,
and F038).
However,
oil recovered from such wastes
may be considered recovered oil.
Recovered oil also does
not
include
used
oil
as
defined
in
35
Ill.
Adm.
Code
739. 100.
b)
Solid wastes that are not hazardous wastes.
The following solid
wastes are not hazardous wastes:
1)
Household
waste,
including
household
waste
that
has
been
collected,
transported,
stored,
treated,
disposed,
recovered
(e.g., refuse—derived fuel), or reused.
“Household waste”
means any waste material (including garbage,
trash,
and
sanitary wastes
in septic tanks)
derived
from households
(including
single
and
multiple
residences,
hotels,
and
motels,
bunkhouses,
ranger
stations,
crew
quarters,
campgrounds,
picnic
grounds,
and
day—use
recreation
areas).
A
resource
recovery
facility
managing
municipal
solid
waste
shall
not
be
deemed
to
be
treating,
storing, disposing of,
or
otherwise
managing
hazardous
wastes
for
the
purposes
of
regulation
under
this
Part,
if
such
facility:
A)
Receives and burns only:
i)
Household
waste
(from
single
and
multiple
dwellings,
hotels,
motels,
and other residential
Bources)1
and
ii)
Solid
waste
from
commercial
or
industrial
sources
that
does
not
contain
hazardous
waste-~-1,
and
B)
Such facility does not accept hazardous waste and the
owner or operator of such facility has established
contractual requirements or other appropriate
notification
or
inspection
procedures
to
assure
that
hazardous wastes
are not received at or burned in such
facility.
BOARD
NOTE:
The U.S. Supreme Court determined,
in
City of Chicago v. Envronmental Defense Fund,
Inc.,
no-
92—1639 (May
2,
1994), that this exclusion and
RCRA
section
3001(i)
(42
U.S.C.
§
6921(i))
do
not
exclude the ash from facilities covered by this
subsection from regulation as
a hazardous waste.
At
59
Fed. Reg.
29372
(June
7,
1994),
U.S. EPA granted
facilities managing ash from such facilities that
is
determined a hazardous waste under 721.Subpart C until
December
7,
1994 to file
a Part A permit application
pursuant to 35
Ill. Adm.
Code 703.181.
2)
Solid
wastes
generated
by
any
of
the
following
that
are
returned
to
the
soil
as
fertilizers:
A)
The growing and harvesting of agricultural crops~.. or
B)
The
raising
of
animals,
including
animal
manures.
48
3)
Mining overburden returned to the mine site.
4)
Fly
ash
waste,
bottom
ash
waste,
slag
waste,
and flue gas
emission control waste generated primarily from the
combustion of coal-, or other fossil fuels, except as
provided in 35
Ill.
Adm.
Code 726.212 for facilities that
burn or process hazardous waste.
5)
Drilling fluids, produced waters,
and other wastes
associated with the exploration,
development,
or production
of crude oil, natural gas, or geothermal energy.
6)
Chromium wastes:
A)
Wastes that fail the test for the toxicity
characteristic
(Sections 721.124 and 721.Appendix B)
because chromium is present or which are are listed in
721.Subpart D of this Part due to the presence of
chromium, that
do not fail the test for the toxicity
characteristic
for
any
other
constituent
or
which
are
not
listed due to the presence of any other
constituent,
and that do not fail the test for any
other characteristic,
if
it
is shown by
a waste
generator or by waste generators that:
i)
The chromium
in the waste
is exclusively
(or
nearly exclusively)
trivalent chromium;
and
ii)
The waste is generated from an industrial
process that uses trivalent chromium exclusively
(or nearly exclusively) and the process does not
generate hexavalent chromium;
and
iii)
The waste
is typically and frequently managed in
non—oxidizing environments.
B)
Specific wastes that meet the standard
in subsectione
(b)(6)(A)(i,
(b)(6)(A)(ii),
and
(b)(6)(A)(iii) above
(so long as they do not fail the test for the toxicity
characteristic for any other constituent and do not
exhibit any other characteristic)
are:
i)
Chrome
(blue) trimmings generated by the
following subcategories of the leather tanning
and finishing industry~j hair pulp/chrome
tan/retan/wet finish~1,hair save/chrome
tan/retan/wet
finishj-1, retan/wet
finishi-,
no
beanihousei-1, through-the-blue-~-1,and shearling-.-j
ii)
Chrome
(blue)
shavings generated by the
following subcategories of the leather tanning
and finishing industry~j hair pulp/chrome
tan/retan/wet
finishi-1, hair save/chrome
tan/retan/wet
finishi-1, retan/wet
finish-~-1,no
beamhousej-1, through-the-blue-~-1,and shearling-.-~
iii)
Buffing dust generated by the
following
subcategories of the leather tanning and
finishing industry:
hair pulp/chrome
tan/retan/wet
finisht1, hair save/chrome
tan/retan/wet
finish-~-1,retan/wet
finishi-1, no
beamhousej-1, through-the-b lue-~-~
49
iv)
Sewer screenings generated by the following
subcategories of the leather tanning and
finishing industry:
hair pulp/chrome
tan/retan/wet finish~1,hair save/chrome
tan/retan/wet
finish-~-1,retan/wet finish~1,no
beamhouse-r1, through-the-blue~1,and
shearling-~-j,
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-~-1,retan/wet finish*1, no
beamhouse~1,through—the-blue-r1, and
shearling-r.j.
vi)
Wastewater treatment sludges generated by the
following subcategories of the leather tanning
and finishing industry:
hair pulp/chrome
tan/retan/wet finish~1,hair save/chrome
tan/retan/wet finish~1,and through—the-blue-.-~
vii)
Waste scrap leather from the leather tanning
industry,
the shoe manufacturing industry,
and
other leather product manufacturing
industries-.-j.
and
viii) Wastewater treatment sludges from the production
of titanium dioxide pigment using chromium—
bearing ores by the chloride process.
7)
SoLid waste from the extraction,
beneficiation, and
processing of ores and minerals
(including coal, phosphate
rock,
and overburden from the mining of uranium ore),
except
as provided by 35 Ill. Adm. Code 726.212 for facilities that
burn or process hazardous waste.
For purposes of this
subsection, beneficiation of ores and minerals is restricted
to the following activities:
crushing,
grinding,
washing,
dissolution, crystallization,
filtration,
sorting,
sizing,
drying,
sintering, pelletizing, briquetting, calcining to
remove water or carbon dioxide,
roasting,
autoclaving or
chlorination in preparation for leaching
(except where the
roasting or autoclaving or chlorination and leaching
sequence produces a final or intermediate product that does
not undergo further beneficiation or processing), gravity
concentration, magnetic separation,
electrostatic
separation, floatation,
ion exchange,
solvent extraction,
electrowinning, precipitation,
amalgamation,
and heap,
dump,
vat tank,
and in situ leaching.
For the purposes of this
subsection, solid waste from the processing of ores and
minerals includes only the following wastes:
A)
Slag from primary copper processing-p-1,
B)
Slag from primary lead processingy-1,
C)
Red and brown muds from bauxite refining-,-1,
D)
Phosphogypsum from phosphoric acid production-i-1,
B)
Slag from elemental phosphorus
production-~-1,
F)
Gasifier ash from coal
gasification-i-1,
50
G)
Process wastewater from coal
gasification-t-1,
H)
Calcium sulfate wastewater treatment plant sludge from
primary copper processing-?-1,
I)
Slag tailings from primary copper processing-?-1,
J)
Fluorogypsum from hydrofluoric acid production-~-1,
K)
Process wastewater from hydrofluoric acid production-i-1,
L)
Air pollution control dust or sludge from iron blast
furnaces-i-1,
M)
Iron blast furnace
slag-i-1,
N)
Treated residue from roasting and leaching of chrome
ore-~-1,
0)
Process wastewater from primary magnesium processing
by the anhydrous
process-i-1,
P)
Process wastewater
from phosphoric acid production-~-1,
Q)
Basic oxygen furnace and open hearth furnace air
pollution control dust or sludge from carbon steel
production-i-1,
R)
Basic oxygen furnace and open hearth furnace slag from
carbon steel production-i-1,
5)
Chloride processing waste solids from titanium
tetrachloride production--1, and-,-
T)
Slag from primary zinc smelting.
8)
Cement kiln dust waste,
except
as provided by 35
Ill.
Adm.
Code 726.212 for facilities that burn or process hazardous
waste.
9)
Solid waste that consists of discarded arsenical—treated
wood or wood products whichthat fails the test for the
toxicity characteristic for hazardous waste codes D004
through DO17 and thatwhich
is not
a hazardous waste for any
other reason if the waste is generated by persons w~ethat
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 D0l8 through D043 only)
and which are
subject to corrective action regulations under
35 Ill.
Adm.
Code 731.
11)
Injected
groundwater
that
is
hazardous
only
because
it
exhibits the toxicity characteristic
(U.S. EPA hazardous
waste coacs uui.~tnrougn
Uu~
Ofli~)
in ~cction
i~i.i~
tna~
is
r~einjccted
throi~gh an
underground
injection
well
pursuant
to
free
phase
hydrocarbon
recovery
operations
undertaken
at
petroleum
refineries,
-petroleum
marketing
terminals
petroleum
bulk
plants,
petroleum
pipe-lines,
and
petroleum
spill
sites
until
January
25,
1093.
This
extension
applies
51
to recovery operations
in existence, or for which contracts
have been issued,
on or bofore Harch 25,
1991.
For
groundwater returned through infiltration galleries from
ouch at petroleum ~efinerico, marketing terminals,
and bulk
plants,
until October
2,
1991.
flew operations involving
injection
wells
(beginning
after
tlarch
25,
1991)
will
qualif--
fr~,-
~)1i-~
compliance
date
extension
‘until January
25,
1993)
~ly
ifiThi~subsection corresponds with 40 CFR
261.4(b)(11),
which
expired
by
its
own
terms
on
January
25,
1993.
This statement maintains structural parity with U.S.
EPA regulations.
A-)
Operations are performed pursuant to
a “free product
removal
repoi~t”pursuant to
35
Ill.
Adm.
Code 731.164k
M~4
B)
A
copy of the “free product removal report”
has been
submitted toz
(08—333
U.C. EPA
-
401
H
Ctrcct,
CW
Washington,
D.C.
~u’~u
12)
Used
chlorofluorocarbon
refrigerants
from
totally
enclosed
heat
transfer
equipment,
including
mobile
air
conditioning
systems,
mobile
refrigeration,
and
commercial
and
industrial
air conditioning and refrigeration systems,
that
uses
chlorofluorocarbons
as
the
heat
transfer
fluid
in
a
refrigeration cycle, provided the refrigerant is reclaimed
for further use.
13)
Non—terne
plated
used
oil
filters
that
are
not
mixed
with
wastes
listed
in
721.Subpart
D
of
this
Part,
if
these
oil
filters
have
been
gravity
hot—drained
using
one
of
the
following methods:
A)
Puncturing
the
filter
anti—drain
back
valve
or
the
filter
dome
end
and
hot—draining;
B)
Hot—draining and crushing;
C)
Dismantling and hot—draining;
or-7-
D)
Any
other
equivalent
hot-draining
method
that
will
remove
used
oil.
14)
Used
oil
re—refining
distillation
bottoms
that
are
used
as
feedstock to manufacture asphalt products.
c)
Hazardous
wastes
that
are
exempted
from
certain
regulations.
A
hazardous
waste
that
is
generated
in
a
product
or
raw
material
storage
tank,
a
product
or
raw
material
transport
vehicle
or
vessel,
a
product
or
raw
material
pipeline,
or
in
a
manufacturing
process
unit,
or
an
associated
non—waste—treatment
manufacturing
unit,
is
not
subject
to
regulation
under
35
111.
Adm.
Code 702,
703,
705,
and
722
through
7251,
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.
52
d)
Samples
1)
Except
as provided in subsection
(d)(2)
below,
a sample of
solid waste or a sample of water,
soil,
or air that is
collected
for the sole purpose of testing to determine its
characteristics or composition is
not subject to any
requirements of this Part or
35 Ill.
Adm.
Code 702,
703,
705,
and 722 through 728.
The sample qualifies when:
A)
The sample
is being transported to
a laboratory
for
the purpose of testing;—e~
3)
The sample is being transported back to the sample
collector
after
testing;—e~
C)
The sample is being stored by the sample collector
before transport to a laboratory for testing;—e~
D)
The sample is being stored
in a laboratory before
testing;—e*
E)
The sample is being stored
in
a laboratory for testing
but before it
is returned to the sample collector;
or
F)
The sample
is being stored temporarily in the
laboratory after testing for
a specific purpose
(for
example, until conclusion of
a court case or
enforcement action where further testing of the sample
may be necessary).
2)
In order to qualify for the exemption in subsections
(d)(1)(A) a~or (d)(1)(B)
above,
a sample collector shipping
samples to a laboratory and a laboratory returning samples
to a sample collector shall:
A)
Comply with U.S. Department
of Transportation
(DOT),
U.S. Postal Service
(USPS), or any other applicable
shipping requirements; or
B)
Comply with the following requirements
if the sample
collector determines that DOT, USPS, or other shipping
requirements do not apply to the shipment of the
sample:
i)
Assure that the following information
accompanies the sample:
The sample collector’s
name,
mailing address,
and telephone number; the
laboratory’s
name,
mailing
address,
and
telephone number;
the quantity of the sample;
the date of the shipment; and
a description
of
the
sample.
ii)
Package the sample so that it
does not leak,
spill,
or vaporize from its packaging.
3)
This exemption does not apply if the laboratory determines
that the waste
is hazardous but the laboratory
is no longer
meeting any of the conditions stated
in subsection (d)(l)
above.
e)
Treatability study samples.
53
1)
Except as
is provided in subsection
(e)(2)
below, ~pereone
w~ethatgenerate~or collect~samples
for the purpose of
conducting
treatability
studies,
as
defined
in
35
Ill.
Adm.
Code
720.110,
are
not
subject
to
any
requirement
of
35
Ill.
Adm.
Code 721
through
723
or
to
the
notification
requirements of Section 3010 of the Resource Conservation
and
Recovery
Act.
Nor
are
such samples included in the
quantity
determinations
of
Section
721.105
and
35
Ill.
Adm.
Code 722.134(d)
when:
A)
The sample is being collected and prepared for
transportation
by
the
generator
or
sample
collector;
B)
The
sample
is
being
accumulated
or
stored
by
the
generator
or
sample
collector
prior
to
transportation
to a laboratory or testing facility; or
C)
The sample is being transported to the laboratory or
testing facility for the purpose of conducting
a
treatability study.
2)
The
exemption
in subsection (e)(1) above
is
applicable to
samples of hazardous waste being collected and shipped for
the purpose of conducting treatability studies provided
that:
A)
The
generator
or
sample
collector
uses
(in
“treatability
studies”)
no
more than 10,000 kg of
media contaminated with non—acute hazardous waste,
1000 kg of non—acute hazardous waste other than
contaminated media,
1 kg of acute hazardous waste, or
2500 kg of media contaminated with acute hazardous
waste for each process being evaluated for each
generated wastestream; and
B)
The mass of each shipment does not exceed 10,000 kg;
the 10,000 kg quantity may be all media contaminated
with non—acute hazardous waste,
or may
include 2500 kg
of media contaminated with acute hazardous waste,
1000
kg of hazardous waste,
and
1 kg of acute hazardous
waste; 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
(e)(2)(C)(ii),
below,
are met.
i)
The transportation of each sample shipment
complies with U.S. Department of Transportation
(DOT), U.S.
Postal Service
(USPS),
or any other
applicable shipping requirements;
or
ii)
If the DOT,
USPS, or other shipping requirements
do
not
apply
to
the
shipment
of
the
sample,
the
following
information
must
accompany
the
sample:
The
name,
mailing
address,
and
telephone
number
of the originator of the sample; the name,
address,
and
telephone
number
of
the
facility
that will perform the treatability study; the
quantity
of
the
sample;
the
date
of
the
shipment;
and,
a
description
of
the
sample,
54
including its
U.S. EPA hazardous waste
number-rj.
D)
The sample
is shipped to a laboratory or testing
facility that
is exempt under subsection
(f)
below,
or
has an appropriate
RCRA permit or interim status~-~
E)
The generator or sample collector maintains the
following records for a period ending
3-three years
after completion of the treatability study:
i)
Copies of the shipping documents;
ii)
A copy of the contract with the facility
conducting the treatability study;
iii)
Documentation showing:
The amount of waste
shipped under this exemption; the name,
address,
and U.S. EPA identification number of the
laboratory or testing facility that received the
waste;
the date the shipment was made;
and,
whether or not unused samples and residues were
returned to the generator-i-;
and
F)
The generator reports the information required
in
subsection
(e)(2)(E)(iii)
above in its report under
35
Ill.
Adrn.
Code 722.141.
3)
The Agency may grant requests on
a case—by—case basis for up
to an additional two years for treatability studies
involving bioremediation.
The Agency may grant requests,
on
a case—by—case basis,
for quantity limits
in excess of those
specified
in subsection
(e)(2)(A)
and
(e)(2)(B)
above and
(f)(4)
below,
for up to an additional 5000 kg of media
contaminated with non—acute hazardous waste,
500 kg of non—
acute hazardous waste, 2500 kg of media contaminated with
acute hazardous waste,
and
1 kg of acute hazardous waste:
A)
In response to requests for authorization to ship,
store,
and conduct
further treatability studies on
additional quantities
in advance of commencing
treatability studies.
Factors to be considered
in
reviewing such requests include the nature of the
technology, the type of
process
(e.g., batch versus
continuous), the size of the unit undergoing testing
(particularly in relation to scale—up considerations),
the time or quantity of material required to reach
steady-state operating conditions,
or test design
considerations,
such
as mass balance calculations.
B)
In response to requests for authorization to ship,
store,
and conduct treatability studies on additional
quantities after initiation or completion of initial
treatability studies when:
There has been an
equipment or mechanical failure during the conduct of
the treatability
study-i-1, there is need to verify the
results of
a previously-conducted treatability
study-p-1,
there is
a need to study and analyze alternative
techniques within
a previously—evaluated treatment
process-i-1, or there
is
a need to do further evaluation
of an ongoing treatability study to determine final
specifications for treatment.
55
C)
The additional quantities allowed and timeframes
allowed in subsections
(e)(3)(A) and
(e)(3)(B) above
are subject to all the provisions
in subsections
(e)(l) and (e)(2)(B) through (e)(2)(F)
above.
The
generator or sample collector shall apply to the
Agency and provide
in writing the following
information:
i)
The reason why the generator or sample collector
requires additional time or quantity of sample
for the treatability study evaluation and the
additional time or quantity needed;
ii)
Documentation accounting for all samples of
hazardous waste from the wastestream that have
been sent for or undergone treatability studies,
including the date each previous sample from the
waste stream was shipped, the quantity
of each
previous shipment,
the laboratory or testing
facility to which
it was shipped, what
treatability study processes were conducted on
each sample shipped,
and the available results
of each treatability study;
iii)
A description of the technical modifications or
change in specifications that will be evaluated
and the expected results;
iv)
If such further study
is being required due to
equipment or mechanical failure, the applicant
shall include information regarding the reason
for the failure or breakdown and also include
what procedures or equipment improvements have
been made to protect against further breakdowns;
and
v)
Such other information as the Agency determines
is necessary.
4)
Final Agency determinations pursuant to this subsection may
be appealed to the Board.
f)
Samples undergoing treatability studies at laboratories or testing
facilities.
Samples undergoing treatability studies and the
laboratory or testing facility conducting such treatability
studies (to the extent such facilities are not otherwise subject
to
RCRA
requirements) are not subject to any requirement of this
Part,
or of
35
Ill.
Adm.
Code 702,
703,
705,
722 through
726,
and
728-,- or to the notification requirements of Section 3010 of the
Resource Conservation and Recovery Act, provided that the
requirements of subsections
(f)(l) through
(f)(11)-, below-, are
met.
A mobile treatment unit may qualify as
a testing facility
subject to subsections
(f)(l)
through
(f)(ll)-, below.
Where
a
group of mobile treatment units are located at the same site,
the
limitations specified
in subsections
(f)(1) through
(f)(11)-,--
below-, apply to the entire group of mobile treatment units
collectively as
if the group were one mobile treatment unit.
1)
No less than 45 days before conducting treatability studies,
the facility notifies the Agency in writing that
it intends
to conduct treatability studies under this subsection.
56
2)
The laboratory or testing facility conducting the
treatability study has
a U.S. EPA identification number.
3)
No more than a total of 10,000 kg of
“as received” media
contaminated with non—acute hazardous waste,
2500 kg of
media contaminated with acute hazardous waste,
or 250 kg of
other “as received” hazardous waste is subject to initiation
of treatment in all treatability studies
in any single day.
“As received” waste refers to the waste as received in the
shipment from the generator or sample collector.
4)
The quantity of
“as received”
hazardous waste stored at the
facility for the purpose of evaluation in treatability
studies does not exceed 10,000 kg, the total of which can
include 10,000 kg of media contaminated with non—acute
hazardous waste,
2500 kg of media contaminated with acute
hazardous waste,
1000 kg of non—acute hazardous wastes other
than contaminated media,
and
1 kg of acute hazardous waste.
This quantity limitation does not includetreatment materials
(including nonhazardous solid waste)
added to “as received”
hazardous waste.
5)
No more than 90 days have elapsed since
the
treatability
study for the sample was completed,
or no more than one year
(two years for treatability studies
involving
bioremediation)
has elapsed since the generator or sample
collector shipped the sample to the laboratory or testing
facility, whichever date first
occurs.
Up to 500 kg of
treated material from a particular waste stream from
treatability studies may be archived for future evaluation
up to five years from the date of
initial receipt.
Quantities of materials archived are counted against the
total storage limit for the facility.
6)
The treatability study does not
involve the placement of
hazardous waste on the land or open burning of hazardous
waste.
7)
The facility maintains records for ~three years following
completion of each study that show compliance with the
treatment rate limits and the storage time and quantity
limits.
The following specific information must be included
for each treatability study conducted:
A)
The name,
address,
and U.S. EPA identification number
of the generator or sample collector of each waste
sample;
B)
The date the shipment was received;
C)
The quantity of waste accepted;
D)
The quantity of “as received” waste in storage each
day;
E)
The date the treatment study was initiated and the
amount of
“as received” waste introduced to treatment
each day;
F)
The date the treatability study was concluded;
G)
The date any unused sample or residues generated from
57
the treatability study were returned to the generator
or sample collector or,
if sent to a designated
facility,
the name of the facility and the U.S. EPA
identification number.
8)
The facility keeps,
on—site,
a copy of the treatability
study contract and all shipping papers associated with the
transport of treatability study samples to and from the
facility for a period ending s-three years from the
completion date of each treatability study.
9)
The facility prepares and submits a report to the Agency by
March
15 of each year that estimates the number of studies
and the amount of waste expected to be used in treatability
studies during the current year, and
includes the following
information
for the previous calendar year:
A)
The name,
address,
and U.S. EPA identification number
of the facility conducting the treatability studies;
B)
The types
(by process)
of treatability studies
conducted;
C)
The names and addresses of persons
for whom studies
have been conducted (including their U.S. EPA
identification numbers);
D)
The total quantity of waste in storage each day;
B)
The quantity and types of waste subjected to
treatability studies;
F)
When each treatability study was conducted;
and
G)
The final disposition of residues and unused sample
from each treatability study.
10)
The facility determines whether any unused sample or
residues generated by the treatability
study are hazardous
waste under Section 721.103
and,
if
so,
are subject to 35
Ill.
Adm.
Code
702,
703,
and 721 through
728, unless the
residues and unused samples are returned to the sample
originator under the subsection
(e) exemption above.
11)
The facility notifies the Agency by letter when the facility
is no
longer planning to conduct any treatability studies at
the site.
(Source:
Amended
at
19
Ill. Reg.
________,
effective
_____________________
Section 721.106
Requirements for Recyclable Materials
a)
Recyclable materials:
1)
Hazardous wastes that are recycled are subject to the
requirements
for generators,
transporters1, and storage
facilities of subsections
(b)
and
(c)-,- below,
except for the
materials listed
in subsections
(a)(2) and j~j(3)-,-below.
Hazardous wastes that are recycled will be known as
“recyclable materials”.
2)
The following recyclable materials are not
subject to the
58
requirements of this Section but are regulated under
35 Ill.
Adxn.
Code 726.Subparts C through H and all applicable
provisions
in 35
Ill.
Adm. Code 702,
7031, and 705.
A)
Recyclable materials used in
a manner constituting
disposal
(35
Ill.
Adm.
Code 726.Subpart C);
B)
Hazardous wastes burned for energy recovery in boilers
and industrial furnaces that are not regulated under
35 Ill.
Adxn.
Code 724.Subpart 0 or 725.Subpart 0
(35
Ill.
Adm.
Code 726.Subpart H-~-)~
C)
Recyclable materials from which precious metals are
reclaimed
(35
Ill.
Adm. Code 726.Subpart F);
D)
Spent lead-acid batteries that are being reclaimed
(35
Ill.
Adm.
Code 726.Subpart G).
3)
The following recyclable materials are not
subject to
regulation under
35
Ill. Adm. Code
722 through 726,
728, or
702,
7031,
or 705 and are not subject to the notification
requirements of Section 3010 of the Resource Conservation
and Recovery Act:
A)
Industrial ethyl alcohol that
is
reclaimed except
that,
unless provided otherwise in an international
agreement as specified in
35
Ill.
Adm.
Code 722.158:
i)
A person initiating a shipment for reclamation
in a foreign country-, and any intermediary
arranging for the shipment-, shall comply with
the requirements applicable to
a primary
exporter in 35
Ill.
Adm. Code 722.l53~~~~
722.156(a)(1) through
(a)(4),
(a)(6)1, and
(b)-7-~
and 722.l57-,~shall export such materials only
upon consent of the receiving country and
in
conformance with the U~S~EPAAcknowledgement of
Consent1, as defined in 35
Ill. Mm. Code
722.Subpart
E-,-l and shall provide a copy of the
U1,S~EPAAcknowledgement of Consent to the
shipment to the transporter transporting the
shipment for export;
ii)
Transporters transporting
a shipment for export
shall not accept a shipment
if the transporter
knows that the shipment does not conform to the
U1,S~EPAAcknowledgement of Consent,
shall
ensure that
a copy of the U1,S.~EPA
Acknowledgement of Consent
accompanies the
shipment1, and shall ensure that
it
is delivered
to the facility designated by the person
initiating the shipment.
B)
Used batteries
(or used battery cells)
returned to
a
battery manufacturer
for regeneration;
C)
Scrap metal;
D)
Fuels produced from the refining of oil—bearing
hazardous wastes along with normal process streams at
a petroleum refining facility
if such wastes result
59
from normal petroleum refining,
production1, and
transportation practices
(this exemption does not
apply to fuels produced from oil recovered from oil—
bearing hazardous waste where such recovered oil
is
already excluded under Section 721.l04(a)(12));
E)
Oil reclaimed from hazardous w.t~i.eresulting
from
normal netroicum reI~i.n1ng~
nroauatlon.
and
transportation practices,
wnicn
oti.
is
to
be refined
along
with
normal
~roccso streams at a —troleum
refining faoility~
~)
Petroleum refining wastes.
i)
Hazardous waste fuel produced from oil—bearing
hazardous wastes
from petroleum refining,
production1, or transportation practices-,
or
produced from oil reclaimed from such hazardous
wastes, where such hazardous wastes are
reintroduced into a process that does not use
distillation or does not produce products from
crude
oil1, so
long as the resulting fuel meets
the used oil specification under
35
Ill.
Adm.
Code 726.140(e) and so long
as no other
hazardous wastes are used to produce the
hazardous waste fuel;
ii)
Hazardous waste fuel produced from oil-bearing
hazardous waste from petroleum refining
production1, and transportation practices,
where
such hazardous wastes are reintroduced into a
refining process after a point at which
contaminants are removed,
so long as the fuel
meets the used oil
fuel specification under 35
Ill.
Adrn.
Code 726.140(e);
and
iii)
Oil reclaimed from oil—bearing hazardous wastes
from petroleum refining,
production1, and
transportation practices, which reclaimed oil
is
burned as a fuel without reintroduction to a
refining process,
so long as the reclaimed oil
meets the used oil fuel specification under
35
Ill.
Adm.
Code 726.140(e);
and
G~)
Petroleum coke produced from petroleum refinery
hazardous wastes containing oil at the
same
facility
at which ouchby the same person that generated the
wastes were generated,- unless the resulting coke
product exceeds one or more of the characteristics of
hazardous waste
in 72l.Subpart ~D of this Part.
4)
Used oil that
is recycled and
is also a hazardous waste
solely because it exhibits
a hazardous characteristic
is not
subject to the requirements of 35 Ill. Mm.
Code 720 through
728, but itis regulated under 35 Ill. Mm.
Code 739.
Used
oil that
is recycled includes any used oil whichthat
is
reused for any purpose-, following its original use,
for any
purpose
(including the purpose for which the oil was
originally usedj.
Such term includes,
but
is
riot limited
to,
oil whiohthat
is re—refined,
reclaimed, burned for
energy recovery, or reprocessed.
60
b)
Generators and transporters of recyclable materials are subject to
the applicable requirements of 35 Ill. Adm. Code 722 and
723 and
the notification requirements under Section 3010 of the Resource
Conservation and Recovery Act,
except
as provided in subsection
(a)-, above.
c)
Storage and recycling:
1)
Owners or operators of facilities that store recyclable
materials before they are recycled are regulated under all
applicable provisions of 35
Ill.
Adm. Code 702,
703, and
705; 724.Subparts A through
L,
AA1, and BB~and 725.Subparte
A through L,
AA1, and
BB-,--~ 726~rj728-,~702, 703 and 705
and
the notification requirement under Section 3010 of the
Resource Conservation and Recovery Act, except as provided
in subsection
(a)-, above.
(The recycling process
itself
is
exempt from regulation,
except as provided in subsection
(d)-, below.)
2)
Owners or operators of
facilities that recycle recyclable
materials without storing them before they are recycled are
subject to the following requirements, except
as provided in
subsection
(a)-,
above-1-:
A)
Notification requirements under Section 3010 of
the
Resource Conservation and Recovery Act-~1,
8)
35
Ill.
Adin. Code 725.171 and 725.172
(dealing with
the use of the manifest and manifest discrepancies)1,
and
C)
subsection
(d)-, below.
d)
Owners or operators of facilities required to have a RCRA permit
pursuant to 35
Ill.
Adm. Code 703 with hazardous waste management
units whiohthat recycle hazardous wastes are subject to
35 Ill.
Adm. Code 724.Subpart~AA and BB and 725.Subpart~AA and BB.
(Source:
Amended at
19 Ill. Reg.
_______,
effective
_____________________
Section 721.Appendix
I
Wastes Excluded under Ccction 720.120 and 720.l22bv
Administrative Action
Table
A
Wastes Excluded by U.S.
EPA under 40 CFR 260.20 and 260.22 flrom
Non—Specific
Sources
Facility Address
Waste Description
Enviritc
Corp-i-
~
Illinois
Dewatcrcd wactewater sludges
(EPA
Hazardous Waste
NO.
F006) acno~
:~4Et~::;:
acing
ttinu
DucraLjofluJ
upenc
uy~nJ~ut~
-
....zareoua
~rnnto
Mo
rLJu,~
generates trom electroplating opcrattono~
plating~bath residues from the bottom
c-f plating
baths
(EPA Hazardous Waste No.
F008) generated
from electroplating operations where oyanideo
are used in the process;
spent stripping and
cleaning bath solutions
(EPA Hazardous ~Jaote
No~
1-0-09)
gone-rate-cl from electroplating opcratio~s
where cyanidcs arc used
in the process;
spent
cyanide solutions from salt bath pot cleaning
(EPA Hazardous Wacstc
No.
FOil)
generated
from
Ol~oLi~u,
SOLUtiOnS
-J-l~
from
------~-
61
__~~_1
L..L
.—,
~
--h,--
(EPA Ha~
w~istewatertreatment
sludges (EP1~H
Waste lb.
F0l9)
generated from the
on
ooiting
of aluminum after Novc
1986.
To
i,r,4~
ti~
lrn
nouro that hazarciouo constituents arc
in the waste at levelo of regulatory
a_ ~_
~~~r—~-6
±~
~
~-
-
—
—~
z
tcoti..-~
~..
“~tecting,
concern,
oontingcncv
ogram
for
the
potitioned
wastes.
-~n~
~ro~rain
must meet the
following coRuicionu
zor tne exclusions to be
valid-sr
1)
Each batch of treatment recidue must be
rcprcoentativ-ely sampled and tested using
the EP Toxicity test
for ares
cadmium,
chrom~-’-’~
conccn~rationoror
c
arsenic,
and silver
bariu..~
~
exceect
selenium c~ccoe-d 0.063
0.0126 ppm;
or nickel
6.3
..t.,
ppm; mer
levels
e
ppm,
tnc waste
mimi-
n~
r~—i-r~
—_—~
I
od 2.205
rod
~...
~spoace
ac a nazaraouo waste
-
35
Ill. Mm.
Code
722 to 725 and the
~-~-...~tting
standards of 35 Ill. Mm.
Code
702. 7O~. rind 705.
2)
Each batch of treatment residue must be
tested- for reactive and leachable cyanide.
If the reactive cyanide levels excn~d250
ppm
or
leachable cyanide levels
(using the
EP Toxicity test without acetic acid
adjustment) exceed 1.26
ppm-,
the waste
must be retreated or managed and disposed
as a hazardous waste under
35
Ill.
Adm.
Code 722 to
725 and the
permitting
standards of
35
Ill. Mm.
Code 702,
703,-
and
705.
3)
Each batch
of waste must be tcotcd for the
total content of opccific organic
anthrasene exceeds 76.8 ppm,
1,2—diphenyl
hydrazino oxceodo 0.001
ppm,
mcthylonc
chloride exceeds 8.18 ppm, methyl ethyl
kctonc exceeds 326 ppm,
n nitrosodiphenyl-
amine exceods 11.9 ppm, phonol
exceeds
1,566 ppm,
tetrachlorocthyleno- exceeds
0.188 ppm,
or trichioroethylene exceeds
0.592 ppm,
the waste must be managed and
disposed as a hazardous waste under
35
Ill.
Ti.dm.
Code 722 to 725 and the
permitting standards of 35 Ill.
Adrn.
Code
702,
703,
and 705.
4)
A grab sample must be colloctc
batch to form one monthly com~
whichthat must be tested using gas
1 from each
site sample
.z-~--.-,
-3
—
-
62
cnromatograpny, mass spcotromctry ansi.ysis
for the compounds listed
in No.3 above as
well as the remaining organico on the
Priority Pollutant List
(incorporated by
reference,
ccc 40
CFII 423 App. A (1983)
(as adopted
at 47 Fed.
Reg.
52,309
(Nov.
19. 1982~-.not including later
amendxnento.
flit...
._3..L.
C
3t
4.
±
c±
I
—
._4~.
4_t~_
C_~_2
I
I
J___
S___
I
1
4 must be kept
~LIU
~
purposes
and must be compiled, oummariwd,
and submitted to the Administrator of
UCEPA by certified mail semi-annually.
The USEPA will review this information and
if needed will propose to modify or
withdraw the exclusion.
Chould UCEPA
propose to modify
or withdraw the
exclusion, Envirito shall promptly provide
notice
thereof
to
the
Board.
The
decision
to conditionally exclude
the treatment
residue generated from the waotcwater
treatment systems at Envirite’s Harvey,
Illinois facility applies only to the
wastewatcr and solids treatment systems as
they presently exist as described in the
dolioting petition submitted to the USEPA~
The exclusion does not apply to the pro-
posed process additions described
in the
petition submitted to UCEPA as recovery
including crystallization, electrolytic
metals recovery, evaporative recovery,
and
ion exchange.
(Source:
Amended at
19
Ill. Reg.
effective
Section 721.Appendix
I
Wastes Excluded under
Administrative Action
Table
B
Wastes Excluded by U.S. EPA under
40 CFR 260.20 and 260.22
f1-rom
Specific Sources
Facility Address
Waste Description
Amoco Oil Company
Wood River,
Illinois
150 million gallons of DAF float
from petroleum
refining contained in four surge ponds after
treatment with the Chemfix stabilization
process.
This waste contains U.S. EPA hazardous
waste number K048.
This exclusion applies to
the 150 million gallons of waste after chemical
stabilization as long as the mixing ratios of
the reagent with the waste are monitored
continuously and do not vary outside of the
limits presented in the demonstration
samples-f
~
one grab sample
is taken each hour from each
treatment unit,
composited,
and EP toxicity
tests performed on each sample.
If the levels
of lead or total chromium exceed 0.5 ppm in the
EP extract,
then the waste that was processed
during the compositing period
is considered
hazardous; the treatment residue shall
be pumped
into bermed cells to ensure that the waste
is
63
identifiable in the event that removal
is
necessary.
Spent pickle liquor
(EPA Hazardous Waste No.
Y.062) generated from steel finishing operations
of
facilities within the
iron and steel industry
(SIC Codes 331 and 332);
waotcwater treatment
sludge (EPA Hazardous Waste No.
K002) generated
from
thefl
production
c-f chrome yellow and orange
pigments; wactewater treatment sludge (EPA
Hazardous Waste No. b~O03) generated from the
production of molybdato orange pigments;
waotcwatcr treatment sludge
(EPA Hazardous Waste
No. K004)
generated from the production of zinc
yellow pigmentos wactewator treatment
oluda-e
(EPA Hit,~rd
thr~
-~
aotcwatcr trea
nfr-
Mr~
T~fl(~7~
i__ 1
r
To ensure that
hazardous conuL~tucnt-oarc not present in the
waste at
~
ut
rcaulatorv concern1
the
facility must implement
a centingency testing
program for the petitioned wastes.
This testing
pro-gram
must moot the following conditions for
the- explusiono to be validi
1)
Each batch of treatment—residue must be
representatively sampled and tooted using
the EP Toxicity test for
arsenic, barium,
oadm-ium-,
chromium,
lead,
selenium,
silver,
mercury,
and nickel.
If the extract
concentrations for chromium,
lead,
arsenic,
and silver
exceed 0.315 ppm,
barium levels exceed 6.3 ppm; cadmuim and
selenium exceed 0.063
ppm;
mercury exceeds
0.0126-ppm;
or nickel
levels exceed 2.205
ppm, the waste must -be re—treated or
managed and disposed as
a hazardous waste
under
35~
Ill. Mm. Code 722 to 725
and the
permitting standards of
35
Ill.
Adm. Code
702,
703,
and 705.
2)
Eachr batch of treatment residue must be
tested for reactive and leachable cyanide.
If the
reactive cyanide levels exceed 250
ppm; or leachable cyanide levels
(using
the EP Toxicity teat without acetic acid
adjustment)
exceed 1.26 ppm, the waste
must be retreated -or managed and disposed
as hazardous waste un~der35
Ill. Mm.
Code
722 to 725 and the permitting standards of
35 Ill.
Adm. Code 702,
703,
and 705.
3)
Each batch of waste must be tested for the
total content of
specific organic
toxteants.
If
the total content of
Envirite Corp.
Harvey,
Illinois
wactewater
treatment
oludge
(EPA
Haza
No.
K006) generated
from the produoti
chrome oxide ~reen pigrncnto (anhydr~
I
‘
Haz-ardo~o
pinments
———-v—
‘——
——
___3
C..~
1.1....
-14, 1~S6
-,
ti-i
7fl~
— —
.I
i
4)
A grab sample must be collected from each
batch to form one monthly oompoaite sample
which must be tested using gas
chromatography, mass spectrometry,
analysis for the compounds
listed
in No.
3
above
as well
as the remaining organioc on
the Priority Pollutant List
inoorporated
by reference,
ceo 40
CFfl 423 App. A (1983)
(as adopted at
47
Fed.
flcg.
52,309
(November
19,
1982)),
not including later
amendments).
-5-)—---
The data
from conditions
1
4 must be kept
on file
at the facility for inspection
purposes and must be compiled,
summarized,
and submitted -to the UCEPA Administrator
by certified mail semi annually.
The
USEPA will review this information and if
needed will propose to modify or withdraw
the exclusion.
Should UCEPA propose to
modify or withdraw the exclusion,
Envirite
shall promptly provide notice thereof to
the Board.
The decision to condition-ally
exclude the treatment
residue generated
from the wastcwatcr treatment systems at
Envirite1s Harvey,
Illinois facility
applies only to- the wastewater and solids
treatment systems as they presently exist
as
described in the delisting petition
submitted to the USEPA.
The exclusion
does not apply to the proposed proc-co-s
additions described
in the petition
submitted to UCEP2\ as recovery,
including
oryatallization, electrolytic metals
rocovorv. evaporative recovery,
and ion
exchange.
USX Steel Corporation-7-
Chicago,
Illinois
Fully—cured chemically stabilized electric arc
furnace dust/sludge
(CSEAFD)
treatment residue
(U.S. EPA Hhazardous Wwaste Ne-~-numberK061)
generated from the primary production of steel
after April
29,
1991.
This exclusion (for
35,000 tons of CSEAFD per year)
is conditioned
i~ponthe data obtained from USX’s full—scale
CSEAFD treatment facility.
To ensure that
hazardous constituents are not present
in the
waste at levels of regulatory concern once the
full—scale treatment facility
is in operation,
TJSX
shall implement
a
testing program
for the
64
anthracone exceeds 76.8 ppm,
1,2-diphenyl
hydra~ineexceeds 0.0~1ppm, methylene
chloride exceeds 8.18 ppm, methyl ethyl
ketono exceeds 326
ppm, n—nitrooo--
diphonylamirie exceeds 11.9 ppm,
phenol
exceeds 1,566 ppm, tetrachloroothylene
exceeds 0.188 ppm, or trichloroothyleno
exceeds 0.592 ppm, the waste muot be
managed and disposed as a havardouo waste
under
35
Ill. Mm.
Code 722 to 725 and the
permitting
-if~~n~1~rdn
-of
?.~
Ti
1
-
1~.dm.
C~odo
65
petitioned waste.
This testing program must
meet the following conditions
for the exclusion
to be valid:
1.
Testing:
Sarnp.e
collection and analyses
(including quality control
(QC)
procedures) must be performed according to
SW—846
methodologies.
EW-8-16
io~
incorporated by reference
in 35 Ill.
Adm.
Code 720.111.
A.
Initial Testing:
During the first
four weeks of operation of the full
scale treatment
system, USX shall
collect representative grab samples
of each treated batch of the CSEAFD
and composite the grab samples
daily.
The daily composites, prior
to disposal,
must be analyzed for
the EP leachate concentrations of
all
‘the EP toxic metals,
nickel,
and
cyanide
(using distilled water in
the cyanide extractions),
and the
total concentrations of reactive
sulfide and reactive cyanide.
IJSX
must report the analytical test
data,
including quality control
information,
obtained during this
initial period no later than 90 days
after the treatment of the first
full—scale batch.
B.
Subsequent Testing:
USX shall
collect representative grab samples
from every treated batch of CSEAFD
generated daily and composite all of
the grab samples to produce a weekly
composite sample.
USX then shall
analyze each weekly composite sample
for all of the EP toxic metals~and
nickel.
The analytical data,
including quality control
information, must be compiled and
maintained on site for
a minimum of
three years.
These data must be
furnished upon request and made
available for inspection by any
employee or representative of U.S~
EPA or the Agency.
2.
Delisting levels:
If the EP extract
concentrations for chromium,
lead,
arsenic,
or silver exceed 0.315 mg/l; 4e~
barium exceeds 6.3 mg/l;
for cadmium or
selenium exceed 0.063 mg/l; for—mecury
exceeds 0.0126 mg/l;
for nickel exceeds
3.15 mg/l;
or for—cyanide exceeds 4.42
mg/l~
total reactive cyanide or total
reactive sulfide levels exceed 250 mg/kg
and 500 mg/kg,
respectively,
the waste
must either be re—treated until
it meets
these levels or managed and disposed of in
66
accordance with Subpart C of Resource
Conservation and Recovery Act
(42 U.S.C.
6901 et seq.).
3.
Data submittal to and enforcement by ~
EPA:
Within one week of system start—up
USX must notify the Section Chief,
Delisting Section
(see address below) when
their full—scale stabilization system is
on—line and waste treatment has begun.
The data obtained through condition (1)(A)
shall
be
submitted
to
the
Section
Chief,
Delisting Section, CAD/OSW
(OS—333),
U.S.
EPA,
401
M Street,
S.W.,
Washington,
DC
20460 within the time period specified.
At
t—ho—U~,S.~...EPA’srequest, USX must submit
any other analytical data obtained through
conditions
(1)(A)
or jfl(B) within the
time peirod specified by the Section
Chief.
Failure to submit the required
data obtained from conditions
(1)(A) or
j.fl(B)
within the specified time period or
maintain the required records for the
specified time will be considered by ~
EPA,
at its decision,
sufficient basis to
revoke USX’s Federal exclusion to the
extent directed by U~S~EPA. All data
must be accompanied by the following
certification statement:
“Under civil and
criminal penalty of
law for the making or
submission of
false or fraudulent
statements or representations
(pursuant to
the applicable provisions of the Federal
Code which include, but may not be limited
to,
18 U.S.C.
Section 6928),
I certify
that the information contained in or
accompanying this document
is true,
accurate and complete.
As to the
(those)
identified section(s)
of this document for
which
I cannot personally verify its
(their)
truth
and
accuracy,
I
certify
as
the company official having supervisory
responsibility for the persons who,
acting
under my direct instructions, made the
vertification that this information
is
true,
accurate and complete.
In the event
that any of this information
is determined
by U~S~EPAin
its sole discretion to be
false,
inaccurate or
incomplete,
and upon
conveyance of this
fact to the company,
I
recognize and agree that this
federal
exclusion of wastes will be void as
if it
never had effect or to the extent directed
by U.~S~EPAand that the company will be
liable
for any actions taken in
contravention of the company’s
RCRA
and
CERCLA obligations premised upon the
company’s reliance on the void exclusion.”
4.
Data Submittal to Agency:
The data
obtained through condition (1)(A) must be
submitted to the Illinois Environmental
67
Protection Agency,
Planning and Reporting
Section,
2200 Churchill Road,
P.O.
Box
19276,
Springfield,
IL
62794—9276
within
the time period specified.
At Agency’s
request, USX must submit any other
analytical data obtained through
conditions
(l)(A)
or jfl(B) within the
time period specified by the Agency.
All
data must be accompanied by the following
certification statement:
“Under civil and
criminal penalty of law for the making or
submission of
false or fraudulent
statements or representations
(pursuant to
the applicable provisions of Illinois’
Environmental Protection Act),
I certify
that the information contained in or
accompanying this document
is true,
accurate and complete.
As to the (those)
identified section(s)
of this document for
which
I
cannot
personally
verify
ita
(their) truth and accuracy,
I certify as
the company official having
supervisory
responsibility
for the persons who, acting
under my direct instructions, made the
verification that this information
is
true,
accurate and complete.,
5.
Enforcement by the
Agency:
Whenever the
Agency finds that USX has violated the
standards in this exclusion, has failed to
submit the required data obtained from
conditions
(1)(A)
or jfl.(B) within the
specified time period, has failed to
maintain the required records for the
specified time or has submitted false,
inaccurate or incomplete data,
the Agency
may take such action as
is allowed by
Title VIII of the Act.
6.
Notification to the Board:
Upon
modification, termination, revocation,
or
other alteration of this exemption by ~
EPA, USX shall file a petition, pursuant
to Part
102,
with this Board requesting
that the Board follow the U.S. EPA action.
(Source:
Amended at 19
Ill. Reg.
________,
effective
_____________________
Section 72l.Appendix
I
Wastes Excluded under Section 720.120 and 720.122~
Administrative Action
Table
C
Wastes Excluded by U.S. EPA under
40 CFR 260.20 and 260.22 fProm
Commercial Chemical Products, 0ff—Specification Species,
Container
Residues,
and Soil Residues Thereof
Facility Address
Waste Description
(Source:
Amended at
19 Ill.
Reg.
________,
effective
_____________________
Section 72l.Appendix
I
Wastes Excluded under Section 720.120 and 720.122~
68
Administrative Action
Table D
Wastes Excluded by the Board by Adjusted Standard
The Board has entered the following orders on petitions for adjusted standards
for delisting,
pursuant to 35
Ill.
Adm.
code 720.122.
AS91—1
Petition of Keystone Steel
and Wire Co.
for Hazardous Waste
Delisting, February
6,
1992,
and modified at 133 PCB 189,
April 23,
1992.
(treated 1(061 waste)
AS91—3
Petition of Peoria Disposal
Co.
for an Adjusted Standard
from 35
Ill.
Adm.
Code 721.Subpart
D, February
6 and March
11,
1993.
(treated F006 waste)
AS93—7
Petition of Keystone Steel
& Wire Co.
for an Adjusted
Standard from 35
Ill.
Adm.
Code 721.Subpart
D, February 17,
1994,
as modified March
17,
1994.
(treated K062 waste)
(Source:
Amended at
19
Ill.
Reg.
________,
effective
_____________________
TITLE 35:
ENVIRONMENTAL PROTECTION
SUBTITLE G:
WASTE DISPOSAL
CHAPTER I:
POLLUTION CONTROL BOARD
SUBCHAPTER
C:
HAZARDOUS WASTE OPERATING REQUIREMENTS
PART 722
STANDARDS APPLICABLE TO GENERATORS OF HAZARDOUS WASTE
SUBPART A:
GENERAL
Section
722.110
Purpose,
Scope and Applicability
722.111
Hazardous Waste Determination
722.112
USEPA Identification Numbers
SUBPART B:
THE
MANIFEST
Section
722.120
General Requirements
722.121
Acquisition of Manifests
722.122
Number of Copies
722.123
Use of the Manifest
SUBPART C:
PRE-TRANSPORT REQUIREMENTS
Section
722.130
Packaging
722.131
Labeling
722.132
Marking
722.133
Placarding
722.134
Accumulation Time
SUBPART D:
RECORDKEEPING AND REPORTING
Section
722. 140
Recordkeeping
722.141
Annual Reporting
722.142
Exception Reporting
722.143
Additional
Reporting
722.144
Special Requirements for Generators of between
100 and 1000
kilograms per month
SUBPART E:
EXPORTS OF HAZARDOUS WASTE
Section
69
722.150
Applicability
722.151
Definitions
722.152
General Requirements
722.153
Notification of Intent to Export
722.154
Special Manifest Requirements
722.155
Exception Report
722.156
Annual Reports
722 .157
Recordkeeping
SUBPART F:
IMPORTS OF HAZARDOUS WASTE
Section
722.160
Imports of Hazardous Waste
SUBPART
G:
FARMERS
Section
722.170
Farmers
722.Appendix A
Hazardous Waste Manifest
AUTHORITY:
Implementing Section 22.4 and authorized by Section 27 of the
Environmental Protection Act 415
ILCS 5/22.4 and 27.
SOURCE:
Adopted in R81-22,
43
PCB 427,
at
5
Ill.
Reg.
9781,
effective ae
noted in 35
Ill. Mm.
Code 700.lO-6May
17, 1982
amended and codified in R81—
22,
45
PCB 317,
at
6 Ill.
Reg.
4828, effective as
noted in 35
Ill. Mm.
Code
700.lO6May 17, 1982
amended in R82—18,
51 PCB 31,
at 7
Ill.
Reg.
2518,
effective February 22,
1983;
amended
in R84—9 at 9
Ill.
Reg.
11950, effective
July 24,
1985;
amended in R85—22 at 10
Ill.
Reg.
1131,
effective January
2,
1986;
amended
in R86—l
at
10
Ill.
Reg.
14112, effective August 12,
1986;
amended in R86-19 at 10
Ill. Reg.
20709, effective December
2,
1986; amended
in R86—46 at 11
Ill. Reg.
13555, effective August
4,
1987;
amended in R87—5 at
11 Ill.
Reg.
19392,
effective November 12,
1987;
amended in R87—39
at
12
Ill.
Reg.
13129, effective July 29,
1988;
amended in R88—l6 at
13
Ill.
Reg.
452,
effective December 27,
1988;
amended in R89—1 at
13 Ill.
Reg.
18523, effective
November 13,
1989;
amended
in R90—lO at
14 Ill.
Reg.
16653, effective
September 25,
1990;
amended in R90—ll at 15
Ill. Reg. 9644,
effective June 17,
1991;
amended in R91—1 at
15
Ill.
Reg.
14562, effective October
1,
1991;
amended
in R91—l3 at 16
Ill. Reg.
9833,
effective June 9,
1992; amended in
R92—l at
16
Ill.
Reg.
17696, effective November
6,
1992;
amended
in R93—4 at
17 Ill.
Reg. 20822,
effective November
22,
1993; amended
in R95-6 at 19
Ill.
Reg.
________,
effective
_____________________
SUBPART
B:
THE
MANIFEST
Section 722.122
Number of Copies
The manifest consists of
at least t~hethatnumber of copies whichthat will
provide the generatorr~each transporter-rI and the owner or operator of the
designated receiving treatment,
storage,
or disposal facility each with one
copy ca-oh--for their records4
and anothorplus provide one copy to be returned
to the generator, a*~4plusprovide two copies to be sent to the Agency,
one by
each of the generator and èy—the HwMreceiving treatment,
storage,
or disposal
facility owner or operator.
(Source:
Amended at
19
Ill.
Reg.
________,
effective
____
SUBPART C:
PRE-TRANSPORT REQUIREMENTS
Section 722.134
Accumulation Time
70
a)
Except as provided in subsections
(d),
(e)4. or
(f)-7- below,
a
generator is
exempt from all the requirements
in 35
Ill.
Adrn.
Code
725.Subparts G and
H,
except
for 35
Ill.
Adm. Code 725.211 and
725.2l4~and may accumulate hazardous waste on—site for 90 days or
less without
a permit or without having interim status,
provided
that:
1)
The waste is placed:
A)
In containers and the generator complies with 35
Ill.
Adm.
Code 725.Subparta
I, AA,
BB,
and CC
or
B)
In tanks and the generator complies with
35
Ill.
Adm.
Code 725.Subparts J jexcept 35
Ill.
Adm.
Code
725.297(c)
and 725.300),
AA,
BB,
and CC
or
C)
On drip pads and the generator complies with 35
Ill.
Adm.
Code 725.Subpart W and maintains the following
records at the facility:
i)
A
description of the procedures that will be
followed to ensure that all wastes are removed
from the drip pad and associated collection
system at least once every 90
daysj-4. and
ii)
Documentation of each waste removal,
including
-
the quantity of waste removed
from the drip pad
and the sump or collection system and the date
and time of removal;
or
D)
In containment buildings and the generator
complies
with 35
Ill. Adm.
Code 725.Subpart DD
(has placed its
Professional Engineer
(FE) certification that the
building complies with the design standards specified
in 35 Ill. Adm. Code 725.1101 in the facility’s
operating record no later than 60 days aftorprior to
the date of initial operation of the unit).
After
February 18,
1993,
the PE certification will be
required prior to operation of the unit.
The owner or
operator shall maintain the following records at the
facility:
i)
A written description of procedures to ensure
that each waste volume remains in the unit for
no more than 90 days,
a written description of
the waste generation and management practices
for the
facility showing that they are
consistent with respecting the 90 day limit,
and
documentation that the procedures are complied
with; or
ii)
Documentation that the unit
is emptied at least
once every 90 days.
BOARD NOTE:
The
“in addition” hanging
subsection
i.ihichthat
appears
in
the
Federal
rules
after 40 CFR 262.34(a)(1)(iv)(B)
is
in the
introduction to subsection
(a),- above.
2)
The date upon which each period of accumulation begins
is
clearly marked and visible for inspection on each container;
71
3)
While being accumulated on-site, each container and tank is
labeled or marked clearly with the
words-,- “Hazardous Waste”,
and
4)
The generator complies with the requirements for treatment,
storage,
and disposal facility owners or operators
in 35
Ill. Adm. Code 725.Subparts C and
D,.- and with 35
Ill.
Adin.
Code 725.116 and 728.107(a)(4).
b)
A generator w~ethataccumulates hazardous waste for more than 90
days is
an operator of
a storage facility and
is subject to the
requirements of
35
Ill.
Adxn.
Code 724 and
725 and the permit
requirements of
35
Ill.
Adm.
Code 702, 703 and 705 unless the
generator has been granted an extension of the 90-day period.
If
hazardous wastes must remain on—site for longer than 90 days due
to unforeseen,
temporary,
and uncontrollable circumstances, the
generator may seek an extension of up to 30 days by means of
a
variance or provisional variance, pursuant to Section 37 of the
Environmental Protection Act and 35
Ill.
Adm.
Code 180 (A~encv
procedural regulations).
c)
Accumulation near the point of generation.
1)
A generator may accumulate as much as
55 gallons of
hazardous waste or one quart of acutely hazardous waste
listed in
35
Ill.
Adm.
Code 721.133(e)
in containers at or
near any point of generation where wastes initially
accumulate-,- whiohthat
is under the control of the operator
of the process generating the waste- without
a permit or
interim status and without complying with subsection
(a),-
above,
provided the generator:
A)
Complies with 35
Ill.
Adm. Code 725.271,
725.272 and
725.273(a)~~and
B)
Marks
the generator’s containers either with the words
“Hazardous Waste” or with other words that identify
the contents of the containers.
2)
A generator whethat accumulates
either hazardous waste or
acutely hazardous waste listed in 35 Ill.
Adm. Code
721.133(e)
in excess of the amounts Listed in subsection
(c)(1),-
above.,- at or near any point of generation must, with
respect to that amount of excess waste,
comply within three
days with subsection
(a)-,- above,- or other applicable
provisions of this eghapter.
During the three day period
the generator must continue to comply with subsection
(c)(1).,- above.
The generator must mark the container
holding the excess accumulation of hazardous waste with the
date the excess amount began accumulating.
d)
A generator whethat generates greater than 100 kilograms but less
than 1000 kilograms of hazardous waste in a calendar month may
accumulate hazardous waste on—site for 180 days or less without a
permit or without having interim status provided that:
1)
The quantity of waste accumulated on—site never exceeds 6000
kilograms;
2)
The generator complies with the requirements of
35 Ill.
Adrn.
Code 725.Subpart
I-,- ~except the generator need-not comply
with 35
Ill.
Adm. Code 725.276 and 725.278)
72
3)
The generator complies with the requirements of
35 Ill.
Adm.
Code 725.301;
4)
The generator complies with the requirements of subsections
(a)(2) and
jgj(3)-,-
above, ef—35 Ill. Adm.
Code 725.Subpart
C,~, and e~—35 Ill. Adm. Code 728.107(a) (4); and
5)
The generator complies with the following requirements:
A)
At all times there must be at least one employee
either on the premises or on call
(i.e., available to
respond to an emergency by reaching the facility
within a short period of time) with the responsibility
for coordinating all emergency response measures
specified
in subsection
(d)(5)(D),- below.
The
employee is the emergency coordinator.
B)
The generator shall post the following information
next to the telephone:
i)
The name and telephone number of the emergency
coordinatori-~
ii)
Location of fire extinguishers and spill control
material,- and4
if present,
fire
alarm-*-~and
iii)
The telephone number of the fire department,
unless the facility has
a direct alarm.
C)
The generator shall ensure that all employees are
thoroughly familiar with proper waste handling and
emergency procedures, relevant to their
responsibilities during normal
facility operations and
emergencies~.L
D)
The emergency coordinator or designee shall respond to
any emergencies that arise.
The applicable responses
are as follows:
i)
In the event of a fire,
call the fire department
or attempt to extinguish it using
a fire
extinguisheri-~
ii)
In the event of a spill,
contain the flow of
hazardous waste to the extent possible,- and,~as
soon as
is practicable, clean up the hazardous
waste and any contaminated materials or soil÷~
iii)
In the event of a fire, explosion~or other
release whichthat could threaten human health
outside the facility~or when the generator has
knowledge that
a spill has reached surface
water, the generator shall immediately notify
the National Response Center (using
its 24—hour
toll free number 8OO~,’-z424-88O2).
The report
must include the following information:
the
name, address~and U.S. EPA identification
number
(35
Ill.
Adm. Code 722.112)
of the
generator; the date, time~and type of incident
(e.g.,
spill or fire); the quantity and type of
hazardous waste involved in the incident; the
extent of injuries,
if any;
and-, the estimated
73
quantity and disposition of recoverable
materials,
if any.
e)
A generator whethat generates greater than 100 kilograms but less
than 1000 kilograms of hazardous waste in a calendar month and
whethat must transport the
waste-,- or offer the waste for
transportation., over a distance of 200 miles or more for off—site
treatment,
storage4, or disposal may accumulate hazardous waste on—
site for 270 days or less without
a permit or without having
interim
status,,
provided that the generator complies with the
requirements of subsection
(d),- above.
f)
A generator whethat generates greater than 100 kilograms but less
than 1000 kilograms of hazardous waste in a calendar month and
whethat accumulates hazardous waste in quantities exceeding 6000
kg or accumulates hazardous waste for more than 180 days
(or for
more than 270 days if the generator must transport the
waste-i- or
offer the waste for transportation,- over a distance of 200 miles
or more)
is an operator of a storage
facility and
is subject to
the requirements
of
35
Ill.
Adm. Code 724 and 725 and the permit
requirements of
35
Ill. Adm.
Code 703 unless the generator has
been granted an extension to the 180—day
(or 270-day
if
applicable) period.
If hazardous wastes must remain on—site for
longer than 180 days
(or 270 days
if applicable)
due to
unforeseen,
temporary4
and uncontrollable circumstances, the
generator may seek an extension of up to 30 days by means of
variance or provisional variance pursuant to Section 37 of the
Environmental Protection Act.
(Source:
Amended at
19
Ill.
Reg.
________,
effective
______________________
TITLE
35:
ENVIRONMENTAL PROTECTION
SUBTITLE G:
WASTE DISPOSAL
CHAPTER
I:
POLLUTION CONTROL BOARD
SUBCHAPTER c:
HAZARDOUS WASTE OPERATING REQUIREMENTS
PART 723
STANDARDS APPLICABLE TO
TRANSPORTERS OF HAZARDOUS WASTE
SUBPART A:
GENERAL
Section
723.110
Scope
723.111
USEPA Identification Number
723.112
Transfer Facility Requirements
SUBPART
B:
COMPLIANCE WITH THE MANIFEST SYSTEM
AND RECORDKEEPING
Section
723.120
The Manifest System
723.121
Compliance with the Manifest
723.122
Recordkeeping
SUBPART
C:
HAZARDOUS WASTE DISCHARGES
Section
723.130
Immediate Action
723.131
Discharge Clean Up
AUTHORITY:
Implementing Section 22.4 and authorized by Section 27 of the
Environmental Protection Act
415
ILCS 5/22.4 and 27).
74
SOURCE:
Adopted
in R81-22,
43 PCB 427,
at
5
Ill. Reg. 9781, effective ee
not-ed in 35 Ill.
Adm.
Code 700.1O6May 17~ 1982 amended and codified in
R8l—22,
45 PCB
17,
at
6 Ill.
Reg. 4828,
effective as
noted in 35 Ill.
Adm.
Code 700.lO6May 17,
1982
amended in R84—9,
at
9
Ill.
Reg.
11961,
effective
July 24,
1985;
amended
in R86—19,
at
10
Ill.
Reg.
20718, effective December
2,
1986;
amended in R86—46 at
11
Ill.
Reg.
13570,
effective August
4,
1987;
amended in R87—5 at
11
Ill. Reg.
19412,
effective November 12,
1987;
amended
in R95—6 at
19
Ill.
Reg.
________,
effective
_____________________
SUBPART C:
HAZARDOUS WASTE DISCHARGES
Section 723.130
Immediate Action
a)
In the event of
a discharge of hazardous waste during
transportation, the transporter must take appropriate immediate
action to protect human health and the environment
(e.g., notify
local authorities, dike the discharge area).
b)
If
a discharge of hazardous waste occurs during transportation and
an official (QL&~tateor local government or Qj~.a~ederal
&~gency)acting within the scope of his or her official
responsibilities determines that immediate removal of the waste
is
necessary to protect human health or the environment, that
official may authorize the removal of the waste by transporters
whethat do not have 0.5. EPA identification numbers and without
the preparation of a manifest.
c)
An air,
rail,
highway.~or water transporter whethat has discharged
hazardous waste must:
1)
Give notice,
if required by
49
CFR
171.15, to the National
Response Center
(800—424—8802
or 202—426—2675),
if required
by 49 CFR 171.15;
and
2)
Report in writing as required by
49 CFR 171.16 to the
Director, Office of Hazardous Materials Regulations,
Materials Transportation Bureau, Department of
Transportation, Washington,
D.C.
20590,
as required by 49
CFR 171.16
and,-
3)
give notice to:
Emergency Cervices and Dicastor Agency,
110 E. Maim
Springfield,
Il 62706,
A/C
217 782—7860.
Illinois Emergency Management Agency
110
East Adams
Springfield,
Illinois
62706
217—782—7860
d)
A water (bulk shipment) transporter whethat has discharged
hazardous waste must give the same notice
as required by 33 CFR
153.203 for oil
and hazardous substances.
(Source:
Amended at 19 Ill. Reg.
________,
effective
____________________
TITLE
35:
ENVIRONMENTAL PROTECTION
SUBTITLE
G:
WASTE DISPOSAL
CHAPTER
I:
POLLUTION CONTROL BOARD
SUBCHAPTER
c:
HAZARDOUS WASTE OPERATING REQUIREMENTS
75
PART 724
STANDARDS FOR OWNERS
AND
OPERATORS OF HAZARDOUS
WASTE
TREATMENT,
STORAGE,
AND DISPOSAL FACILITIES
SUBPART A:
GENERAL PROVISIONS
Section
724.101
Purpose,
Scope and Applicability
724.103
Relationship to Interim Status Standards
SUBPART
B:
GENERAL FACILITY STANDARDS
Section
724.110
Applicability
724.111
Identification Number
724.112
Required Notices
724.113
General Waste Analysis
724.114
Security
724.115
General Inspection Requirements
724.116
Personnel Training
724.117
General Requirements
for Ignitable, Reactive or Incompatible
Wastes
724.118
Location Standards
724.119
Construction Quality Assurance Program
SUBPART
C:
PREPAREDNESS
AND
PREVENTION
Section
724.130
Applicability
724.131
Design and Operation of Facility
724.132
Required Equipment
724.133
Testing and Maintenance of Equipment
724.134
Access to Communications or Alarm System
724.135
Required Aisle Space
724.137
Arrangements with Local Authorities
SUBPART D:
CONTINGENCY PLAN
AND
EMERGENCY PROCEDURES
Section
724. 150
Applicability
724.151
,
Purpose and Implementation of Contingency Plan
724.152
Content of Contingency Plan
724.153
Copies of Contingency Plan
724.154
Amendment
of
Contingency Plan
724.155
Emergency Coordinator
724.156
Emergency Procedures
SUBPART
E:
MANIFEST
SYSTEM,
RECORDKEEPING
AND
REPORTING
Section
724.170
Applicability
724.171
Use of Manifest System
724.172
Manifest Discrepancies
724.173
Operating Record
724.174
Availability, Retention and Disposition of Records
724.175
Annual Report
724.176
Unmanifested Waste Report
724.177
Additional Reports
SUBPART F:
RELEASES FROM SOLID WASTE MANAGEMENT UNITS
Section
724. 190
Applicability
724. 191
Required Programs
724.192
Groundwater Protection Standard
724.193
Hazardous Constituents
724. 194
Concentration Limits
724.195
Point of Compliance
76
724.196
Compliance Period
724.197
General Groundwater Monitoring Requirements
724.198
Detection Monitoring Program
724.199
Compliance Monitoring Program
724.200
Corrective Action Program
724.201
Corrective Action for Solid Waste Management Units
SUBPART G:
CLOSURE AND POST-CLOSURE
Section
724.210
Applicability
724.211
Closure Performance Standard
724.212
Closure Plan; Amendment of Plan
724.213
Closure; Time Allowed For Closure
724.214
Disposal or Decontamination of Equipment, Structures and Soils
724.215
Certification of
Closure
724.216
Survey Plat
724.217
Post—closure Care and Use of Property
724.218
Post—closure Plan;
Amendment of Plan
724.219
Post—closure Notices
724.220
Certification of Completion of Post-closure Care
SUBPART H:
FINANCIAL REQUIREMENTS
Section
724.240
Applicability
724.241
Definitions of Terms As Used In This Subpart
724.242
Cost Estimate for Closure
724.243
Financial Assurance for Closure
724.244
Cost Estimate for Post-closure Care
724.245
Financial Assurance for Post—closure Care
724.246
Use of
a Mechanism for Financial Assurance of Both Closure and
Post—closure Care
724.247
Liability Requirements
724.248
Incapacity of Owners or Operators, Guarantors or Financial
Institutions
724.251
Wording of the Instruments
SUBPART I:
USE AND MANAGEMENT OF CONTAINERS
Section
724.270
Applicability
724.271
Condition of Containers
724.272
Compatibility of Waste With Container
724.273
Management
of Containers
724.274
Inspections
724.275
Containment
724.276
Special Requirements for Ignitable or Reactive Waste
724.277
Special Requirements for Incompatible Wastes
724.278
Closure
724.279
Air Emission Standards
SUBPART
J:
TANK SYSTEMS
Section
724.290
Applicability
724.291
Assessment of Existing Tank System’s Integrity
724.292
Design and Installation of New Tank Systems or Components
724.293
Containment and Detection of Releases
724.294
General Operating Requirements
724.295
Inspections
724.296
Response to Leaks or Spills and Disposition of Leaking or unf it—
for—use Tank Systems
724.297
Closure and Post—Closure Care
724.298
Special Requirements for Ignitable or Reacti,ve Waste
724.299
Special Requirements for Incompatible Wastes
77
724.300
Cpocial Requirements for 1Ia~ardousWastes F020,
P021,
F022,
P023,
F026 and FO27Air Emission Standards
SUBPART K:
SURFACE IMPOUNDMENTS
Section
724.320
Applicability
724.321
Design and Operating Requirements
724.322
Action Leakage Rate
724.323
Response Actions
724.326
Monitoring and Inspection
724.327
Emergency Repairs; Contingency Plans
724.328
Closure and Post—closure Care
724.329
Special Requirements
for Ignitable or Reactive Waste
724.330
Special Requirements
for Incompatible Wastes
724.331
Special Requirements for Hazardous Wastes F020, FO21,
F022,
F023,
F026 and F027
724.332
Air Emission Standards
SUBPART
L:
WASTE PILES
Section
724.350
Applicability
724.351
Design and Operating Requirements
724.352
Action Leakage Rate
724.353
Response Action Plan
724.354
Monitoring and Inspection
724.356
Special Requirements for Ignitable or Reactive Waste
724.357
Special Requirements for Incompatible Wastes
724.358
Closure and Post—closure Care
724.359
Special Requirements for Hazardous Wastes F020,
F02l,
F022,
FO23,
F026 and F027
SUBPART M:
LAND TREATMENT
Section
724.370
Applicability
724.371
Treatment Program
724.372
Treatment Demonstration
724.373
Design and Operating Requirements
724.376
Food-chain Crops
724.378
Unsaturated Zone Monitoring
724.379
Recordkeeping
724.380
Closure and Post-closure Care
724.381
Special Requirements
for Ignitable or Reactive Waste
724.382
Special Requirements for Incompatible Wastes
724.383
Special Requirements
for Hazardous Wastes FO2O,
F021,
F022,
F023,
F026 and F027
SUBPART N:
LANDFILLS
Section
724.400
Applicability
724.401
Design and Operating Requirements
724.402
Action Leakage Rate
724.403
Monitoring and Inspection
724.404
Response Actions
724.409
Surveying and Recordkeeping
724.410
Closure and Post—closure Care
724.412
Special Requirements for Ignitable or Reactive Waste
724.413
Special Requirements for Incompatible Wastes
724.414
Special Requirements
for Bulk and Containerized Liquids
724.415
Special Requirements for Containers
724.416
Disposal of Small Containers of Hazardous Waste in Overpacked
Drums
(Lab Packs)
724.417
Special Requirements
for Hazardous Wastes F020,
FO21,
F022,
F023,
78
Applicability
Waste Analysis
Principal Organic Hazardous
Performance Standards
Hazardous Waste Incinerator Permits
Operating Requirements
Monitoring and Inspections
Closure
SUBPART S:
CORRECTIVE
ACTION FOR SOLID WASTE MANAGEMENT UNITS
Corrective Action Management Units
Temporary Units
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,
Corrective Action
Post—closure Care
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
Reporting Requirements
SUBPART BB:
AIR EMISSION STANDARDS FOR EQUIPMENT LEAKS
Applicability
Definitions
Standards:
Standards:
Standards:
Standards:
Standards:
Standards:
Standards:
Connectors
Standards:
Standards:
Alternative
Skip Period
Test Methods and Procedures
F026 and F027
SUBPART 0:
INCINERATORS
Constituents
(POHC5)
Section
724. 440
724. 441
724. 442
724. 443
724. 444
724. 445
724. 447
724. 451
Section
724. 652
724.653
Section
724. 670
724. 671
724. 672
724. 673
724. 674
724. 675
Section
724. 700
724. 701
724. 702
724. 703
Section
724. 930
724. 931
724. 932
724. 933
724.934
724.935
724.936
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
Reporting and
Pumps
in
Light
Liquid
Service
Compressors
Pressure Relief Devices in Gas/Vapor Service
Sampling Connecting Systems
Open—ended Valves or Lines
Valves in Gas/Vapor or Light Liquid Service
Pumps,
Valves,
Pressure Relief Devices and Other
Delay of Repair
Closed—vent Systems and Control Devices
Percentage Standard for Valves
Alternative
for Valves
79
724. 964
Recordkeeping Requirements
724.965
Reporting Requirements
SUBPART CC:
AIR EMISSION STANDARDS FOR TANKS,
SURFACE IMPOUNDMENTS,
AND CONTAINERS
Section
724.980
Applicability
724.981
Definitions
724.982
Standards:
General
724.983
Waste Determination Procedures
724.984
Standards:
Tanks
724.985
Standards:
Surface Im2oundments
724.986
Standards:
Containers
724.987
Standards:
Closed—vent Systems and Control Devices
724.988
Inspection and Monitoring Requirements
724.989
Recordkeepinq Requirements
724.990
Reportina Requirements
724.991
Alternative Control Requirements
for Tanks
SUBPART DD:
CONTAINMENT BUILDINGS
Section
724.1100
Applicability
724.1101
Design and operating standards
724.1102
Closure and pPost-closure e~are
724.Appendix A
Recordkeeping Instructions
724.Appendix B
EPA Report Form and Instructions
(Repealed)
724.Appendix D
Cochran’s Approximation to the Behrens—Fisher Student’s T—
Test
724.Appendix E
Examples of Potentially Incompatible Waste
724.Appendix
I
Groundwater
Monitoring
List
AUTHORITY:
Implementing Section 22.4 and authorized by Section 27
of the
Environmental Protection Act 415
ILCS
5/22.4 and 27.
SOURCE:
Adopted in R82—19,
53 PCB
131,
at
7
Ill. Reg.
14059, effective
October
12,
1983;
amended in R84—9 at
9
111.
Reg.
11964,
effective July 24,
1985;
amended in 1185—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—l
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—1l at 15
Ill. Reg.
9654,
effective June
17,
1991; amended in R91—l
at
15
Ill. Reg. 14572, effective October
1,
1991;
amended
in R9l—13 at
16 Ill.
Reg.
9833,
effective June
9,
1992;
amended in R92—1 at
16 Ill. Reg.
17702,
effective November
6,
1992;
amended in R92—10 at
17
Ill. Reg.
5806, effective
March
26,
1993;
amended in R93—4
at
17
Ill. Reg.
20830, effective November 22,
1993; amended
in R93—16
at
18
Ill. Reg.
6973,
effective April 26,
1994;
amended in
1194—7 at
18
Ill.
Reg.
12487, effective July
29,
1994;
amended in
R94—17
at
18 Ill. Reg.
17601,
effective November 23,
1994;
amended in R95—6 at
19
Ill. Reg.
________,
effective
_____________________
SUBPART A:
GENERAL PROVISIONS
Section 724.101
Purpose, Scope and Applicability
80
a)
The purpose of this Part
is to establish minimum standards
whiohthat define the acceptable management of hazardous waste.
b)
The standards in this Part apply to owners and operators of all
facilities whichthat treat, store~or dispose of hazardous waste,
except as specifically provided otherwise
in this Part or
35 Ill.
Adm.
Code 721.
C)
The requirements of this Part apply to a person disposing of
hazardous waste by means of ocean disposal subject to a permit
issued under the Marine Protection, Research and Sanctuaries Act
(16 U.S.C.
1431—1434,
33 U.S.C.
1401)
only to the extent they are
included in
a RCRA permit by rule granted to such a person under
35
Ill.
Adm. Code 703.141.
A “RCRA permit” is
a permit required
by Section 21(f) of the Environmental Protection Act and 35
Ill.
Adm. Code 703.121.
BOARD NOTE:
This Part does apply to the treatment or storage of
hazardous waste before it
is
loaded onto an ocean vessel for
incineration or disposal
at sea.
d)
The requirements of this Part apply to
a person disposing of
hazardous waste by means of underground injection subject to
a
permit issued by the Agency pursuant to Section 12(g)
of the
Environmental Protection Act only to the extent they are required
by 35
Ill.
Adm.
Code 704,—~SubpartF.
BOARD NOTE:
This Part does apply to the above—ground treatment or
storage of hazardous waste before it
is injected underground.
e)
The requirements of this Part apply to the owner or operator of
a
POTW (publicly owned treatment works) whichthat treats,
stores.L or
disposes of hazardous waste only to the extent
included in a RCRA
permit by rule granted to such
a person under 35
Ill. Adm. Code
703.141.
f)
This subsection corresponds with 40 CFR 264.1(f), which provides
that the federal
regulations do not apply to T/S/D activities
in
authorized states,
except under limited,
enumerated circumstances.
This statement maintains structural consistency with U.S. EPA
rules.
g)
The requirements of this Part do not apply to:
1)
The owner or operator of
a facility permitted by the Agency
under Section 21
of the Environmental Protection Act to
manage municipal or industrial solid waste,
if the only
hazardous waste the facility treats,
stores~,or disposes of
is excluded from regulation under this Part by 35
Ill.
Adm.
Code 721.105.
BOARD
NOTE:
The owner or operator may be subject to
35 Ill.
Adm.
Code 807 and may have to have
a supplemental permit
under 35
Ill. Adm. Code 807.210.
2)
The owner or operator of
a facility managing recyclable
materials described
in 35
Ill.
Adm.
Code 721.106(a) (2),-
through
(a)(4)
(except to the extent that requirements of
this Part are referred to in 35 Ill. Mm.
Code 726.Subparts
C,
F,
G,
or H or 35
Ill. Mm.
Code 739).
3)
A generator accumulating waste on—site in compliance with 35
81
Ill. Adm. Code 722.134.
4)
A farmer disposing of waste pesticides from the farmer’s Own
use in compliance with 35 Ill. Adm. Code 722.170.
5)
The owner or operator of a totally enclosed treatment
facility,
as defined
in
35
Ill. Adm.
Code
720.110.
6)
The owner or operator of an elementary neutralization unit
or a wastewater treatment unit.1, as defined in 35 Ill.
Adm.
Code 720.110, provided that
if the owner or operator
is
diluting hazardous ignitable
(DOOl) wastes
(other than the
DOOl High TOC Subcategory defined in 35
Ill.
Adm. Code
728.Table BT),- or corrosivoreactive (D00~) waste-,- to remove
the characteristic before land disposal,
the owner or
operator must comply with the requirements set out in
Section 724.117(b)
of this part;~,
7)
Immediate response:
A)
Except as provided in subsection (~)(8)(B)below,
a
person engaged
in
treatment or containment activities
during immediate response to any of the following
situations:
i)
A
discharge of
a hazardous waste;
ii)
An
imminent and substantial threat of
a
discharge of hazardous waste;
iii)
A
discharge of
a material whichthat, when
discharged, becomes a hazardous waste when
discharged.
B)
An owner or operator of
a facility otherwise regulated
by this Part must comply with all applicable
requirements
of 724.Subparts C and D.
C)
Any person
whethat
is
covered by subsection
(.~g)(8)(A)
above and
whethat
continues or initiates hazardous
waste treatment or containment activities
after the
immediate response is over is subject to all
applicable requirements of this Part and 35
Ill. Adm.
Code 702, 703~and 705 for those activities.
Or,
8)
A
transporter storing manifested shipments of hazardous
waste in containers meeting the requirements of 35
Ill. Adm.
Code
722.130
at
a transfer facility for
a period of ten days
or less.
9)
The addition of absorbent materials to waste in a container
(as defined in
35 Ill. Adm. Code 720)
or the addition of
waste to absorbent material in a container, provided these
actions occur at the time waste
is first placed in the
container~~and Sections 724.117(b),
724.271.1, and 724.272
are complied with.
h)
This Part applies to owners and operators of facilities whichthat
treat,
storer or dispose of hazardous wastes referred to in 35
Ill.
Adm.
Code 728.
(Source:
Amended at
19
Ill. Reg.
________,
effective
_____________________
82
SUBPART B:
GENERAL FACILITY STANDARDS
Section 724.113
General Waste Analysis
a)
Analysis:
1)
Before an owner or operator treats, storea~or disposes of
any hazardous wastes,
or non—hazardous wastes
if applicable
under Section
724.213(d),
the owner or operator shall obtain
a detailed chemical and physical analysis of a
representative sample of the wastes.
At
a minimum, the
analysis must contain all the information whichthat must be
known to treat,
store4, or dispose of the waste
in accordance
with this Part and 35
Ill.
Adrn.
Code
728.
2)
The analysis may include data developed under
35
Ill.
Adxn.
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)(l)
above.
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)(l)
above,
except as otherwise specified in
35 Ill. Adm.
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) 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
movcmentshipment 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 ~hichthat describes the procedures whichthat
it will
carry out to comply with subsection
(a)
above.
The owner or
operator shall keep this plan at the facility.
At a minimum,
the
83
plan must specify:
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 waste’s properties to
comply with subsection
(a)
above).
2)
The test methods whichthat will be used to test for these
parameters.
3)
The sampling method whichthat 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. Mm.
Code 721.Appendix
A; or
B)
An equivalent sampling method.
BOARD NOTE:
See 35
Ill.
Adm.
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 whichthat 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)4, and 724.963(d),
and 724.983
and
35
Ill. Adm. Code 728.107. And,
7)
For surface impoundments exempted from land disposal
restrictions under 35
Ill. Mm.
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 whichthat are not
delisted under
35
Ill. Adm. Code 720.122 or which
exhibit
a characteristic of hazardous waste-, and
either:
i)
Do not meet applicable treatment standards of
35
Ill.
Adm. Code 728.Subpart
D; or
ii)
Where no treatment
standards have been
established-.-4, S~uchresidues are prohibited from
land disposal under
35
Ill. Adm. Code 728.132 or
‘728.l39-~-
or such residues are prohibited from
land disposal under
35
Ill. Adm. Code
728.133(f).
~J,
For owners and operators seeking an exemption to the air
emission standards of 724.Subpart CC in accordance with
84
Section 724.982:
~,
The procedures and schedules
for waste sampling and
analysis and the analysis of test data to verify the
exemption,
and
~j
Each generator’s notice and certification of the
volatile organic concentration in the waste
if the
waste is received from off site.
C)
For off—site facilities,
the waste analysis plan required
in
subsection
(b)
above must also specify the procedures whiohthat
will be used to inspect and,
if necessary,
analyze each
movcmentshipment 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 whichthat will be used to determine the
identity of each movement of waste managed at the facility;
2)
The sampling method whichthat will be used to obtain a
representative sample of the waste to be identified,
if the
identification method includes
sampling-r;
and
3)
The procedures that the owner or operator of an off—site
landfill receiving containerized hazardous waste will use to
determine whether a hazardous waste generator or treater has
added a biodegradable sorbent to the waste in the
container.
BOARD NOTE:
35
Ill.
Adm. Code 703,- requires that the waste
analysis plan be submitted with Part B of the permit
application.
(Source:
Amended at
19
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
errors4,
and discharges whiohthat 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.
1)
The owner or operator shall develop and follow a written
schedule for inspecting monitoring equipment,
safety and
emergency equipment,
security devices4, and operating and
structural equipment
(such as dikes and sump pumps)
that are
important to preventing,
detecting4, or responding to
environmental or human health hazards.
2)
The owner or operator shall keep this schedule at the
facility.
85
3)
The schedule must identify the types of problems
(e.g.,
malfunctions or deterioration) whiehthat 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
deterioration of the equipment and the probability of an
environmental or human health incident if the deterioration,
malfunction4, 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 724.274,
724.293,
724.295,
724.326,
724.354,
724.378,
724.403,
724.447,
724.702,
724.933,
724.952,
724.9534,
and
724.958,
724.988,
and
724.9911b’j,
where applicable.
BOARD NOTE:
35
Ill. Mm.
Code 703 requires the inspection
schedule to be submitted with Part
B of the permit
application.
The Agency wilimust 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 whichthat 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 date4, and nature of any repairs or other
remedial actions.
(Source:
Amended
at
19
Ill. Reg.
________,
effective
_____________________
SUBPART D: CONTINGENCY PLAN AND EMERGENCY PROCEDURES
Section 724.156
Emergency Procedures
a)
Whenever there is an imminent or actual emergency situation, the
emergency coordinator
(or the designee when the emergency
coordinator
is on call)
shall immediately:
1)
Activate internal facility alarms or communication systems,
where applicable,
to notify all facility personnel;
and
2)
Notify appropriate state or local agencies with designated
response roles
if their help is needed.
b)
Whenever there
is
a release,
fire,
or explosion,
the emergency
coordinator shall immediately identify the character,
exact
source,
amount,
and areal extent
of any released materials.
The
emergency coordinator may do this by observation or review of
86
facility records or manifests, and,
if necessary,
by chemical
analysis.
c)
Concurrently, the emergency coordinator shall assess possible
hazards to human health or the environment that may result
from
the release,
fire,
or explosion.
This assessment must consider
both direct and indirect effects of the release,
fire,
or
explosion
(e.g., the effects of any toxic,
irritating,
or
asphyxiating gases that are generated, or the effects of any
hazardous surface water run—off from water or chemical agents used
to control fire and heat—induced explosions).
d)
If the emergency coordinator determines that the facility has had
a release,
fire,
or explosion that
could threaten human health, or
the environment, outside the facility, the emergency coordinator
shall report the findings as follows:
1)
If
the assessment indicates that evacuation of local areas
may be advisable,
the emergency coordinator shall
immediately notify appropriate local authorities.
The
emergency coordinator must be available to help appropriate
officials decide whether local areas should be evacuated;
and
2)
The emergency coordinator shall immediately notify either
the government official designated as the on—scene
coordinator for that geographical area
(in the applicable
regional contingency plan under 40 CFR Part
300),- or the
National Response Center
(using their 24-hour toll free
number 800—424—8802).
The report must include:
A)
Name and telephone number of reporter;
B)
Name and address of facility;
C)
Time and type of incident
(e.g.,
release,
fire);
D)
Name and quantity of material-(-s±involved,
to the
extent known;
E)
The extent of injuries,
if any;
and
F)
The possible hazards to human
health-,- or the
environment, outside the facility.
e)
During an emergency,
the emergency coordinator shall take all
reasonable measures necessary to ensure that fires,
explosions,
and releases do not occur, recur,
or spread to other hazardous
waste
at the facility.
These measures must include, where
applicable, stopping processes and operations,
collecting and
containing release waste,
and removing or isolating containers.
f)
If the facility stops operations
in response to
a fire, explosion4,
or release, the emergency coordinator shall monitor for leaks,
pressure buildup,
gas generation, or ruptures
in valves,
pipes,
or
other equipment,
wherever this is appropriate.
g)
Immediately after
an emergency, the emergency coordinator shall
provide for treating,
storing, or disposing of recovered waste,
contaminated soil or surface water,
or any other material that
results from a release,
fire,
or explosion
at the facility.
87
BOARD NOTE:
Unless the owner or operator can demonstrate,
in
accordance with
35
Ill. Adm. Code 721.l03(e~)or
(~e),that the
recovered material
is not a hazardous waste,
the owner or operator
becomes a generator of hazardous waste and shall manage
it in
accordance with
all applicable requirements of
35
Ill.
Adm.
Code
722,
723,
and 724.
h)
The emergency coordinator shall ensure that, in the affected
area.(-s-)- of the facility:
1)
No waste that may be incompatible with the released material
is treated,
stored,
or disposed of until cleanup procedures
are completed;
and
2)
All emergency equipment listed
in the contingency plan is
cleaned and fit for
its intended use before operations are
resumed.
i)
The owner or operator shall notify the Agency, and appropriate
state and local authorities, that the facility is in compliance
with paragraphsubsection
(h)
above before operations are resumed
in the affected area-(-s+
of the facility.
j)
The owner or operator shall note in the operating record the time,
date, and details of any incident that requires
implementing the
contingency plan.
Within
15 days after the
incident, the owner or
operator shall submit a written report on the incident to the
Agency.
The report must include:
1)
Name,
address,
and
telephone
number
of
the
owner
or
operator;
2)
Name,
address,
and telephone number of the facility;
3)
Date,
time,
and type of
incident
(e.g.,
fire,
explosion);
4)
Name
and
quantity of material-(-s-~- involved;
5)
The extent of
injuries,
if
any;
6)
An assessment of actual or potential
hazards to human health
or the environment, where this is
applicable; and
7)
Estimated quantity and disposition of recovered material
that resulted from the incident.
(Source:
Amended at
19 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
88
treatment,
storage4, or disposal at the facility4, as required
by Section 724.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 and waste
determinations performed as specified in Sections 724.113,
724.117,
724.414,
724.441,
724.934,
724.963,
and 724.983 and
in 35
Ill. Adm. Code 728.104(a) and 728.107;
4)
Summary reports
and details of all
incidents that require
implementing the contingency plan4, as specified in Section
724.156(j);
5)
Records and results of
inspections4, as
required by Section
724.115(d)
(except these data need to be kept only three
years);
6)
Monitoring,
testing4, or analytical data and corrective
action data where required by 724.Subpart
F or Sections
724.119,
724.291,
724.293,
724.295,
724.322,
724.323,
724.326,
724.352 through 724.354,
724.376,
724.378,
724.380,
724.402 through 724.404,
724.409,
724.447,
724.702,
724.934(c)
through
(f),
724.935,
724.963(d) through
(i)4, e~
724.964,
724.988,
724.989,
and
724.991-v.~.
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 pernhittee determines
to be economically practicable~-4,and that the proposed
method of treatment,
storage4, or disposal
is that
practicable method currently available to the permittee
whichthat 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.
Adm. Code
728.105,
a petition pursuant to 35 Ill.
Adin.
Code 728.106 or
a certification under 35
Ill. Adm. Code 728.108,
and the
applicable notice required of
a generator under
35
Ill.
Adrn.
Code 728.107(a);
11)
For an off—site treatment facility,
a copy of the notice,
and the certification and demonstration,
if applicable,
89
required of the generator or the owner or operator under 35
Ill.
Adm. Code 728.107 or 728.108;
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.
Adm.
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.
Adm.
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.
Adm.
Code
728.107,
except for the manifest number, and the
certification and demonstration if applicable,
required
under 35
Ill. Adm.
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. Adm.
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.
Adm.
Code 728.107 or 728.108.
(Source:
Amended at 19
Ill.
Reg.
,
effective
_____________________
Section 724.177
Additional Reports
-
In addition to submitting the annual
report and unmanifested waste reports
described in Sections 724.175 and 724.176,
the owner or operator
shall also
report to the Agency:
a)
Releases,
fires4, and explosions4, as specified in Section
724.156(j);
b)
Facility closures specified in Section 724.215;
and
c)
As otherwise required by 724.Subparts
F,
K through
N,
AA4, and BB4,
and CC.
(Source:
Amended at
19
Ill.
Reg.
,
effective
_____________________
SUBPART
I:
USE AND MANAGEMENT OF CONTAINERS
Section 724.279
Air Emission Standards
The owner or operator
shall manage all hazardous waste placed
in
a container
in accordance with the requirements of 724.Subpart CC.
(Source:
Added at
19
Ill. Reg.
________,
effective
_____________________
90
SUBPART J:
TANK
SYSTEMS
Section 724.300
F023,
F026 and FO27Air Emission Standards
—
—
—
tsar.
..fl9.
r, t~‘S ~S
of this Cubpart, the following
~
~stco
F020, F021,
~S.
S.
—-i
3__1
~
~
i--..
_~__.&__.___
~
.ircd by eubpart
D,
the
ow:
•dureo for responding to
a
The owner or operator shall manage all hazardous waste placed in
a tank
in
accordance with the requirements of 724.Subpart
CC.
(Source:
Section Repealed,
new Section added at 19
Ill. Reg.
effective
______________________
SUBPART K:
SURFACE IMPOUNDMENTS
Section 724.332
Air Emission Standards
The owner or operator shall manage all hazardous waste placed in
a surface
impoundment
in accordance with the requirements
of
724.Subpart CC.
(Source:
Added at
19 Ill. Reg.
effective
SUBPART X:
MISCELLANEOUS UNITS
Section 724.701
Environmental Performance Standards
A miscellaneous unit must be
located,
designed,
constructed,
operated,
maintained4, and closed in a manner that will ensure protection of human health
and the environment.
Permits for miscellaneous units are to contain such
terms and provisions as are necessary to protect human health and the
environment,
including,
but not limited to,
as appropriate, design and
operating requirements, detection and monitoring requirements,
and
....—...‘.——
~
adequately contain spills or bake.
The design and operation of
any containment system must reflect consideration of all relevant
factors,
including:
1)
Capacity of the tank;
2)
Volumes
and
characteristics
of
wastes
stored
or
trcatcd
in
the
tank;
3)
Method
of
collection
of
spills
or
leaks;
4)
The design and construction materials of the tank and
containment system;
and
5)
The need to prevent precipitation and run—on from entering
b)
Ac part of the conti
or operator ohall
spccify ouch p
tank.
spiii or
necessary
icai~trom tno tan~tinto
to protect human health
tnc
and
contairmicn~~ystom
the environment.
as may ~c
Those
procedures must include measures for immediate removal of the
waste from the system and replacement
or repair of the leaking
91
requirements
for responses to
releases of hazardous waste or hazardous
constituents from the unit.
Permit terms and provisions must include those
requirements
of 724.Subparts
I through
0 and AA through
CC-,- and
e4—35
Ill.
Adm.
Code 702,
7034,
and
730-,- that are appropriate for the miscellaneous unit
being permitted.
Protection of human health and the environment includes, but
is
not
limited
to:
a)
Prevention of any releases that may have adverse effects on human
health or the environment due to migration of waste constituents
in the groundwater or subsurface environment, considering:
1)
The volume and physical and chemical characteristics of the
waste in the unit,
including its potential for migration
through soil,
liners4, or other containing structures;
2)
The
hydrologic
and
geologic
characteristics
of
the
unit
and
the surrounding area;
3)
The existing quality of groundwater,
including other sources
of contamination and their cumulative impact on the
groundwater;
4)
The quantity and direction of groundwater flow;
5)
The proximity to and withdrawal rates
of current and
potential groundwater users;
6)
The patterns of land use in the region;
7)
The potential for deposition or migration of waste
constituents
into
subsurface
physical
structures,
and
into
the root zone of food—chain crops and other vegetation;
8)
The potential for health risks caused by human exposure to
waste constituents;
and
9)
The potential for damage to domestic animals,
wildlife,
crops,
vegetation4,
and
physical
structures
caused
by
exposure to waste constituents.
b)
Prevention of any releases that may have adverse effects on human
health or the environment due to migration of waste constituents
in surface water,
e-rin wetlands4, or on the soil surface,
considering:
1)
The volume and physical and chemical characteristics of the
waste in the unit;
2)
The effectiveness and reliability of containing,
confining4,
and collecting systems and structures
in preventing
migration;
3)
The hydrologic characteristics of the unit and surrounding
area,
including the topography of the land around the unit;
4)
The patterns of precipitation in the region;
5)
The quantity,
quality4, and direction of groundwater flow;
6)
The proximity of the unit to surface waters;
7)
The current
and potential uses of the nearby surface waters
92
and any water quality standards in 35 Ill. Adm.
Code 302 or
303;
8)
The existing quality of surface waters and surface soils,
including other sources of contamination and their
cumulative impact on surface waters and surface soils;
9)
The patterns of
land use
in the region;
10)
The potential for health risks caused by human exposure to
waste
constituents;
and
11)
The potential for damage to domestic animals, wildlife,
crops, vegetation4, and physical structures casued by
exposure to waste constituents.
c)
Prevention of any release that may have adverse effects on human
health or the environment
due to migration of waste constituents
in the air, considering:
1)
The volume and physical and chemical characteristics of the
waste
in the unit,
including its potential for the emission
and dispersal of gases, aerosols4, and particulates;
2)
The effectiveness and reliability of systems and structures
to reduce or prevent emissions of hazardous constituents to
the
air;
3)
The operating characteristics of the unit;
4)
The atmospheric, meteorologic4, and topographic
characteristics of the unit and the surrounding area;
5)
The existing quality of the
air,
including other sources of
contamination and their cumulative impact on the air;
6)
The potential for health risks caused by human exposure to
waste
constituents;
and
7)
The potential for damage to domestic animals, wildlife,
crops,
vegetation4, and physical structures caused by waste
constituents.
(Source:
Amended
at
19
Ill.
Reg.
________,
effective
______________________-
SUBPART AA:
AIR EMISSION STANDARDS FOR PROCESS VENTS
Section
724.933
Standards:
Closed—vent
Systems
and
Control
Devices
a)
Compliance
Required.
1)
Owners
or
operators
of
closed—vent
systems
and
control
devices used to comply with provisions of this Part shall
comply with the provisions of this Section.
2)
The
owner
or
operator
of
an
existing
facility
whethat
cannot
install a closed—vent system and control device to comply
with
the
provisions
of
this
Subpart
on
the
effective
date
that the facility becomes subject to the provisions of this
Subpart
shall
prepare
an
implementation
schedule
that
includes
dates
by
which
the
closed—vent
system
and
control
93
device
will
be
installed
and
in
operation.
The
controls
must be installed as soon as possible,
but the
implementation
schedule
may
allow
up
to
18
months
after
the
effective date that the facility becomes subject to this
Subpart for installation and startup.
All units that begin
operation
after
December
21,
1990,
must
comply
with
the
rules immediately
(i.e., must have control devices installed
and operating on startup of the affected unit);
the 2—year
implementation
schedule
does
not
apply
to
these
units.
b)
A control device involving vapor recovery
(e.g.,
a condenser or
adsorber) must be designed and operated to recover the organic
vapors
vented
to
it
with
an
efficiency
of
95
weight
percent
or
greater unless the total organic emission limits of Section
724.932(a)(1)
for all affected process vents
is
attained at an
efficiency
less
than
95
weight
percent.
c)
An
enclosed
combustion
device
(e.g.,
a
vapor
incinerator,
boiler4,
or process heater) must be designed and operated to reduce the
organic emissions vented to
it by 95 weight percent or greater; to
achieve a total organic compound concentration of 20 ppmv,
expressed
as
the
sum
of
the
actual
compounds-,
and
not
j~carbon
equivalents,
on
a dry basis4, corrected to
3 percent oxygen; or to
provide a minimum residence time of 0.50 seconds at
a minimum
temperature of 760~C.
If
a boiler or process heater
is used as
the control device,
then the vent stream must be introduced into
the flame zone of the boiler or process heater.
d)
Flares:
1)
A flare must be designed for and operated with no visible
emissions4, as determined by the methods specified in
subsection
(e)(1)4, except for periods not to exceed a total
of
5 minutes during any 2 consecutive hours.
2)
A flare must be operated with a flame present
at all times,
as determined by the methods specified in subsection
(f)(2)(eC) below.
3)
A flare must be used only if the net heating value of the
gas being combusted is 11.2 MJ/scm
(300 Btu/scf)
or greater
~#and the flare
is steam—assisted or air—assisted~or
if the
net heating value of the gas being combusted
is 7.45 MJ/scm
(200 Btu/scf)
or greater
~
the flare
is nonaseisted.
The net heating value of the gas being combusted must be
determined by the methods specified
in subsection
(e)(2)
below.
4)
Exit Velocity.
A)
A steam—assisted or nonassisted flare must be designed
for and operated with an exit velocity,
as determined
by the methods
specified
in subsection
(e)(3) below,
less
than
18.3
rn/s
(60 ft/s), except as provided in
subsections
(d)(4)(B)
and
(d)(4)(C)
below.
B)
A steam-assisted or nonassisted flare designed for and
operated with an exit velocity,
as determined by the
methods specified in subsection (e)(3)
below,
equal
to
or greater than 18.3
rn/s
(60 ft/s)
but less than 122
rn/s
(400 ft/s)
is allowed
if the net heating value of
the gas being combusted
is greater than 37.3 MJ/scm
94
(1000 Btu/scf).
C)
A steam—assisted or nonassisted flare designed for and
operated with an exit velocity,
as determined by the
methods specified in subsection
(e)(3)
below,
less
than
the
velocity,
V4,
as
determined
by
the
method
specified
in
subsection
(e)(4)
below
and
less
than
122
m/s (400
ft/s)
is allowed.
5)
An air—assisted flare must be designed and operated with an
exit velocity less than the velocity,
V4, as determined by
the method specified in subsection
(e)(5) below.
6)
A flare used to comply with this Section must be steam-
-
assisted,
air—assisted4, or nonassisted.
e)
Compliance determination and equations.
1)
Reference Method
22
in 40 CFR 60, incorporated by reference
in 35
Ill. Adm. Code 720.111, must be used to determine the
compliance of a flare with the visible emission provisions
of this Subpart.
The observation period
is
2 hours and must
be used according to Method 22.
2)
The net heating value of the gas being combusted in
a flare
must be calculated using the
following equation:
H
—
K
SUH(Ci
Hi)
HT=Kx~C1xH1
Where:
HT is the net heating value of the sample
in MJ/scm;
where the net enthalpy per mole of offgas
is based on
combustion at 25~C and 760 mm Hg,
but the standard
temperature for determining the volume corrersponding
to
1 mole
is 20°C.
K
=
1.74 E —7
(1/ppm)(g mol/scm)(MJ/kcal) where
standard temperature for
(g mol/scm) 20~C.
6~M~(Xi)
means the sum of the values of
X
for each
component
i,
from
i=1
to
n.
C4~is the concentration of sample component i in ppm
on a wet basis,
as measured for organics by Reference
Method
18
in 40 CFR 60,
and for carbon monoxide,
by
ASTM
D_1946~~, incorporated
by
reference
in
35
Ill.
Adm. Code 720.111.
H4~~is the net heat of combustion of sample component
i,
kcal/gmol
at
252, C and 760 mm Hg.
The heats of
combustion must be determined using ASTM D_2382,
incorporated
by
reference
in
35
Ill.
Adm.
Code
720.111,
if published values are not available or
cannot be calculated.
95
3)
The actual exit velocity of a flare must be determined by
dividing the volumetric flow rate
(in units of standard
temperature and pressure),
as determined by Reference
Methods
2,
2A,
2C,
or 2D in
40 CFR 60,
incorporated by
reference in
35 Ill.
Adm.
Code 720.111,
as appropriate, by
the unobstructed
(free) crosB—sectional area of the flare
tip.
4)
The maximum allowed velocity in m/s, V for a flare complying
with subsection
(d)(4)(C) must be determined by the
following equation:
LOC(V)
—
(H ÷28.8)
/
31.7
H~+28
.8
1og10V~~=31.7
Where:
L~G~g~
means
logarithm to the base 10
H1
is the net heating value as determined in
subsection
(e) (2).
5)
The maximum allowed velocity in m/s, V for an air—assisted
flare must be determined by the following equation:
V=8 .706+0
.7O84xHT
V
—
~.
rut
i-
ti.
iu~4H
Where:
HT is the net heating value as determined in
subsection
(e)(2)
below.
f)
The owner or operator shall monitor and inspect each control
device required to comply with this Section to ensure proper
operation and maintenance of the control device by implementing
the following requirements:
1)
Install,
calibrate, maintain4, and operate according to the
manufacturer’s specifications
a flow indicator that provides
a record of stream flow from each affected process vent to
the control device at least once every hour.
The flow
indicator sensor must be installed in the vent stream at the
nearest
feasible
point
to
the
control
device
inlet
but
before the point at which the vent streams are combined.
2)
Install,
calibrate,
maintain4, and operate according to the
manufacturer’s specifications a device to continuously
monitor control device operation as specified below:
A)
For a thermal vapor incinerator,
a temperature
monitoring device equipped with a continuous recorder.
The device must have accuracy of +~1percent of the
temperature being monitored in
2,
C or +±0.5°C,
whichever
is
greater.
t-Ihe
temperature
sensor
must
be
96
installed
at
a location in the combustion chamber
downstream of the combustion zone.
B)
For a catalytic vapor incinerator,
a temperature
monitoring
device
equipped
with
a
continuous
recorder.
The device must be capable of monitoring temperature
at two locations and have an accuracy of +±1percent
of the temperature being monitored in
2,
C or +±O.5°C,
whichever
is greater.
One temperature sensor must be
installed
in the vent stream at the nearest feasible
point to the catalyst bed inlet and a second
temperature sensor must be installed in the vent
stream
at
the
nearest feasible point to the catalyst
bed outlet.
C)
For a flare,
a heat sensing monitoring device equipped
with a continuous recorder that indicates the
continuous ignition of the pilot
flame.
D)
For a boiler or process heater having a design heat
input capacity less than 44 MW,
a temperature
monitoring device equipped with a continuous recorder.
The device must have an accuracy of +~lpercent of the
temperature being monitored
in
2,
C or 4-±O.5°C,
whichever
is greater.
The temperature sensor must be
installed at
a location
in the furnace downstream of
the combustion
zone.
E)
For
a boiler or process heater having a design heat
input capacity greater than or equal to 44 MW,
a
monitoring device equipped with a continuous recorder
to measure
-a----parameter-fs+ that indicates good
combustion operating practices are being used.
F)
For a condenser, either:
i)
A monitoring device equipped with
a continuous
recorder
to
measure
the
concentration
level
of
the organic compounds in the exhaust vent stream
from the condenser; or
ii)
A temperature monitoring device equipped with a
continuous recorder.
The device must be capable
of monitoring temperature at two locations and
have an accuracy of +~lpercent of the
temperature being monitored in
2,
C or +±0.5°C,
whichever is greater.
One temperature sensor
must be installed at
a location
in the exhaust
vent stream from the condenser,
and
a second
temperature sensor must be installed at
a
location
in the coolant fluid exiting the
condenser.
C)
For a carbon adsorption system that regenerates the
carbon bed directly in the control device such as a
fixed—bed carbon adsorber,
either:
i)
A monitoring device equipped with a continuous
recorder to measure the concentration level of
the organic compounds
in the exhaust vent stream
from
the
carbon
bed,
or
97
ii)
A monitoring device equipped with a continuous
recorder to measure
a parameter that indicates
the carbon bed is regenerated on a regular,
predetermined time cycle.
3)
Inspect the readings
from each monitoring device required by
subsection
(f)(1) and Jfl(2) at least once each operating
day to check control device operation and,
if necessary,
immediately implement the corrective measures necessary to
ensure the control device operates
in compliance with the
requirements of this Section.
-
g)
An owner or operator using a carbon adsorption system such as
a
fixed—bed carbon adsorber that regenerates the carbon bed directly
onsite in the control device shall replace the existing carbon in
the control device with fresh carbon at
a regular, predetermined
time interval that
is no longer than the carbon service -life
established as
a requirement of
Section 724.935(b)(4) (C) (vi).
h)
An owner or operator using a carbon adsorption system such as
a
carbon canister that does not regenerate the carbon bed directly
onsite in the control device shall replace the existing carbon in
the control device with fresh carbon on
a regular basis by using
one of the following procedures:
1)
Monitor the concentration
level of the organic compounds in
the exhaust vent stream from the carbon adsorption system on
a regular schedule,
and replace the existing carbon with
fresh carbon immediately when carbon breakthrough
is
indicated.
The monitoring frequency must be daily or at an
interval no greater than 20 percent of the time required to
consume the total carbon working capacity established as a
requirement of
Section 724.935(b) (4) (C) (vii), whichever is
longer.
2)
Replace the existing carbon with fresh carbon at a regular,
predetermined
time
interval
that
is
less
than
the
design
carbon replacement interval established as
a requirement of
Section 724.935(b) (4) (CI(vii).
i)
An alternative operational or process parameter may be monitored
if the operator demonstrates that the parameter will ensure that
the control device
is operated in conformance with these standards
and the control device’s design specifications.
j)
An owner or operator of an affected facility seeking to comply
with the provisions of this Part by using
a control device other
than a thermal vapor incinerator,
catalytic vapor incinerator,
flare,
boiler,
process heater, condenser4, or carbon adsorption
system is required to develop documentation including sufficient
information to describe the control device operation and identify
the process parameter or parameters that indicate proper operation
and maintenance
of the control device.
k)
Closed vent systems.
1)
Closed-vent systems must be designed for and operated with
no detectable emissions,
as indicated by an instrument
reading
of
less
than
500
ppm
above
background
and
by
visual
inspections,
as determined by the methods specified at
Section 724.934(b).
98
2)
Closed—vent systems must be monitored to determine
compliance with this Section during the initial leak
detection
monitoring,
which
must
be
conducted
by
the
date
that the facility becomes subject to the provisions
of this
Section annually,
and at other times
as specified in the
RCRA
permit.
For the annual leak detection monitoring after
the initial leak detection monitoring, the owner or operator
is not required to monitor those closed—vent
system
components that operate in vacuum service or those closed—
vent system loints,
seams,
or other connections that are
permanently or semi—permanently sealed
(e.g.,
a welded loint
between
two
sections
of
metal
pipe or a bolted and gasketed
pipe flange~i.
3)
Detectable emissions,
as indicated by an instrument reading
greater than 500 ppm and visual
inspections, must be
controlled
as
soon
as
practicable,
but
not
later
than
15
calendar days after the emission is detected.
4)
A first attempt at repair must be made no later than
5
calendar days after the emission is detected..
1)
Closed—vent systems and control devices used to comply with
provisions of this Subpart must be operated at all times when
emissions may be vented to them.
~
The owner or operator using a carbon
adsorption system shall
document
that
all
carbon
removed
from
a
carbon
adsorption
system
to comply with subsections
(g)
and
(h) above
is managed
in one of
the following manners:
3j
It
is regenerated or reactivated
in
a thermal treatment unit
that
is permitted under 724.Subpart
X,
~j.
It is incinerated by a process that
is permitted under
724.Subpart 0,
or
~j,
It
is burned
in a boiler or industrial
furnace that is
permitted under 724.Subpart
H.
(Source:
Amended at
19
Ill.
Reg.
_______,
effective
_____________________
SUBPART BB:
AIR EMISSION STANDARDS FOR EQUIPMENT LEAKS
Section 724.963
Test Methods and Procedures
a)
Each owner or operator subject to the provisions of this Subpart
shall comply with the test methods and procedures requirements
provided in this Section.
b)
Leak detection monitoring,
as required in Sections 724.952 through
724.962, must comply with the following requirements:
1)
Monitoring must comply with Reference Method 21 in 40 CFR
60,
incorporated by reference in
35
Ill.
Adm. Code 720.111.
2)
The detection instrument must meet the performance criteria
of Reference Method 21.
3)
The instrument must be calibrated before use on each day of
its use by the procedures specified in Reference Method 21.
99
4)
Calibration gases must be:
A)
Zero air
(less than 10 ppm of hydrocarbon
in air).
B)
A mixture
of methane or n—hexane and air
at
a
concentration of
approximately, but less than 10,000
ppm methane or n—hexane.
5)
The instrument probe must be traversed around all potential
leak interfaces as close to the interface as possible as
described
in Reference Method 21.
c)
When equipment is tested for compliance with no detectable
emissions,
as required
in Sections 724.952(e),
724.953(i),
724.9544,
and 724.957(f), the test must comply with the following
requirements:
1)
The requirements of subsections
(b)(l) through
j~J,(4)
above
apply.
2)
The background level must be determined as set forth in
Reference Method 21.
3)
The instrument probe must be traversed around all potential
leak interfaces as close to the interface as possible as
described in Reference Method 21.
4)
This arithmetic difference between the maximum concentration
indicated by the instrument and the background level is
compared with 500 ppm for determining compliance.
d)
In accordance with the waste analysis plan required by Section
724.113(b),
an owner or operator of a facility shall determine,
for each piece of equipment, whether the equipment contains or
contacts a hazardous waste with organic concentration that equals
or exceeds
10 percent by weight using the
following:
1)
Methods described in ASTM Methods D 2267~, E 168-88.
E
169—87,
E 168,and E
260—85,
incorporated by reference in
35
Ill. Adm. Code 720.111;
2)
Method 9060 or 8240 of SW—846, incorporated by reference in
35
Ill. Adm. Code 720.111;
or
3)
Application of the knowledge of the nature of the hazardous
wastestream or the process by which
it was produced.
Documentation of
a waste determination by knowledge is
required.
Examples of documentation that must be used to
support a determination under this provision include
production process information documenting that no organic
compounds are used,
information that the waste
is generated
by a process that is identical to a process at the same or
another facility that has previously been demonstrated by
direct measurement to have a total organic content less than
10 percent,
or prior speciation analysis results on the same
wastestrearn where
it
is also documented that no process
changes have occurred since that analysis that could affect
the waste total organic concentration.
e)
If an owner or operator determines that a piece of equipment
contains or contacts
a hazardous waste with organic concentrations
at least
10 percent by weight,
the determination can be revised
100
only after following the procedures in subsection
(d)(l) or ,(,~j,(2)
above.
f)
When an owner or operator and the Agency do not agree on whether a
piece of equipment contains or contacts a hazardous waste with
organic concentrations at least 10 percent by weight,
the
procedures in subsection
(d)(1) or j.~I(2) above must be used to
resolve the dispute.
g)
Samples used in determining the percent organic content must be
representative of the highest total organic content hazardous
waste that
is expected to be contained in or contact the
equipment.
h)
To determine if pumps or valves are in light liquid service, the
vapor pressures of constituents must either be obtained from
standard reference texts or be determined by ASTM D—_2879—86.
incorporated by reference in 35
Ill. Adm. Code 720.111.
i)
Performance tests to determine
if
a control device achieves
95
weight percent organic emission reduction must comply with the
procedures of Section 724.934(c)(l)
through
~gj(4).
(Source:
Amended at
19
Ill.
Reg.
________,
effective
_____________________
SUBPART CC:
AIR EMISSION STANDARDS FOR TANKS,
SURFACE
IMPOUNDMENTS, AND CONTAINERS
Section 724.980
Applicability
~,
The requirements of this Subpart apply, effective December
6,
1995,
to owners and operators of all facilities that treat,
store,
or dispose of hazardous waste in tanks,
surface impoundments,
or
containers
sub-iect to 724.Subparts
I,
3, or K, except as Section
724.101 and subsection
(b) below provide otherwise.
BOARD NOTE:
U.S. EPA adopted these regulations
at 59 Fed.
Req.
62896
(Dec.
6,
1994), effective June
6,
1995.
At 60 Fed. Rea~
26828 (May
19,
1995),
U.S. EPA delayed the effective date until
December
6,
1995.
If action by U.S. EPA or a decision of a
federal court changes the effectiveness of these regulations, the
Board does not intend that the 724.Subpart CC rules be enforceable
to the extent that they become more stringent that the federal
regulations upon which they are based.
~j.
The requirements of this Subpart do not apply to the following
waste management units
at the facility:
fl,
A waste management unit that holds hazardous waste placed in
the unit before December
6,
1995,
and in which no hazardous
waste is
added to the unit on or after this date.
21
A container that has a design capacity less than or equal to
0.1
m3
(3.5
ft3 or 26.4 gal).
~j,
A tank in which
an owner or operator has stopped adding
hazardous waste and the owner or operator has begun
implementing
or completed closure pursuant to an approved
closure plan.
j~
A surface impoundment
in which an owner or operator has
101
stopped adding hazardous waste
(except to implement an
approved
closure
plan)
and
the
owner
or
operator
has
begun
implementing or completed closure pursuant to an approved
closure plan.
~,1
A
waste
management
unit
that
is
used
solely
for
on—site
treatment
or
storage
of
hazardous
waste
that
is
generated
as
the
result
of
implementing
remedial
activities
required
pursuant
to
the
Act
or
Board
regulations
or
under
the
corrective
action
authorities
of
RCRA
sections
3004(u).,
3004(v)
or
3008(h);
CERCLA
authorities;
or
similar
federal
or
state
authorities.
~,1
A
waste
management
unit
that
is
used
solely
for
the
management
of
radioactive
mixed
waste
in
accordance
with
all
applicable
regulations
under
the
authority
of
the
Atomic
Energy
Act
(42
U.S.C.
2011
et
seq.)
and
the
Nuclear
Waste
Policy
Act.
~j.
For
the
owner
and
operator
of
a
facility
subject
to
this
Subpart
and
who
received
a
final
RCRA
permit
prior
to
December
6,
1995,
the
reguirements
of
this
Subpart
shall
be
incorporated
into
the
permit
when
the
permit
is
reissued,
renewed,
or
modified
in
accordance
with
the
requirements
of
35
Ill.
Adm.
Code
703
and
705.
Until
such
date
when
the
owner
and
operator
receives
a
final
permit incorporating the requirements
of this Subpart, the owner
and operator is
sub-ject to the requirements of 35 Ill.
Adm.
Code
725.Subpart
CC.
(Source:
Added at 19
Ill. Reg.
________,
effective
_____________________
Section
724.981
Definitions
As used in this Subpart,
all terms shall have the meaning given to them in
35
Ill.
Adm. Code 725.981,
RCRA,
and
35
Ill.
Adm.
Code 720.110.
(Source:
Added at 19
Ill.
Reg.
________,
effective
_____________________
Section
724.982
Standards:
General
~J,
This Section
applies
to
the
management
of
hazardous
waste
in
tanks,
surface impoundments,
and containers
sub-~iectto this
Subpart.
~
The owner or operator shall control air emissions from each waste
management unit
in accordance with standards specified in Section
724.984 through 724.987,
as applicable to the waste management
unit,
except
as provided for in subsection
(c)
below.
~j,
A waste management unit
is exempted from standards specified in
Sections_724.984 through 724.987, provided that all
hazardous
waste placed
in the waste management unit
is determined by the
owner or operator to meet either of the following conditions:
fl..
The average VO concentration of the hazardous waste
at the
point of waste origination is less than 100 parts ~er
million by weight
(ppmw).
The averaQe VO concentration
shall be determined by the procedures specified in Section
724.983(a).
~J,
The
organic content of the hazardous waste has been reduced
by an organic destruction or removal process that achieves
102
any one of the following conditions:
~j,
The process removes or destroys the organics contained
in the hazardous waste to
a level such that the
average VO concentration of the hazardous waste at the
point
of waste treatment
is less than the exit
concentration limit
(C.) established
for the process.
The average VO concentration of the hazardous waste at
the point
of waste treatment and the exit
concentration
limit
for
the
process
shall
be
determined using the procedures specified
in Section
724.983(b).
~j,
The process removes or destroys the organics contained
in the hazardous waste to
a level such that the
organic reduction efficiency
(R)
for the process
is
equal to or greater than 95 percent,
and the average
VO
concentration
of
the
hazardous
waste
at
the
point
of
waste
treatment
is
less
than
50
ppmw.
The
organic
reduction
efficiency
for
the
process
and
the
average
VO
concentration
of
the
hazardous
waste
at
the
point
of
waste
treatment
shall
be
determined
using
the
procedures
specified
in
Section
724.983(b).
~J
The
process
removes
or
destroys
the
organics
contained
in
the
hazardous
waste
to
a
level
such
that
the
actual
organic
mass
removal’
rate
(MR)
for
the
process
is
greater
than
the
required
organic
mass
removal
rate
(RMR)
established
for
the
process.
The
required
organic mass removal rate and the actual organic mass
removal
rate
for
the
process
shall
be
determined
using
the procedures
specified in Section 724.983(b).
Q,).
The
process
is
a
biological
process
that
destroys
or
degrades
the
organics
contained
in
the
hazardous
waste-,- so that either of the following conditions
is
-
met:
jj,
The organic reduction efficiency
(R)
for the
process
is equal to or greater than
95 percent,
and_the_organic
biodegradation
efficiency
(R~,1
for
the
process
is
equal
to
or
greater
than
95
percent.
The organic reduction efficiency and
the organic biodegradation efficiency for the
process shall be determined in accordance with
the procedures specified in Section 724.983(b).
jj,1
The total actual organic mass biodegradation
rate
(MRbI~) for
all
hazardous
waste
treated
by
the process
is equal to or greater than the
required organic mass removal rate
(RMR).
The
required organic mass removal rate and the
actual organic mass biodegradation rate for the
process shall be determined using the procedures
specified
in Section 724.983(b).
~,1
The process removes or destroys the organics contained
in the hazardous waste and meets all of the following
conditions:
jj
All of the materials entering the process are
hazardous wastes.
103
~JJ.
From the
point of waste origination through the
point where the hazardous waste enters the
process,
the hazardous waste is continuously
managed
in waste management units which use air
emissioncontrols
in accordance with the
standards specified in Sections 724.984 through
724.987,
as applicable to the waste management
unit.
iii)
The average VO concentration of the hazardous
waste at the point of waste treatment is less
than the lowest average VO concentration at the
point of waste origination,
determined for each
of the individual
hazardous
waste
streams
entering the process,
or 100 ppmw, whichever
value
is lower.
The average VO concentration of
each individual hazardous waste stream at the
point of waste origination shall
be determined
using_the procedure specified
in Section
724.983(a).
The average VO concentration of the
hazardous waste
at the point of waste treatment
shall be determined using the procedure
specified
in Section 724.983(b).
fi
A hazardous waste incinerator for which the owner or
operator has either:
j),
Been issued a final permit under
35
Ill.
Adm.
Code 703
and 705, and designs
and operates the
unit in accordance with the requirements of
724.Subpart
0; or
j~
Has certified compliance with the interim status
requirements of
35
Ill.
Adm. Code 725.Subpart 0.
~j.
A boiler or
industrial furnace for which the owner or
operator has either:
fl,
Been issued a final permit under 35
Ill.
Adm.
Code 703 and 705,
and designs
and operates the
unit in accordance with the requirements of 35
Ill. Adm.
Code 726.Subpart H;
or
jj,1
Has certified compliance with the interim status
requirements of
35 Ill.
Adm. Code 726.Subpart H.
~J
When a
process
is used for the purpose of treating a hazardous
waste to meet one of the sets of conditions specified in
subsections
(c)(2)(A) through
(c)(2)(E)
above, each material
removed from or exiting the process that
is
not a hazardous waste
but which has an average VO concentration equal to or greater than
100 p~mwshall be managed in a waste management unit in accordance
with the requirements of subsection
(b)
above.
~,1
The Agency may at any time perform or request that the owner or
operator_perform
a waste determination for a hazardous waste
managed in a tank,
surface impoundment,
or container that
is
exempted from using air emission controls under the provisions of
this Section as follows:
fl.
The
waste determination for average VO concentration of
a
hazardous waste at the point of waste origination shall be
104
performed using direct measurement
in accordance with the
applicable requirements of Section
724.983(a).
The waste
determination for a hazardous waste at the point of waste
treatment shall be performed in accordance with the
applicable requirements of Section
724.983(b).
2.1
Where
the owner or operator is requested to perform the
waste determination, the Agency may elect to have an
authorized representative observe the collection of the
hazardous waste samples used for the analysis.
~J,
Where the results of the waste determination performed or
requested by the Agency do
not agree with the results of
a
waste determination performed by the owner or operator using
knowledge of the waste, then the results of the waste
determination performed in accordance with the requirements
of subsection
(e)(1)
above shall be used to establish
compliance with the requirements of this Subpart.
j)
Where the owner or operator has used an averaging period
greater than one hour for determining the average VO
concentration of a hazardous waste at the point of waste
origination,
the Agency may elect to establish compliance
with this Subpart by performing or requesting that the owner
or operator perform a waste determination using direct
measurement based on waste samples collected within a one—
hour period
as
follows:
~
The average VO concentration of the hazardous waste at
the point of waste origination shall be determined by
direct measurement in accordance with the requirements
of Section 724.983(a).
~
Results of the waste determination
performed or
requested by the Agency showing that the average VO
concentration of the hazardous waste at the point of
waste origination is equal to or greater than 100 p~mw
shall constitute noncompliance with this Subpart.
except
in
a case
as provided
for in subsection
(e)(4UC) below.
Qj,
Where the average VO concentration of the hazardous
waste at the point of waste origination previously has
been determined by the owner or operator using an
averaging period greater than one hour to be less than
100 ppmw but because of normal operating process
variations the VO concentration
of the hazardous waste
determined by direct measurement for any given one—
hour period may be equal to or greater than 100
ppmw,
information that was used by the owner or operator to
determine the average VO concentration of the
hazardous waste (e.g., test results, measurements,
calculations,
and other documentation)
and recorded in
the facility records
in accordance with the
requirements of Section 724.983(a)
and Section 724.989
shall be considered by the Agency together with the
results of the waste determination performed or
requested by the Agency
in establishing compliance
with this Subpart.
(Source:
Added at
19
Ill.
Reg.
________,
effective
______________________
105
Section 724.983
Waste Determination Procedures
~j,
Waste determination procedure for average volatile organic
(VO)
concentration of
a hazardous waste at the point of waste
origination.
fl
An owner or operator shall determine the average VO
concentration
at the point of waste origination for each
hazardous waste placed in waste management units exempted
under the provisions of Section 724.982(c)(U
from using air
emission controls
in accordance with standards specified in
Section 724.984 through Section 724.987,
as applicable to
the waste management unit.
2,),
The VO concentration at the point of waste origination for a
hazardous_waste shall be determined
in accordance with the
procedures specified
in 35
Ill.
Adm.
Code 725.984(a) (2)
through
(a)(6).
Waste determination procedures
for treated hazardous waste.
fl
An owner or operator shall perform the applicable waste
determinations
for each treated hazardous waste placed in
waste management units exempted under the provisions of
Section 724.982(c) (2)
from using air emission controls in
accordance with standards specified in Section 724.984
through 724.987,
as
applicable to the waste management unit.
21
The waste determination for
a treated hazardous waste
shall
be performed
in accordance with the procedures specified in
35
Ill.
Adm.
Code 725.984(b) (2) through
(b)(10),
as
applicable to the treated hazardous waste.
g,1
Procedure to determine the maximum organic vapor pressure of a
hazardous waste
in
a tank.
fl
An owner or operator shall determine the maximum organic
vapor pressure for each hazardous waste placed in tanks
using air emission controls
in accordance with standards
specified in Section 724.984(c).
21
The maximum organic vapor pressure of the hazardous waste
shall be determined
in accordance with the procedures
specified in 35
Ill.
Adm. Code 725.984(c) (2) through
(c)(4).
(Source:
Added at
19 Ill. Reg.
________,
effective
_____________________
Section 724.984
Standards:
Tanks
~j
This Section applies to owners and operators of tanks sublect to
this Subpart into which any hazardous waste
is placed, except for
the following tanks:
fl..
A tank
in which all hazardous waste entering the tank meets
the conditions specified in Section 724.982(c),
or
21
A tank used for biological treatment of hazardous waste in
accordance with the requirements of Section
724.982(c)(2) (D).
~j
The owner or operator shall place the hazardous waste into one of
the following tanks:
106
fl.
A
tank
equipped
with
a
cover
(e.g.,
a
fixed
roof)
that
is
vented
through
a
closed—vent system to
a control device in
accordance
with
the
requirements
specified
in
subsection
(d)
below
21
A
tank
equipped
with
a
fixed
roof
and
internal
floating
roof
in
accordance
with
the
requirements
of
Section
724.991
~j,
A
tank
equipped
with
an
external
floating
roof
in
accordance
with
the
requirements
of
Section
724.991;
or
ii
A
pressure
tank
that
is
designed
to
operate
as
a
closed
system
such
that
the
tank
operates
with
no
detectable
organic
emissions
at
all
times
that
hazardous
waste
is
in
the
tank
except
as
provided
for
in
subsection
(p)
below.
~J
As
an
alternative
to
complying
with
subsection
(b)
above,
an
owner
or
operator
may
place
hazardous
waste
in
a
tank
equipped
with
a
cover
(e.g.,
a
fixed
roof) meeting the requirements specified
in
subsection
(d)(1)
below
when
the hazardous waste
is determined to
meet
all
of
the following conditions:
fl
The hazardous waste
is not mixed,
stirred,
agitated,
or
circulated within the tank by the owner or operator using
a
process
that
results
in
splashing,
frothing,
or
visible
turbulent flow on the waste surface during normal
process
operations
21
The hazardous waste in the tank is not heated by the owner
or operator except during conditions requiring that the
waste
be heated to prevent the waste from freezing or to
maintain
adequate
waste
flow
conditions
for
continuing
normal process
operations
21
The hazardous waste
in the tank is
not treated by the owner
or operator using a waste stabilization process or
a process
that produces an exothermic reaction; and
4,).
The maximum organic vapor pressure of the hazardous waste in
the_tank,_as determined using the procedure specified
in
Section 724.983(c),
is
less than the following applicable
value:
~j
If the tank design capacity is equal to or greater
than 151
m3
(5333
ft3 or 39,887 gal),
then the maximum
organic vapor pressure shall be less than 5.2 kPa
(0.75 psia or 39 mm Hg)
~).
If
the tank design capacity
is equal to or greater
than 75
m3
(2649
ft3 or 19,810 gal) but less than 151
in3
(5333
ft3 or 39,887 gal),
then the maximum organic
vapor
pressure shall be
less than 27.6 kPa
(4.0 psia
or 207
mm
Hg);
or
~,1
If the tank design capacity
is less than 75
m3
(2649
ft3
or 19,810 gal),
then the maximum organic vapor
pressure shall be less than 76.6 kPa
(11.1 psia or 574
mm_Hg).
~J
To comply with subsection
(b)(1)
above,
the owner or operator
shall
design,
install,
operate,
and
maintain
a
cover
that
vents
the organic vapors emitted from hazardous waste in the tank
107
through
a closed—vent system connected to
a control device.
jj
The cover
shall be designed and operated to meet the
following requirements:
~
The cover and all cover openings
(e.g., access
hatches,
sampling ports,
and gauge wells)
shall be
designed to operate with no detectable organic
emissions when all cover openings
are secured in
a
closed,
sealed position;
and
flj
Each cover opening shall be secured
in
a closed,
sealed position
(e.g., covered by
a qasketed lid or
cap)
at all times that hazardous waste is in the tank
except
as provided for in
subsection
(f)
below.
2.1
The closed—vent system and control device shall be designed
and operated in accordance with the requirements of Section
724. 987.
~J
The owner and operator shall install,
operate,
and maintain
enclosed pipes or other closed—systems to:
il
gj~
One or more safety devices that vent directly to the atmosphere
may be used on the tank
cover,
closed—vent system,
or control
device provided each safety device meets all
of the following
conditions:
~j-
The safety device is not used for planned or routine venting
of organic vaporB
from the tank or closed—vent system
connected to
a control device;
and
I-
BOARD NOTE:
U.S. EPA considers a drain system that meets the
requirements of 40 CFR 61.346(aUl)
or
(b)(l) through (b)(3) to be
a
“closed—system”.
The Board intends that this meaning be
included in the use of that term for the purposes of this Subpart.
fl
Transfer all hazardous waste to the tank from another tank,
surface impoundment, or container subject to this Subpart
except
for those hazardous wastes that meet the conditions
specified in Section 724.982(c);
and
21
Transfer all hazardous waste from the tank to another tank,
surface impoundment, or container subject to this Subpart
except
for those hazardous wastes that meet the conditions
specified in Section 724.982(c).
Each cover opening shall be secured
in
a closed,
sealed position
(e.g.,
covered by a gasketed
lid)
at
all times that hazardous
waste
is
in the tank except when it
is necessary to use the cover
opening to:
jj.
Add,
remove,
inspect,
or sample the material
in the tank;
21
Inspect, maintain,
repair,
or replace equipment located
inside the tank;
or
~j
Vent gases or vapors from the tank to
a closed—vent system
connected to
a control device that
is designed and operated
in accordance with the requirements of Section 724.987.
21
The safety device remains
in
a closed,
sealed position at
108
all times,
except when
an unplanned event requires that the
device open for the purpose of preventing physical damage or
permanent deformation of the tank,
cover,
closed—vent
system,
or control device in accordance with good
engineering and safety practices for handling flammable,
combustible, explosive,
or other hazardous materials.
An
example of an unplanned event is a sudden power outage.
(Source:
Added
at
19
Ill.
Reg.
effective
______________________
Section 724.985
Standards:
Surface Impoundments
~j
This Section applies to owners and operators of surface
impoundments subject to this Subpart into which any hazardous
waste is placed except
for the following surface impoundments:
fl
A surface impoundment
in which
all hazardous waste entering
the surface impoundment meets the conditions specified in
Section 724.982(c);
or
21
A surface impoundment used for biological treatment of
hazardous waste in accordance with the requirements of
Section 724.982(c)(2)(D).
~j
The owner or operator shall place the hazardous waste into a
surface impoundment equipped with a cover (e.g.,
an air—supported
structure or
a rigid cover)
that
is vented through
a closed—vent
system to
a control device meeting the requirements
specified in
subsection
(d) below.
~J
As an alternative to complying with subsection
(b)
above,
an owner
or operator may place hazardous waste in a surface
impoundment
equipped with
a floating membrane cover meeting the requirements
specified in subsection
(e)
below when the hazardous waste is
determined to meet all of the following conditions:
fl
The hazardous waste
is not mixed,
stirred,
agitated,
or
circulated within the surface impoundment by the owner or
operator using a process that results in splashing,
frothing,
or visible turbulent flow on the waste surface
during normal process operations
21
The hazardous waste
in the surface impoundment
is not heated
by the owner or operator;
and
~j
The hazardous waste
is not treated by the owner or operator
using a waste stabilization process or
a process that
produces an exothermic reaction.
~j
To comply with subsection
(b)(l) above,
the owner or operator
shall design,
install,
operate, and maintain
a cover that vents
the organic vapors emitted from hazardous waste in the surface
impoundment through
a closed—vent system connected to
a control
device.
fl
The cover shall be designed and operated to meet the
following requirements:
~j
The cover and all cover openings
(e.g.,
access
hatches,
sampling ports,
and gauge wells)
shall be
designed to operate with no detectable organic
emissions when all cover openings are secured
in
a
109
closed,
sealed position
~j
Each cover opening shall be secured
in the closed,
sealed position (e.g., covered by a gasketed lid or
cap)
at all times that hazardous waste
is
in the
surface impoundment,
except as provided for in
subsection
(g)
below; and
~
The closed—vent system and control device shall be
designed and operated
in accordance with Section
724. 987.
~
To comply with subsection
(c)
above, the owner or operator
shall
design,
install,
operate,
and maintain
a floating membrane cover
that meets all of the requirements specified in
35 Ill.
Adxn.
Code
725.986(e)(1) through
(e)(4).
LI
The owner or operator shall install, operate,
and maintain
enclosed pipes or other closed-systems to:
BOARD NOTE:
U.S. EPA considers
a drain system that meets the
requirements of 40 CFR 6l.346(a)(l) or
(b)(1) through (b)(3) to be
a “closed—system”.
The Board intends that this meaning be
included in the use of that term for the purposes of this Subpart.
fl
Transfer all hazardous waste to the surface impoundment from
another tank,
surface impoundment,
or container subject to
this Subpart except
for those hazardous wastes that meet the
conditions specified
in Section 724.982(c);
and
21
Transfer all hazardous waste from the surface impoundment to
another tank,
surface impoundment,
or container
subject to
this Subpart except
for those hazardous wastes that meet the
conditions specified
in Section 724.982(c).
g~
Each cover opening shall be secured
in the closed,
sealed position
(e.g.,
a cover by
a gasketed
lid or
cap)
at all times that
hazardous waste
is
in the surface impoundment except when it
is
necessary to use the cover opening to:
fl
Add,
remove,
inspect,
or sample the material in the surface
impoundment
21
Inspect,
maintain,
repair,
or
replace equipment
located
underneath the cover
~J
Remove treatment residues from the surface impoundment
in
accordance with the requirements of
35
Ill.
Adm. Code 728.4
or
jJ
Vent gases or vapors from the surface impoundment to a
closed—vent
system connected to
a control device that
is
designed and operated
in accordance with the requirements of
Section 724.987.
~j
One or more safety devices that vent directly to the atmosphere
may be installed on the cover,
closed—vent
system,
or control
device provided each device meets all of the following conditions:
fl
The safety device
is not used for planned or routine venting
of organic vapors from the surface impoundment or the
closed—vent system connected to
a control device;
and
110
21
The safety device remains
in a closed,
sealed position
at
all times,
except when an unplanned event requires that the
device open for the purpose of preventing physical damage or
permanent deformation of the cover,
closed—vent system,
or
control device in accordance with good engineering and
safety practices for handling flammable, combustible,
explosive,
or other hazardous materials.
An example of an
unplanned event
is a sudden power outage.
(Source:
Added at
19
Ill.
Reg.
________,
effective
______________________
Section 724.986
Standards:
Containers
~j
This Section applies to the owners and operators of containers
having design capacities greater than 0.1
m3
(3.5 ft3 or 26.4 gal)
subject to this Subpart into which any hazardous waste is
placed
except_for_a container in which all hazardous waste entering the
container meets the conditions specified in Section 724.9B2~c).
~j
An owner or operator shall manage hazardous waste
in
containers
using the
following procedures:
fl
The owner or operator shall place the hazardous waste into
one of the following containers, except when a container
is
used for hazardous waste treatment
as required by subsection
(bU2) below:
A container that
is equipped with
a cover which
oPerates with no detectable organic emissions when all
container openings
(e.g.,
lids,
things,
hatches,
and
sampling ports)
are secured
in a closed,
sealed
position.
The owner or operator shall determine that
a container operates with no detectable emissions by
testing each opening on the container for leaks
in
accordance with Method 21 in
40 CFR
60,
Appendix
A,
incorporated by reference
in
35
Ill.
Adm. Code
720.111,
the first time any portion of the hazardous
waste
is placed into the container.
If
a leak
is
detected and cannot be repaired immediately, the
hazardous waste shall be removed from the container
and the container not used to meet the requirements of
this subsection until the leak is repaired and the
container
is retested.
~1
A container having a design capacity less than or
equal to 0.46
m
(16.2
ft
or 122 gal) that is equipped
with a cover and complies with all applicable
Department of Transportation regulations on packaging
hazardous waste for transport under 49
CFR 178,
incorporated by reference at
35
Ill.
Adm.
Code
720.111.
jj
A container that
is managed in accordance with
the requirements of 49 CFR 178,
incorporated by
reference at
35 Ill. Adm. Code 720.111,
for the
purpose of complying with this Subpart,
is not
subject to any exceptions to the 49 CFR 178
regulations, except
as noted
in
subsection
(b)(1) (B) (ii)
below.
~jJj
A lab pack that
is managed in accordance with
the requirements of
49 CFR 178,
incorporated by
111
reference at
35
Ill. Adm.
Code 720.111,
for the
purpose of complying with this Subpart, may
comply with the exceptions
for combination
packagings specified
in
49 CFR 173.12(b),
incorporated by reference at
35
Ill.
Adin.
Code
720.111.
Qj.
A container that
is attached to or forms
a part of any
truck, trailer,
or railcar and that has been
demonstrated within the preceding
12 months to be
organic vapor tight when all container openings
are in
a closed,
sealed position
(e.g., the container hatches
or lids are gasketed and latched).
For the purpose of
meeting the requirements of this subsection,
a
container is organic vapor tight
if the container
sustains
a pressure change of not more than 0.75 kPa
(0.11 psig or 5.6 mm Hg)
within
5 minutes after
it is
pressurized to
a minimum of
4.50 kPa
(0.65 psig or
33.7 mm Hg).
This condition
is to be demonstrated
using the pressure test specified in Method 27
of 40
CFR 60, Appendix A,
and a pressure measurement device
which has a precision of ±2.5nun water and which
is
capable of measuring above the pressure at which the
container
is to be tested
for vapor tightness.
21
An owner or operator treating hazardous waste in a container
by either
a waste stabilization process,
any process that
requires the addition of heat to the waste,
or any process
that produces an exothermic reaction shall meet the
following requirements:
~j
Whenever
it
is necessary for the container to be open
during the treatment process, the container shall be
located inside an enclosure that
is vented through
a
closed—vent
system to
a control device.
~j
The enclosure shall be
a structure that
is designed
and operated in accordance with the following
requirements:
j~
The enclosure shall be
a structure that is
designed and operated with sufficient airflow
into the structure to capture the organic vapors
emitted_from the hazardous waste
in the
container and vent the vapors through the
closed—vent system to the control device.
jjj
The enclosure may have permanent or temporary
openings to allow worker access,
passage of
containers through the enclosure by conveyor or
other mechanical means,
entry
of permanent
mechanical or electrical equipment,
or to direct
airflow into the enclosure.
The pressure drop
across each opening in the enclosure shall be
maintained at a pressure below atmospheric
pressure so that whenever an open container
is
placed inside the enclosure no organic vapors
released from the container exit the enclosure
through the opening.
The owner or operator
shall determine that an enclosure achieves this
condition by measuring the pressure drop across
each opening
in the enclosure.
If the pressure
112
within the enclosure
is equal to or greater than
atmospheric pressure then the enclosure does not
meet the requirements of this Section.
~j
The closed—vent system and control device shall be
designed and operated in accordance with the
requirements of Section 724.987.
~j
An owner or operator transferring hazardous waste into a
container having a design capacity greater than 0.46
m3
(16.2
ft3 or 122 gal)
shall meet the following requirements:
~
Hazardous waste transfer by pumping shall be performed
using a conveyance system that uses
a tube
(e.g.,
ripe, hose)
to add the waste into the container.
During transfer of the waste into the container,
the
cover shall remain
in place and all container openings
shall be maintained
in a closed,
sealed position
except
for those openings through which the tube
enters the container and as provided for in subsection
(c) below.
The tube shall be positioned in
a manner
so that:
ii
The tube outlet continuously remains submerged
below the waste surface at all times waste is
flowing through the tube
£jj
The lower bottom edge of the tube outlet
is
located
at a distance no greater than two inside
diameters of the tube or 15.25 cm
(6.0 in),
whichever distance is greater,
from the bottom
of the container
at all times waste is
flowing
through the tube;
or
iii)
The tube is
connected to a permanent port
mounted on the bottom of the container so that
the lower edge of the port opening inside the
container
is located at a distance egual to or
less than 15.25 cm
(6.0 in)
from the container
bottom.
~j
Hazardous waste transferred by a means other than
pumping shall be performed such that during transfer
of the waste into the container,
the cover remains
in
place and
all container openings are maintained
in
a
closed,
sealed position except for those openings
through which the hazardous waste is added and
as
provided for in subsection
(d) below.
~gJ
Each container opening shall be maintained in a closed,
sealed
position
(e.g., covered by a gasketed lid) at all times that
hazardous waste
is
in the container except when
it is necessary to
use the opening to:
fl
Add,
remove,
inspect,
or sample the material
in the
container
21
Inspect,
maintain,
repair,
or replace equipment located
inside the container;
or
~j
Vent gases or vapors from a cover located over or enclosing
an open container to
a closed—vent system connected to a
113
control device that
is designed and operated in accordance
with the requirements of Section 724.987.
~
One or more safety devices that vent directly to the atmosphere
may be used on the container,
cover,
enclosure, closed—vent
system,
or control device provided each device meets
all of the
following conditions:
jj~.
The safety device
is not used for planned or routine venting
of organic vapors
from the container,
cover,
enclosure,
or
closed—vent system connected to a control device;
and
21
The safety device remains in
a closed,
sealed position at
all times except when an unplanned event requires that the
device open for the purpose of preventing physical damage or
permanent deformation of the container,
cover,
enclosure,
closed-vent system, or control device in accordance with
good engineering and safety practices for handling
flammable,
combustible, explosive, or other hazardous
materials.
An example of an unplanned event
is a sudden
power outage.
(Source:
Added at
19
Ill. Reg.
effective
______________________
Section 724.987
Standards:
Closed—vent Systems and Control Devices
~j
This Section applies to each closed—vent system and control device
installed and operated by the owner or operator to control air
emissions in accordance with standards of this Subpart.
~j.
The closed—vent system shall meet the following reguirements:
~.
The closed—vent
system shall route the gases,
vapors, and
fumes emitted from the hazardous waste in the waste
management unit to a control device that meets the
requirements specified in subsection
(C)
below.
21
The closed—vent system shall be designed and operated in
accordance with the requirements specified in Section
724.933(k).
~j
If the closed—vent
system contains one or more bypass
devices that could be used to divert all or a portion of the
gases,
vapors,
or fumes from entering the control device,
the owner or operator
shall meet the following requirements:
~j
For each bypass device,
except as provided for
in
subsection
(b)(3)(B)
below, the owner or operator
shall either:
J~j
Install,
calibrate, maintain,
and operate a flow
indicator at the inlet to the bypass device that
indicates at
least once every
15 minutes whether
gas,
vapor,
or fume flow is present
in the
bypass device; or
jj1
Secure
a valve installed
at the inlet to the
bypass device in the closed position using a
car—seal or a lock—and—key type configuration.
The owner or operator shall visually inspect the
seal or closure mechanism at least once every
month to verify that the valve is maintained in
114
the closed position.
~J
Low leg drains, high point bleeds, analyzer vents,
open—ended valves or lines,
and safety devices are not
subject to the requirements of subsection (b)(3)(A)
above.
~
The control device shall meet the following requirements:
fl
The control device shall be one of the following devices:
~J
A control device designed and operated to reduce the
total organic content of the inlet vapor stream vented
to the control device by at least
95 percent by
weight
~
An enclosed combustion device designed and operated in
accordance with the requirements of Section
724.933(c); or
çj
A flare designed and operated in accordance with the
requirements of Section 724.933(d).
21
The control device shall be operating at all times when
eases,
vapors, or fumes are vented from the waste management
unit through the closed—vent system to the control device.
~J
The owner or operator using a carbon adsorption system to
comply with subsection
(c)(l)
above shall operate and
maintain the control device in accordance with the followina
requirements:
~
Following the initial startup of the control device,
all activated carbon in the control device shall be
replaced with fresh carbon on a regular basis in
accordance with the requirements of Section 724.933(g)
or Section 724.933(h).
~
All carbon removed from the control device shall be
managed
in accordance with the requirements of Section
724.933(m).
j)
An owner or operator using a control device other than a
thermal vapor incinerator,
flare,
boiler, process heater,
condenser, or carbon adsorption system to comply with
subsection
(c)(1)
above shall operate and maintain the
control device in accordance with the requirements of
Section 724.933(j).
~j
The owner or operator shall demonstrate that
a control
device achieves the performance requirements of subsection
(c)(1)
above,
as follows:
ai.
An owner or operator shall demonstrate using either a
performance test,
as specified in subsection (c)(5)(C)
below, or
a design analysis,
as specified
in
subsection (c)(SUD)
below, the performance of each
control device except for the following:
fl
A flare
jjJ
A boiler or process heater with a design heat
115
input capacity of
44 megawatts
or greater;
iii)
A boiler or process heater into which the vent
stream
is introduced with the primary fuel
jy~.
A boiler or process heater burning hazardous
waste for which the owner or operator has been
issued
a final permit under 35
Ill.
Adm.
Code
703 and 705 and designs and operates the unit in
accordance with the requirements of 35
Ill. Adm.
Code 726.Subpart H;
or
~J
A boiler or process heater burning hazardous
waste for which the owner or operator has
certified compliance with the interim status
requirements of 35 Ill.
Adm. Code 726.Subpart H.
flj..
An owner or operator shall demonstrate the performance
of each flare
in accordance with the requirements
specified in Section 724.933(e).
.ç~j
For
a performance test conducted to meet the
requirements of subsection
(c)(5)(A)
above, the owner
or operator shall use the test methods and procedures
specified in Section 724.934(c)(1)
through
(c)(4).
P1
For
a design analysis conducted to meet the
requirements of subsection
(c)(5)(A)
above, the design
analysis shall meet the requirements specified
in
Section 724.935(b)(4)(C).
~J..
The owner or operator shall demonstrate that a carbon
adsorption system achieves the performance
requirements of subsection
(c)(l)
above based on the
total_quantity of organics vented to the atmosphere
from all
carbon adsorption system equipment that
is
used for organic adsorption,
organic desorption or
carbon regeneration,
organic recovery,
and carbon
disposal.
~
If the owner or oPerator and the Agency do not agree on
a
demonstration of control device performance using a design
analysis then the disagreement shall be resolved using the
results of
a performance test performed by the owner or
operator in accordance with the requirements of subsection
(c)(5)(C)
above.
The Agency may choose to have an
authorized representative observe the performance test.
(Source:
Added
at
19
Ill. Reg.
________,
effective
______________________
Section 724.988
Inspection and Monitoring Requirements
~j
This Section applies
to an owner or operator using air emission
controls in accordance with the requirements of Sections 724.984
through 724.987.
~j..
Each cover used in accordance with requirements
of Section 724.984
through 724.986 shall be visually inspected and monitored for
detectable oraanic emissionE by the owner or operator using the
procedure specified in 35
Ill. Adm. Code 725.989(f(1)
through
(f)(7),
except as follows:
116
~
An owner or operator is exempted from performing the cover
inspection and monitoring requirements
specified in 35
Ill.
Adrn. Code 725.989(f)(l)
through
(f)(7)
for the
following
tank covers:
~j
A tank internal floating roof that
is inspected and
monitored
in accordance with the requirements of
Section 724.991; or
-
~j
A tank external
floating roof that
is inspected and
monitored in accordance with the requirements of
Section 724.991.
21
If a tank is buried partially or entirely underground,
an
owner or operator
is required to perform the cover
inspection and monitoring requirements specified in
35
Ill.
Adm.
Code 725.989(f)(l)
through
(f)(7) only for those
portions of the tank cover and those connections to the tank
cover or tank body
(e.g.,
fill ports,
access hatches, gauge
wells, etc.)
that extend to or above the ground surface and
can be opened to the atmosphere.
~J.
An owner or operator is exempted from performing the cover
inspection and monitoring requirements specified in 35
111.
Adni.
Code 725.989(f)(l)
through
(f)(7)
for
a container that
meets all requirements specified in either Section
724.986(b)(1)(B) or
(b)(1)(C).
LL
An owner or operator is exempted from performing the cover
inspection and monitoring requirements specified in 35
Ill.
Adm.
Code 725.989(f)(l)
through
(f)(7)
for an enclosure used
to control air emissions from containers
in accordance with
the requirements of Section 724.986(b) (2).
~
Each closed—vent system used in accordance with the requirements
of Section 724.987 shall be inspected and monitored by the owner
or operator
in accordance with the procedure specified
in Section
724.933(k).
~,j
Each control device used
in accordance with the requirements of
Section 724.987 shall be inspected and monitored by the owner or
operator in accordance with the procedures specified
in Sections
724.933(f)
and 724.933(i).
~j
The owner or operator shall develop and implement
a written plan
and schedule to perform all inspection and monitoring requirements
of this section.
The owner or operator shall
incorporate this
plan and schedule into the facility inspection plan required under
Section 724.115.
(Source:
Added at
19
Ill. Reg.
________,
effective
_____________________)
Section 724.989
Recordkeeping Requirements
~j
Each owner or operator of
a facility
subject to requirements in
this Subpart shall record and maintain the following information
as applicable:
j)
Documentation
for each cover installed on
a tank in
accordance with the requirements of Section 724.984(b) (2)
or
(b)(3)
that includes information prepared by the owner or
operator or provided by the cover manufacturer
or vendor
117
describing the cover design,
and certification by the owner
or operator that the cover meets the applicable design
specifications as
listed
in
35
Ill.
Adm.
Code 725.991(c).
21
Documentation for each floating membrane cover installed on
a surface impoundment in accordance with the requirements of
Section 724.985(c)
that includes information prepared by the
owner_or operator or provided by the cover manufacturer or
vendor describing the cover design,
and certification by the
owner or operator that the cover meets the specifications
listed in 35
Ill.
Adm. Code 725.986(e).
~J.
Documentation for each enclosure used to control air
emissions from containers
in accordance with the
requirements of Section 724.986(b) (2) (A)
that includes
information prepared by the owner or operator or provided by
the manufacturer or vendor describing the enclosure design,
and certification by the owner or operator that the
enclosure meets the specifications
listed
in Section
724.986(b) (2) (B).
~J
Documentation for each closed—vent
system and control device
installed
in accordance with the requirements of Section
724.987 that includes:
~j_
Certification that
is
signed and dated by the owner or
operator stating that the control device
is designed
to operate
at the performance level
documented by a
design analysis
as specified
in subsection
(a)(4)(B)
below or by performance tests
as
specified in
subsection
(a)(4)(C) below when the tank,
surface
impoundment, or container
is or would be operating at
capacity or the highest level reasonably expected to
occur.
flj..
If
a design analysis
is used,
then design
documentation as specified in Section 724.935(b)(4).
The documentation shall
include information prepared
by the owner or operator or provided by the control
device_manufacturer or vendor that describes the
control device design in accordance with Section
724.935(b) (4) (C)
and certification by the owner or
operator that the control equipment meets the
applicable specifications.
gI
If performance tests are used, then a performance test
plan as specified
in Section 724.935(b) (3)
and all
test results.
P1
Information as
required by Section 724.935(c)(l) and
(C)
(2).
~j
Records for all Method 27 tests performed by the owner or
operator for each container used to meet the requirements of
Section 724.986(b~(1) (C).
~J
Records for all visual
inspections conducted
in
accordance
with the requirements of Section
724.988.
21
Records for all monitoring for detectable organic emissions
conducted
in accordance with the requirements of Section
724. 988.
118
~j.
Records of the date of each attempt to repair
a leak,
repair
methods applied,
and the date of successful repair.
~j
Records for all continuous monitoring conducted in
accordance with the requirements of Section 724.988.
IQI
Records of the management of carbon removed from a carbon
adsorption system conducted in accordance with Section
724.987(c) (3) (B).
~J~j
Records for all inspections of each cover installed on
a
tank in accordance with the requirements of Section
724.984(b) (2) or
(b)(3) that includes information as listed
in 35
Ill. Adm. Code 725.991(c).
~J
An owner or operator electing to use air emission controls for a
tank in accordance with the conditions specified
in Section
724.984(c)
shall record the following information:
jj
Date and time each waste sample
is collected for direct
measurement of maximum organic vapor pressure in accordance
with Section 724.983(c).
21
Results of each determination of the maximum organic vapor
pressure of the waste in
a tank performed
in accordance with
Section 724.983(c).
~J
Records specifying the tank dimensions and design capacity.
~
An owner or operator electing to use air emission controls
for a
tank in accordance with the requirements of Section 724.991 shall
record the information required by Section 724.991(c).
~J.
An owner or operator electing not to use air emission controls for
a particular tank, surface impoundment,
or container subject to
this Subpart in accordance with the conditions specified in
Section 724.982(c)
shall record the information used by the owner
or operator for each waste determination
(e.g., test result~~
measurements,
calculations,
and other documentation)
in the
facility operating
log.
If analysis results for waste samples are
used for the waste determination, then the owner or operator shall
record the date,
time,
and location that each waste sample
is
collected in accordance with applicable requirements of Section
724.983.
~J.
An owner or operator electing to comply with requirements
in
accordance with Section 724.982(c)(2)(E)
or Section
724.982(c)(2)(F)
shall record the identification number for the
incinerator,
boiler,
or industrial
furnace
in which the hazardous
waste is treated.
fi
An owner or operator designating a cover as unsafe to inspect and
monitor pursuant to 35
Ill. Adm.
Code 725.989(f)(5) or difficult
to inspect and monitor pursuant to
35 Ill.
Adm. Code 725.989(f)(6)
shall record in a log that
is kept in the facility operatin,g
record the following information:
IL
A list of identification numbers
for tanks with covers that
are designated as unsafe to inspect and monitor in
accordance with the requirements
of
35
Ill. Adm.
Code
725.989(f)(5),
an explanation for each cover stating why the
cover
is unsafe to inspect and monitor,
and the plan and
119
schedule for inspecting and monitoring each cover.
21
A list
of identification numbers for tanks with covers that
are designated
as difficult to inspect and monitor in
accordance with the requirements of
35
Ill.
Adm.
Code
725.989(f)(6),
an explanation
for each cover
stating why the
cover
is difficult to inspect and monitor,
and the plan and
schedule for inspecting and monitoring each cover.
2).
All records required by subsections
(a) through
(f)
above, except
as required
in subsections
(a)(l) through (a)(4),
shall be
maintained in the operating record
for
a minimum of
3 years.
All
records required by subsections
(a)(1) through
(a)(4)
above shall
be maintained in the operating record until the air emission
control equipment
is replaced or otherwise no longer in service.
~j
The owner or operator of
a facility that is subject to this
Subpart and to the control device standards
in 40 CFR 60,
Subpart
VV or
40 CFR 61,
Subpart V,
incorporated by reference
in
35
Ill.
Adm.
Code 720.111, may elect to demonstrate compliance with the
applicable Sections of this Subpart by documentation either
pursuant to this Subpart,
or pursuant to the provisions of 40 CFR
60,
Subpart VV or 40
CFR 61,
Subpart V,
to the extent that the
documentation required by
40 CFR
60 or
61 duplicates the
documentation required by this Section.
(Source:
Added at
19 Ill. Reg.
,
effective
______________________
Section 724.990
Reporting Requirements
~J
Each owner or operator managing hazardous waste in a tank,
surface
impoundment,
or container exempted from using air emission
controls under the provisions of Section 724.982(c)
shall report
to the Agency each occurrence when hazardous waste
is placed in
the waste management unit
in noncompliance with the conditions
specified in Section 724.982(c)(l)
or
(c)(2),
as applicable.
Examples of such occurrences
include placing
in the waste
management unit
a hazardous waste having an average VO
concentration equal to or greater than 100 ppmw at
the Point of
waste origination or placing in the waste management unit a
treated hazardous waste that fails to meet the applicable
conditions specified in Section 724.982(c)(2)(A) through
(c)(2)(E).
The owner or operator shall submit
a written report
within_15_calendar days of the time that the owner or operator
becomes aware of the occurrence.
The written report shall contain
the U.S. EPA identification number, the facility name and address,
a description of the noncompliance event and the
cause, the dates
of
the noncompliance,
and the actions taken to correct the
noncompliance and prevent reoccurrence of the noncompliance.
The
report shall be
signed and dated by an authorized representative
of
the owner or operator.
~j
Each owner or operator using air emission controls on
a tank in
accordance with the requirements Section 724.984(c)
shall report
to the Agency each occurrence when hazardous waste
is managed in
the tank in noncompliance with the conditions specified in Section
724.984(c)(l) through
(c)(4).
The owner or operator shall
submit
a written report within 15 calendar days of the time that the
owner or operator becomes aware
of the occurrence.
The written
report shall contain the U.S. EPA identification number,
the
facility name and address,
a description of the noncompliance
event and the cause,
the dates of the noncompliance, and the
120
actions taken to correct the noncompliance and prevent
reoccurrence of the noncompliance.
The report
shall be signed and
dated by an authorized representative of the owner or operator.
~j
Each owner or operator using a control device in accordance with
the requirements of Section 724.987 shall
submit a semiannual
written report to the Agency excepted
as provided for in
subsection
(d)
below.
The report shall describe each occurrence
during the previous 6-month period when a control device
is
operated continuously for 24 hours or longer in noncompliance with
the applicable operating values defined
in Section 724.935(c)(4)
or when a flare is operated with visible emissions as defined
in
Section 724.933(d).
The written report
shall include the
U.
S.
EPA identification number, the facility name and address,
and an
explanation why the control device could not be returned to
compliance within 24 hours, and actions taken to correct the
noncompliance.
The report
shall be signed and dated by an
authorized representative of the owner or operator.
~J
A report to the Agency
in accordance with the requirements of
subsection
(c)
above
is not required for
a 6—month period during
which all control devices subject to this Subpart are operated by
the owner or operator so that during no period of 24 hours or
longer did
a control device operate continuously
in noncompliance
with the applicable operating values defined
in Section
724.935(c)(4)
or
a flare operate with visible emissions,
as
defined in Section 724.933(d).
(Source:
Added at
19
Ill.
Reg.
________,
effective
______________________
Section 724.991
Alternative Control Requirements for Tanks
~J
This Section applies to owners and operators of tanks that elect
to comply with Section 724.984(b) (2) or Section 724.984(b) (3).
11
The owner or operator that elects to comply with Section
724.984(b) (2) shall design,
install,
operate,
and maintain a
fixed roof and internal
floating roof that meet the
requirements
specified
in 35
Ill. Adm. Code 725.991(a)(l)(A)
through
(a)(1)(I).
21
The owner or operator that elects to comply with Section
724.984(b) (3)
shall design,
install,
operate,
and maintain
an external floating roof that meets the requirements
specified in
35
Ill.
Adm. Code 725.99l(a)(2)(A) through
(a) (2) (C).
~J
The owner or operator shall
inspect and monitor the control
equipment
in
accordance with the following requirements:
11
For
a tank equipped with a fixed roof and internal floating
roof in accordance with the requirements of
subsection
Ia)(l)
above, the owner or operator shall perform the
inspection and monitoring requirements
specified in
35
Ill.
Adm. Code 725.991(b)(l).
21
For
a tank equipped with an external floating roof in
accordance with the requirements of subsection
(a)(2)
above,
the owner or operator shall perform the inspection and
monitoring requirements specified in
35
Ill. Mm.
Code
725.991(b) (2).
121
çj
The owner or operator shall record the following information in
the operating record in accordance with the requirements
of
Section 724.989(a) (1) and
(a)(ll):
IL
For
a tank equipped with
a fixed roof and internal floating
roof
in accordance with the requirements of subsection
(a)(l) above,
the owner or operator shall record the
information listed
in
35
Ill. Adm. Code 725.991(c)(l).
21
For a tank equipped with an external floating roof in
accordance with the requirements of subsection
(a)(l) above,
the owner or operator shall record the information listed in
35
Ill.
Adm.
Code 725.991(c)(2).
(Source:
Added at
19
111.
Reg.
_______,
effective
_____________________)
SUBPART DD:
CONTAINMENT BUILDINGS
Section 724.1102
Closure and ~Pogt-closure eCare
a)
At closure of
a containment building,
the owner or operator must
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.
Adin.
Code 721.103(eQ)
applies.
The closure plan,
closure activities,
cost estimates
for closure,
and financial responsibility for
containment buildings must meet all of the requirements specified
in 739.Subparts G and
H.
b)
If,
after removing or decontaminating all residues and making all
reasonable efforts to effect removal or decontamination of
contaminated components,
aubsoils,
structures,
and equipment as
required in subsection
(a) above, the owner or operator finds that
not all contaminated subsoils can be practicably removed or
decontaminated, he must close the facility and perform post—
closure care in accordance with the closure and post—closure
requirements that
apply to landfills
(35 Ill. Adm. Code 724.310).
In addition,
for the purposes of closure, post—closure,
and
financial responsibility,
such a containment building
is then
considered to be a landfill,
and the owner or operator must meet
all the requirements
for landfills specified in 739.Subparts G and
H.
(Source:
Amended at 19
Ill. Reg.
________,
effective
________________
TITLE
35:
ENVIRONMENTAL PROTECTION
SUBTITLE G:
WASTE DISPOSAL
CHAPTER I:
POLLUTION CONTROL BOARD
SUBCHAPTER
c:
HAZARDOUS WASTE OPERATING REQUIREMENTS
PART 725
INTERIM STATUS STANDARDS FOR OWNERS AND OPERATORS OF HAZARDOUS
WASTE TREATMENT,
STORAGE, AND DISPOSAL FACILITIES
SUBPART A:
GENERAL PROVISIONS
Section
725.101
Purpose,
Scope and Applicability
725.104
Imminent Hazard Action
122
SUBPART
B:
GENERAL
FACILITY STANDARDS
Section
725.110
Applicability
725.111
USEPA Identification Number
725.112
Required Notices
725.113
General Waste Analysis
725.114
Security
725.115
General Inspection Requirements
725.116
Personnel Training
725.117
General Requirements for Ignitable, Reactive~or Incompatible
Wastes
725.118
Location Standards
725.119
Construction Quality Assurance Program
SUBPART C:
PREPAREDNESS
AND
PREVENTION
Section
725.130
Applicability
725.131
Maintenance and Operation of Facility
725.132
Required Equipment
725.133
Testing and Maintenance of Equipment
725.134
Access to Communications or Alarm System
725.135
Required Aisle Space
725.137
Arrangements with Local Authorities
SUBPART D:
CONTINGENCY PLAN AND EMERGENCY PROCEDURES
Section
725.150
Applicability
725.151
Purpose and Implementation of Contingency Plan
725.152
Content of Contingency Plan
725.153
Copies of Contingency Plan
725.154
Amendment of Contingency Plan
725.155
Emergency Coordinator
725.156
Emergency Procedures
SUBPART E:
MANIFEST SYSTEM,
RECORDKEEPING AND REPORTING
Section
725.170
Applicability
725.171
Use of Manifest System
725.172
Manifest Discrepancies
725.173
Operating Record
725.174
Availability,
Retention and Disposition of Records
725.175
Annual Report
725.176
Unmanifested Waste Report
725.177
Additional Reports
SUBPART F:
GROUNDWATER MONITORING
Section
725.190
Applicability
725.191
Groundwater Monitoring System
725.192
Sampling and Analysis
725.193
Preparation, Evaluation
and Response
725.194
Recordkeeping and Reporting
SUBPART
G:
CLOSURE
AND POST-CLOSURE
Section
725.210
Applicability
725.211
Closure Performance Standard
725.212
Closure Plan;
Amendment of Plan
725.213
Closure; Time Allowed for Closure
725.214
Disposal or Decontamination of Equipment,
Structures
and Soils
725.215
Certification of Closure
725.216
Survey Plat
123
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
Liability Requirements
Incapacity of Owners or Operators,
Guarantors or Financial
Institutions
Promulgation of Forms
(Repealed)
SUBPART
I:
USE AND MANAGEMENT OF CONTAINERS
Applicability
Condition of Containers
Compatibility of Waste with Container
Management of Containers
Inspections
Special Requirements for Ignitable or Reactive Waste
Special Requirements for Incompatible Wastes
Air Emission Standards
SUBPART
J:
TANK
SYSTEMS
Applicability
Assessment
of
Existing
Tank System’s Integrity
Design
and
Installation
of
New Tank Systems or
Containment
and
Detection
of
Releases
General
Operating
Requirements
Inspections
Response to leaks or spills and disposition of
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-r
Air Emission Standards
SUBPART
K:
SURFACE IMPOUNDMENTS
Applicability
Design
and
Operating
Requirements
Action
Leakage
Rate
Response
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
Air Emission Standards
725. 217
725. 218
725.219
725. 220
Section
725. 240
725. 241
725.242
725. 243
725. 244
725. 245
725. 246
725. 247
725. 248
725. 251
Section
725. 270
725.271
725. 272
725.273
725.274
725.276
725.277
725.278
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
725.302
Section
725. 320
725.321
725. 322
725.323
725.324
725. 325
725. 326
725. 328
725.329
725. 330
725.331
Components
Tank
Systems
SUBPART L:
WASTE PILES
124
Section
725. 350
Applicability
725.351
Protection
from
Wind
725.352
Waste
Analysis
725.353
Containment
725.354
Design and Operating Requirements
725.355
Action Leakage Rates
725.356
Special Requirements for Ignitable or Reactive Waste
725.357
Special Requirements for Incompatible Wastes
725.358
Closure and Post—Closure Care
725.359
Response Actions
725.360
Monitoring and Inspection
SUBPART
M:
LAND
TREATMENT
Section
725.370
Applicability
725.372
General Operating Requirements
725.373
Waste Analysis
725.376
Food Chain Crops
725.378
Unsaturated Zone (Zone of Aeration) Monitoring
725.379
Recordkeeping
725.380
Closure and Post-closure
725.381
Special Requirements for Ignitable or Reactive Waste
725.382
Special Requirements for Incompatible Wastes
SUBPART N:
LANDFILLS
Section
725.400
Applicability
725.401
Design
Requirements
725.402
Action
Leakage
Rate
725.403
Response Actions
725.404
Monitoring and Inspection
725.409
Surveying and Recordkeeping
725.410
Closure and Post—Closure
725.412
Special Requirements for Ignitable or Reactive Waste
725.413
Special Requirements for Incompatible Wastes
725.414
Special Requirements for Liquid Wastes
725.415
Special
Requirements
for
Containers
725.416
Disposal
of
Small
Containers
of
Hazardous
Waste
in
Overpacked
Drums (Lab Packs)
SUBPART 0:
INCINERATORS
Section
725.440
Applicability
725.441
Waste Analysis
725.445
General Operating Requirements
725.447
Monitoring and Inspection
725.451
Closure
725.452
Interim Status Incinerators Burning Particular Hazardous Wastes
SUBPART
P:
THERMAL
TREATMENT
Section
725.470
Other Thermal Treatment
725.473
General Operating Requirements
725.475
Waste Analysis
725.477
Monitoring and Inspections
725.481
Closure
725.482
Open Burning; Waste Explosives
725.483
Interim Status Thermal Treatment Devices Burning Particular
Hazardous
Waste
SUBPART Q:
CHEMICAL,
PHYSICAL
AND
BIOLOGICAL TREATMENT
125
Section
725.500
Applicability
725.501
General Operating Requirements
725.502
Waste Analysis and Trial Tests
725.503
Inspections
725.504
Closure
725.505
Special Requirements for Ignitable or Reactive Waste
725.506
Special Requirements for Incompatible Wastes
SUBPART R:
UNDERGROUND INJECTION
Section
725.530
Applicability
SUBPART
W:
DRIP
PADS
Section
725.540
Applicability
725.541
Assessment
of
existing
drip
pad
integrity
725.542
Design
and
installation
of
new
drip
pads
725.543
Design
and
operating
requirements
725.544
Inspections
725.545
Closure
SUBPART AA:
AIR EMISSION STANDARDS FOR PROCESS VENTS
Section
725.930
Applicability
725.931
Definitions
725.932
Standards:
Process Vents
725.933
Standards:
Closed—vent Systems and Control Devices
725.934
Test methods and procedures
725.935
Recordkeeping Requirements
SUBPART
BB:
AIR
EMISSION
STANDARDS
FOR
EQUIPMENT
LEAKS
Section
725.950
Applicability
725.951
Definitions
725.952
Standards:
Pumps
in
Light Liquid Service
725.953
Standards:
Compressors
725.954
Standards:
Pressure Relief Devices
in Gas/Vapor Service
725.955
Standards:
Sampling
Connecting
Systems
725.956
Standards:
Open-ended
Valves
or
Lines
725.957
Standards:
Valves
in
Gas/Vapor or Light Liquid Service
725.958
Standards:
Pumps,
Valves,
Pressure Relief Devices,
Flanges and
Other Connectors
725.959
Standards:
Delay of Repair
725.960
Standards:
Closed—vent Systems and Control Devices
725.961
Percent Leakage Alternative
for Valves
725.962
Skip Period Alternative for Valves
725.963
Test Methods and Procedures
725.964
Recordkeeping Requirements
SUBPART CC:
AIR EMISSION STANDARDS FOR TANKS,
SURFACE IMPOUNDMENTS, AND CONTAINERS
Section
725.980
Applicability
725.981
Definitions
725.982
Schedule
for
Implementation
of
Air
Emission
Standards
725.983
Standards:
General
725.984
Waste Determination Procedures
725.985
Standards:
Tanks
725.986
Standards:
Surface Impoundments
725. 987
________________________
725. 988
Standards:
Containers
Standards:
Closed—vent Systems and Control Devices
126
725.989
Inspection and Monitoring Requirements
725.990
Recordkeeping Requirements
725.991
Alternative
Tank
Emission
Control
Requirements
SUBPART
PD:
CONTAINMENT BUILDINGS
Section
725.1100
Applicability
725.1101
Design
and
operating
standards
725.1102
Closure and pPost eçlosure-e~are
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 P
Tests for Significance
725.Appendix
E
Examples
of
Potentially
Incompatible
Waste
AUTHORITY:
Implementing Section
22.4
and
authorized
by
Section
27
of
the
Environmental Protection Act
(415 ILCS 5/22.4 and 271.
SOURCE:
Adopted in R81~-22, 43 PCB 427,
at
5
Ill. Reg.
9781,
effective ee
notcd in 35
Ill.
Adm.
Codo
700.lO6May
17, 1982
amended
and codified
in R81—
22,
45
PCB
317,
at
6
Ill.
Reg.
4828,
effective
as
notcd
in
35
Ill.
Mm.
Codo
700.lO6May
17. 1982
amended in R82—18,
51 PCB 831, at
7
Ill. Reg. 2518,
effective February 22,
1983;
amended in R82—l9,
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—l6 at
13
Ill. Reg.
437,
effective December 28,
1988;
amended in R89—.
at
13
Ill.
Reg.
18354,
effective
November
13,
1989;
amended in R90—2
at
14
Ill. Reg.
14447,
effective August
22,
1990;
amended in R90—10 at
14 Ill.
Reg.
16498,
effective September 25,
1990;
amended
in R90—ll
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—l at 16
Ill.
Reg.
17672,
effective
November
6,
1992;
amended
in
R92—1O
at
17
Ill.
Reg.
5681,
effective
March
26,
1993;
amended
in
R93-4
at
17
Ill.
Reg.
20620,
effective
November
22,
1993;
amended
in
R93—16
at
18
Ill.
Reg.
6771,
effective
April
26,
1994;
amended
in
R94—7 at
18
Ill.
Reg.
12190,
effective
July
29,
1994;
amended
in R94—17 at 18
Ill.
Reg.
17548,
effective November 23,
1994;
amended in
R95—6
at
19
Ill.
Reg.
________,
effective
_____________________
SUBPART
A:
GENERAL
PROVISIONS
Section
725.101
Purpose,
Scope
and
Applicability
a)
The
purpose
of
this
Part
is
to
establish
minimum
standards
~hichthat
define
the
acceptable management of hazardous waste
during
the
period
of
interim
status
and
until
certification of
final closure or,
if the facility is
subject to post—closure
requirements,
until post-closure responsibilities are fulfilled.
b)
Except as provided
in Section 725.980(b), t~hestandards
in this
Part and
e~—35 Ill. Adm. Code 724.652 and 724.653 apply to owners
and operators of facilities whiohthat treat,
storer or dispose of
hazardous waste whethat have fully complied with the requirements
for interim status under Section 3005(e)
of the Resource
Conservation
and
Recovery
Act
(RCRA)
(42 U.S.C.
6901 et seq.) and
127
35
Ill.
Adxn.
Code
703,
until either a permit
is issued under
Section 3005 of the Resource Conservation and Recovery Act or
Section
21(f)
of
the
Environmental
Protection
Act,
or
until
applicable
closure
and
post-closure
responsibilities
under
this
Part
are
fulfilled,
and
to
those
owners
and
operators
of
facilities
in existence on November
19,
1980,
w1~ethathave failed
to provide timely notification as required by Section 3010(a)
of
RCRA7- or that have failed to file Part A of the Permit
App1ication~as required by
40
CFR
270.10(e)
and
(g)
or 35
Ill.
Adxn. Code 703.150 and 703.152.
These standards
apply
to
all
treatment, storage~or disposal of hazardous waste at these
facilities after November 19,
1980,
except as specifically
provided otherwise in this Part or 35
Ill.
Adni. Code 721;
BOARD
NOTE:
As stated
in Section 3005(a)
of RCRA,
after the
effective date of regulations under that Section-,- ji.e.,
40 CFR
270 and
l24-,.j the treatment, storage~or disposal of hazardous
waste
is
prohibited
except
in
accordance
with
a
permit.
Section
3005(e)
of
RCRA
provides for the continued operation of
an
existing
facility
whichthat
meets certain conditions until
final
administrative disposition of the
owner’s
and operator’s permit
application
is
made.
35
Ill.
Adm.
Code
703.140
et
seq.
provide
that
a
permit
is
deemed
issued
under
Section
2l(f)(l)
of the
Environmental Protection Act under conditions similar to federal
interim status.
c)
The requirements of this Part do not apply to:
1)
A
person
disposing
of
hazardous
waste
by
means
of
ocean
disposal
subject
to
a
permit
issued
under
the
Marine
Protection,
Research
and
Sanctuaries
Act
(16
U.S.C.
1431—
1434;
33
U.S.C.
1401);
BOARD
NOTE:
This
Part applies to the treatment or
storage
of
hazardous
waste
before
it
is
loaded
into
an
ocean
vessel
for
incineration
or
disposal
at
sea,
as
provided
in
subsection
(b)
above.
3)
The
owner
or
operator
of
a
POTW
(publicly
owned
treatment
works)
whichthat treats,
stores or disposes of hazardous
waste;
BOARD
NOTE:
The owner or operator of a facility under
subsections
(c)(1) through
(c)(3)
is subject to the
requirements of
35
Ill.
Adm.
Code
724 to the extent they are
included in
a permit by rule granted to such a person under
35
Ill.
Adm.
Code
702
and
703
or
are
required
by
35
Ill.
Adin.
Code
704.Subpart F.
5)
The
owner
or
operator
of
a
facility permitted, licensed~ or
registered
by
Illinois
to
manage
municipal
or
industrial
solid
waste,
if
the
only
hazardous
waste
the
facility
treats, etores~or disposes of
is
excluded
from regulation
under
this
Part
by
35
Ill.
Adm.
Code
721.105;
6)
The
owner
or
operator
of
a
facility
managing
recyclable
materials
described
in
35
Ill.
Adm.
Code
721.106(a)
(2)-,-
through
(a)(4)~
-(-except
to
the
extent
that requirements
of
this
Part
are
referred
to
in
35
Iii.
Mm.
Code
726.Subparts
C,
F,
G,
or
H
or
35
Ill.
Adni.
Code
739-)-;
7)
A
generator
accumulating
waste
on—site
in
compliance
with
35
128
Ill.
Adm.
Code
722.134,
except to the extent the
requirements are included in
~35
Ill.
Adm. Code 722.134;
8)
A farmer disposing of waste pesticides from the farmer’s own
use in compliance with 35 Ill. Adm. Code 722.170;
9)
The owner or operator of
a totally enclosed treatment
facility,
as defined in 35
Ill.
Adni.
Code 720.110;
10)
The owner or operator of an elementary neutralization unit
or a wastewater treatment
unit as defined
in 35 Ill. Adm.
Code 720.110,
provided that if the owner or operator
is
diluting hazardous ignitable
(DOOl) wastes (other than the
D001 High TOC Subcategory defined
in 35
Ill.
Adm. Code
728.Table
ST)-,- or corrosive (D002)
waste-,- in order to remove
the characteristic before
land disposal,
the owner or
operator must comply with the requirements set out in
Section 725.117(b);
11)
Immediate response:
A)
Except as provided in subsection
(c)(ll)(B)-,- below,
a
person engaged
in treatment or containment activities
during
immediate
response
to
any
of
the
following
situations:
i)
A
discharge
of
a
hazardous waste;
ii)
An
imminent
and
substantial
threat of
a
discharge of
a hazardous waste;
iii)
A discharge of
a material which, whon
diocharg-cd, that becomes a hazardous waste when
discharged.
B)
An
owner
or
operator
of
a
facility
otherwise
regulated
by
thia
Part must comply with all applicable
requirements of 725.Subparts C and P.
C)
Any person whethat
is covered by subsection
(c)(ll)(A)-,-
above
and whothat continues or initiates
hazardous
waste
treatment
or
containment
activities
after
the
immediate response
is over
is
subject to all
applicable requirements of this Part and 35
Ill.
Adm.
Code
702,
703~ and
705
for
those
activities.
12)
A transporter storing manifested shipments of hazardous
waste
in
containers
meeting
the
requirements
of
35
Ill.
Adm.
Code
722.130
at
a
transfer
facility
for
a
period
of
ten
days
or less.
13)
The
addition
of
absorbent
material
to
waste
in
a
container
(as
defined
in
35
Ill.
Adni.
Code
720.110)-,-
or
the
addition
of
waste
to
the
absorbent
material
in
a
container,
provided
that
these
actions
occur at the time that the waste
is first
placed
in
the
containers-p-
and
Sections 725.117(b),
725.271,
and
725.272
are complied with.
d)
The
following
hazardous
wastes
must
not
be
managed
at
facilities
subject
to
regulation
under
this
Part:
hazardous waste numbers
F020,
F021,
F022,
F023, FO26~or P027 unless:
129
1)
The wastewater treatment sludge
is generated in a surface
impoundment as part of the plant’s wastewater treatment
system;
2)
The
waste
is
stored
in
tanks
or
containers;
3)
The
waste
is
stored
or
treated
in
waste
piles
that
meet
the
requirements
of
35
111.
Adm.
Code
724.350(c)
ac
t:oll
~
all
other
applicable
requirements
of
725.Subpart
L;
4)
The
waste
is
burned
in
incinerators
that are certified
pursuant
to
the
standards
and
procedures
in
Section
725.452;
or
5)
The
waste
is
burned
in
facilities that thermally treat the
waste
in
a
device
other
than
an
incinerator
and
that are
certified
pursuant
to
the
standards and procedures
in
Section
725.483.
e)
This
Part
applies
to
owners
and
operators
of
facilities
whiohthat
treat,
store~
or
dispose
of
hazardous
wastes
referred
to
in
35
Ill.
Adm.
Code
728,
and
the
35
Ill.
Adm.
Code
728
standards
are
considered
material
conditions
or
requirements
of
the
interim
status
standards
of
this
Part.
f)
.i~ iii.
hum.
~oue
,uu
containo
rulec
concerning
appiication
ot
othor
Board
rogulationo.Other
bodies
of
regulations
may
apply
a
person,
facility, or activity,
such as
35
Ill.
Adm.
Code
809
(special waste hauling),
35
Ill.
Adm.
Code 807
or
810
through
817
(solid waste
landfills),
35
Ill.
Adm. Code 848 or 849
(used and
scrap tires),
or 35
Ill. Adm. Code 1420 through 1422
(potenyially
infectious
medical
waste),
depending
on
the
provisions
of
those
other regulations.
(Source:
Amended
at
19
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
wastes,
or
non—hazardous
wastes
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 wastes.
At
a minimum, the
analysis must contain all the information whichthat must be
known
to
treat,
storer
or
dispose
of
the
waste
in
accordance
with
this
Part
and
35
Ill.
Adm.
Code
728.
2)
The
analysis
may
include
data
developed under
35
Ill.
Adm.
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
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
included in the
130
data base required to comply with subsection
(a) (1)-,- above,
except as otherwise specified in 35
Ill.
Adm.
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)(l)-,- 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 whichthat describes the procedures whichthat 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 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 (a)T above.
2)
The test methods whichthat will be used to test for those
parameters.
3)
The sampling method whichthat 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.
Adm.
Code 721.Appendix A~or
B)
An equivalent sampling method.
BOARD NOTE:
See
35
Ill.
Adni.
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
131
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 whichthat 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
725.984,
and
35
Ill.
Adm.
Code 728.107.
And,
7)
For
surface impoundments exempted from land disposal
restrictions under 35
Ill.
Adrn.
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 whichthat are not
delisted under 35 111.
Adm. Code 720.122 or whichthat
exhibit
a characteristic of hazardous
waste-,-- and
either:
i)
Do not meet the applicable treatment standards
of 35 Ill.
Adm. Code 728.Subpart D-~-~
or
ii)
Where no treatment
standards have been
established:
Such residues are prohibited from
land disposal under 35
Ill. Adm.
Code 728.132 or
728.139; or ~uoh reciduoc arc prohibitcd from
land diciporial undcr
35
Ill.
Mm.
Codc
7-28.133(f).
~j.
For owners and operators seeking an exemption to the air
emission standards of 724.Subpart CC of this part
in
accordance with Section 725.983:
~j.
The procedures and schedules for waste sampling and
analysis,
and the analysis of test data to verify the
exemption.
~J
Each generator’s notice and certification of the
volatile organic concentration
in the waste
if the
waste is received from offsite.
c)
For off—site facilities, the waste analysis plan required in
subsection
(b)-,-
above-,- must also specify the procedures whichthat
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 ~hichthat will be used to determine the
identity of each movement of waste managed at the facility;
and
2)
The sampling method whiohthat will be used to obtain
a
representative sample of the waste to be
identified-,-
if the
identification method includes sampling.
132
3)
The
procedures
that
the
owner
or
operator
of
an
off—site
landfill
receiving
containerized hazardous waste will use to
determine
whether
a
hazardous
waste
generator
or
treater
has
added
a
biodegradable
sorbent
to
the
waste
in
the
container.
(Source:
Amended
at
19
Ill.
Reg.
________,
effective
_____________________
Section
725.114
Security
a)
The
owner
or
operator
must
prevent
the
unknowing
entry
and
minimize
the
possibility
for
the
unauthorized
entry
of
persons
or
livestock
onto
the
active
portion
of
his
facility,
unless:
1)
Physical
contact
with
the
waste,
structures1,
or
equipment
of
the
active
portion
of
the
facility
will
not
injure
unknowing
or
unauthorized
persons
or
livestock
whichthat
may
enter
the
active
portion
of
a~
facility;
and
2)
Disturbance
of
the
waste
or
equipment-,-
by
the
unknowing
or
unauthorized
entry
of
persons
or
livestock
onto
the
active
portion
of
a
facility
will
not
cause
a
violation
of
the
requirements
of
this
p~art.
b)
Unless
exempt
under
paragraphosubsections
(a)(l)
and
(a)(2)
ef-
thin
occtionabove,
a
facility
must
have:
1)
A
24—hour
surveillance
system
(e.g.,
television
monitoring
or
surveillance
by
guards
or
facility
personnel)
whiohthat
continuously
monitors
and
controls
entry
into
the
active
portion
of
the
facility;
or—~-
21
Controlled
access,
including
the
following
minimum
elements:
A)
An
artificial
or
natural
barrier
(e.g.,
a
fence
in
good
repair
or
a
fence
combined
with
a
cliff)-,-
~:hiohthat
completely
surrounds
the
active
portion
of
the
facility;
and
B)
A
means
to
control
entry
at
all
times
through
the
gates
or
other
entrances
to
the
active
portion
of
the
facility
(e.g.,
an
attendant,
television
monitors,
locked
entrance1,
or
controlled
roadway
access
to
the
facility).
BOARD
NOTE:
The
requirements
of
paragrapheubsection
(b)
of
thin
occtionabove
are
satisfied
if
the
facility
or
plant
within
which
the
active
portion
is
located
itself
has
a
surveillance
system
or
a
barrier
and
a
means
to
control
entry
whiohthat
complies
with
the
requirements
of
paragrapheubsection
(b)(l)
or
(b)(2)
of
thin
cootion.
c)
Unless
exempt
under
paragraphasubsection
(a)(l)
~dQ~
(a)(2)
ef-
thin
cioctionabove,
a
sign
with
the
legend,
“Danger——Unauthorized
Personnel
Keep
Out,”
must
be
posted
at
each
entrance
to
the
active
portion
of
a
facility
and
at
other
locations-,-
in
sufficient
numbers
to
be
seen
from
any
approach
to
this
active
portion.
The
sign
must
be
legible
from
a
distance
of
at
least
25
feet.
Existing
signs
with
a
legend
other
than
“Danger——Unauthorized
Personnel
Keep
Out”
may
be
used
if
the
legend
on
the
sign
indicates
that
only
authorized
personnel
are
allowed
to
enter
the
active
portion
and
that
entry
onto
the
active
portion
can
be
133
dangerous.
BOARD
NOTE:
See
Section
725.217(b)
for
discussion
of
security
requirements
at
disposal
facilities
during
the
post—closure
care
period.
(Source:
Amended
at
19
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
whiohthat
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
environment1,
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,
security
devices1,
and
operating
and
structural
equipment
(such
as
dikes
and
sump
pumps)
that
are
important
to
preventing,
detecting1,
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)
whiohthat
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
deterioration
of
the
equipment
and
the
probability
of
an
environmental
or
human
health
incident
if
the
deterioration,
malfunction1,
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,
725.326,
725.360,
725.378,
725.404,
725.447,
725.477,
725.503,
725.933,
725.952,
725.9531,
and
725.958,
725.989,
and
725.991(b),
where
applicable.
c)
The
owner
or
operator
shall
remedy
any
deterioration
or
malfunction
of
equipment
or
structure
whichthat
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
134
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
date1,
and
nature
of
any
repairs
or
other
remedial
actions.
(Source:
Amended
at
19
Ill.
Reg.
_______,
effective
____________________)
Section 725.117
General Requirements for Ignitable,
Reactive1, or
Incompatible
Wastes
a)
The
owner
or
operator
must
take
precautions
to
prevent
accidental
ignition
or
reaction
of
ignitable
or
reactive
waste.
This
waste
must
be
separated
and
protected
from
sources
of
ignition
or
reaction1,
including1,
but
not
limited
to-t---1,
open
flames,
smoking,
cutting and welding, hot surfaces,
frictional heat,
sparks
(static,
electrical
or
mechanical),
spontaneous
ignition
(e.g.1,
from
heat—producing
chemical
reactions),
and
radiant
heat.
While
ignitable or reactive waste
is being
handled, the owner
or
operator
must
confine
smoking
and
open
flame
to
specially
designated locations.
“No Smoking”
signs must be conspicuously
placed
wherever
there
is
a
hazard
from
ignitable
or
reactive
waste.
b)
Where specifically required by other e~ectionsof this ~art,
the
treatment, storage~or disposal of ignitable or reactive waste and
the mixture or commingling of
incompatible waste or incompatible
wastes
and materials, must be conducted so that
it does not:
1)
Generate extreme heat or pressure,
fire or explo-sion1, or
violent reaction;
2)
Produce uncontrolled toxic mists,
fumes,
dusts1, or gases
in
sufficient
quantities
to
threaten
human
health;
3)
Produce
uncontrolled
flammable
fumes
or
gases
in
sufficient
quantities
to
pose
a
risk
of
fire
or
explosions;
4)
Damage the structural integrity of the device or facility
containing the waste; or
5)
Through other
like means1, threaten human health or the
environment.
(Source:
Amended at
19 Ill.
Reg.
_______,
effective
_____________________
SUBPART
D:
CONTINGENCY
PLAN
AND
EMERGENCY
PROCEDURES
Section
725.150
Applicability
The
regulations
in
this
e~ubpart
apply
to
owners
and
operators
of
all
hazardous
waste
facilities,
except
as
Section
725.101
provides
otherwise.
(Source:
Amended
at
19
Ill.
Reg.
________,
effective
_____________________
Section
725.156
Emergency
Procedures
a)
Whenever there
is
an imminent or actual emergency situation,
the
emergency
coordinator
(or
his
designee
when
the
emergency
coordinator
is
on
call)
shall
immediately:
1)
Activate
internal facility alarms or communication systems,
135
where
applicable,
to
notify
all
facility
personnel;
and
2)
Notify
appropriate
state
or
local
agencies
with
designated
response
roles
if
their
help
is
needed.
b)
Whenever
there
is
a
release,
fire,
or
explosion,
the
emergency
coordinator
shall
immediately
identify
the
character,
exact
source,
amount,
and
a
real
extent
of
any
released
materials.
He
or she may do this by observation or review of facility records or
manifests and,
if necessary,
by chemical analysis.
c)
Concurrently, the emergency coordinator shall assess possible
hazards to human health or the environment that may result from
the release,
fire,
or explosion.
This assessment must consider
both direct and indirect effects of the release,
fire, or
explosion
(e.g.,
the
effects
of
any
toxic,
irritating,
or
asphyxiating
gases
that
are
generated,
or
the
effects
of
any
hazardous
surface
water
runoffs
from
water
or
chemical
agents
used
to
control
fire
and
heat—induced
explosions).
d)
If the emergency coordinator determines that the facility has had
a release,
fire,
or explosion that could threaten human health or
the environment outside the facility, he or she shall report his
findings as follows:
1)
If his assessment indicates that evacuation of local areas
may be
advisable, he or she shall immediately notify
appropriate local authorities.
He or she must be available
to help appropriate officials decide whether local areas
should be evacuated; and
2)
He or she shall immediately notify either the government
official designated as the on—scene coordinator for that
geographical area
(in the applicable regional contingency
plan under
40 CFR Part 300),
or the National Response Center
(using their 24—hour toll free number 800—424—8802).
The
report must include:
A)
Name and telephone number of reporter;
B)
Name and address of facility;
C)
Time and type of
incident
(e.g.,
release,
fire);
D)
Name and quantity of material±s-)-involved,
to the
extent known;
E)
The extent of injuries,
if any; and
F)
The possible hazards to human health or the
environment outside the facility.
e)
During an emergency the emergency coordinator shall take all
reasonable measures necessary to ensure that fires,
explosions,
and releases do not occur,
recur, or spread to other hazardous
waste at the
facility.
These measures must
include, where
applicable, stopping processes and operations,
collecting and
containing released waste,
and removing or isolating containers.
f)
If the facility stops operations in response to
a fire,
explosion
or release, the emergency coordinator shall monitor for leaks,
pressure buildup,
gas generation, or ruptures in valves,
pipes, or
136
other
equipment,
wherever
this
is
appropriate.
g)
Immediately
after
an
emergency,
the
emergency
coordinator
shall
provide for treating,
storing, or disposing of recovered waste,
contaminated soil,
or surface water,
or any other material that
results from a release,
fire,
or explosion at the facility.
CornmontBOARD
NOTE:
Unless
the
owner
or
operator
can
demonstrate-,-
in
accordance
with
Section
721.l03(ed)
or
(se)
that
the
recovered
material
is
not
a
hazardous
waste,
the
owner
or
operator
becomes
a
generator
of
hazardous
waste
and
shall
manage
it
in
accordance
with
all
applicable
requirements
of
Parts
722,
723,
and
725.
h)
The
emergency
coordinator
shall
ensure
that,
in
the affected
area-(--s-)- of the facility:
1)
No waste that may be incompatible with the released material
is
treated,
stored,
or
disposed
of
until
cleanup
procedures
are completed; and
2)
All
emergency
equipment
listed
in
the
contingency
plan
is
cleaned
and
fit
for
its
intended
use
before
operations
are
resumed.
i)
The owner or operator shall notify the Director and other
appropriate state and local authorities that the facility
is
in
compliance with paragr~phsubsection (h) of thin occtionabove
before operations are resumed
in the affected
area-(-s-)- of the
facility.
j)
The owner or operator shall note in the operating record the time,
date,
and
details
of
any
incident
that
requires
implementing
the
contingency
plan.
Within
15
days
after
the
incident,
it
shall
submit
a written report on the incident to the Director.
The
report
must
include:
1)
Name,
address,
and telephone number of the owner or
operator;
2)
Name,
address,
and
telephone
number
of
the
facility;
3)
Date,
time,
and
type
of
incident
(e.g.,
fire,
explosion);
4)
Name
and
quantity
of
material-(-s-)-
involved;
5)
The
extent
of
injuries,
if
any;
6)
An
assessment
of
actual
or
potential
hazards
to
human
health
or the environment,
where this is applicable;
and
7)
Estimated quantity and disposition of recovered material
that resulted from the incident.
(Source:
Amended at
19
Ill.
Reg.
________,
effective
_____________________
SUBPART E:
MANIFEST SYSTEM,
RECORDKEEPING AND REPORTING
Section 725.171
Use of Manifest System
a)
If a
facility receives hazardous waste accompanied by a manifest,
the owner or operator or his agent must:
137
1)
Sign and date each copy of the manifest to certify that the
hazardous waste covered by the manifest was received;
2)
Note any significant discrepancies in the manifest1,
-f--as
defined
in Section 725.172(a)-)-1, on each copy of the
manifest;
CommcntBOARD NOTE:
The Board doca not intend that the~
owner or operator of a facility whose procedures under
Section 725.113(c) include waste analysis muetneed not
perform that analysis before signing the manifest
and giving
it to the transporter.
Section 725.172(b),
however,
requires the owner or operator to report
an~unreconciled
discrepancy discovered during later analysis.
3)
Immediately give the transporter at least one copy of the
signed manifest;
4)
Within 30 dayn after the delivery, n~enda copy of the
manifest to each of the generator and
t-e—the Agency within
30 days of the date of delivery
and
5)
Retain
at the facility a copy of each manifest
for at least
three years
from the date of delivery.
b)
If
a facility receives from
a rail or water (bulk shipment)
transporter hazardous waste whichthat
is accompanied by a shipping
paper containing all the information required on the manifest
(excluding the U.S. EPA identification numbers, generator’s
certification and signatures)1, the owner or operator or 4ej~.
agent must:
1)
Sign and date each copy of the manifest or shipping paper
(if the manifest has not been received) to certify that the
hazardous waste covered by the manifest or shipping paper
was received;
2)
Note any
significant discrepancies1, -f-as defined in Section
725.172(a)-)-1, in the manifest or shipping paper
(if the
manifest has not been received)
on each copy of the manifest
or shipping paper;
CommentBOARD NOTE:
The Board doon not
intend that
the
owner
or operator of a facility whose procedures under Section
725.113(c)
include waste analysis mucitneed not perform that
analysis before signing the shipping paper and giving
it to
the transporter.
Section 725.172(b),
however, requires
reporting an unreconciled discrepancy discovered during
later analysis.
3)
Immediately give the rail or water (bulk shipment)
transporter
at least one copy of the manifest or shipping
paper
(if the manifest has not been received);
4)
Within
30 dayn after tho dclivory, n~enda copy of the
signed and dated manifest to the generator and to the Agency
within 30 days after the delivery however,
if the manifest
has not been received within 30 days after delivery,
the
owner or operator,
or his agent,
must send
a copy of the
shipping paper signed and dated to the generator;
and
CommentBOARD NOTE:
Cection35
Ill.
Adm. Code 722.123(c)
138
requires the generator to send three copies of the manifest
to the facility when hazardous waste
is sent by rail or
water (bulk shipment).
5)
Retain at the facility a copy of the manifest and shipping
paper
(if signed in lieu of the manifest at the time of
delivery)
for at least three years from the date of
delivery.
C)
Whenever a shipment of hazardous waste
is initiated from a
facility,
the owner or operator of that facility must comply with
the requirements of Part3S
Ill. Adm.
Code 722.
CommcntBOARD NOTE:
The provisions of Cection35 Ill. Adm. Code
722.134 are applicable to the on—site accumulation of hazardous
wastes by generators.
Therefore, the provisions of Cection35
Ill.
Adm.
Code 722.134 only apply only to owners or operators whethat
are shipping hazardous waste whichthat they generated at
that
facility.
(Source:
Amended at
19
Ill. Reg.
_______,
effective
_____________________
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,
storage1, or disposal at the facility as required
by Section 725.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,
725.3791, and 725.409 for
related requirements.
3)
Records and results of waste analysis,
waste determinations,
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,
725.9341,
and
725.963,
and
725.984
and
35
Ill.
Adm.
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);
5)
Records and results of inspections
as required by Sections
725.115(d)
(except these data need be kept only three
years);
6)
Monitoring,
testing1, or analytical data -a~-
139
action dat~whererequired by 725.Subpart
F or 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 through 725.404,
725.447,
725.477,
725.934(c) through
(f),
725.935,
725.963(d) through
(i)1, or 725.964,
725.989 through 725.991
BOARD
NOTE:
As required by Section 725.194, monitoring data
at disposal facilities must be kept throughout the poet—
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.
Adm.
Code
728.105,
a petition pursuant to 35
Ill. Adm. Code 728.1061,
or a certification under
35
Ill.
Adm.
Code 728.lO8r and the
applicable notice required of
a generator under
35 Ill. Adm.
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.
Adm. 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. Adm.
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.
Adm. Code
728.107 or 728.108, whichever
in applicable;
and
12)
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. Adm. Code
728.107, except for the manifest number,
and the
certification and demonstration,
if applicable,
required
under 35
Ill.
Adm. Code 728.107 or 728.108, whichever in
applicablo.~
13)
For an off-site storage facility,
a copy of the notice-, and
the certification and demonstration1, if applicable,
required
of the generator or the owner or operator under 35
Ill.
Adm.
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 demonstration1, if applicable,
required of
the generator or the owner or operator under
35
Ill.
Adm.
Code 728.107 or 728.108.
(Source:
Amended at
19
Ill.
Reg.
________,
effective
_____________________
140
Section 725.177
Additional Reports
In addition to submitting the annual report and unmanifested waste reports
described in Sections 725.175 and 725.176, the owner or operator shall also
report to the Agency:
a)
Releases,
fires1, and explosions1, as specified in Section
725.156(j);
b)
Groundwater contamination and monitoring
data1, as specified
in
Section 725.193 and 725.194;
c)
Facility closure1, as specified in Section 725.215; and
d)
As otherwise required by 725.Subparts AA1, and BB,
and CC.
(Source:
Amended at
19 Ill.
Reg.
________,
effective
______________________
SUBPART F: GROUNDWATER MONITORING
Section 725.192
Sampling and Analysis
a)
The owner or operator muntshall obtain and analyze samples from
the installed groundwater monitoring system.
The owner or
operator muctehall develop and follow a groundwater sampling and
analysis plan.
HeThe owner or operator muotshall keep this plan
at the facility.
The plan must include procedures and techniques
for:
1)
Sample collection;
2)
Sample preservation and shipment;
3)
Analytical procedures;
and
4)
Chain of custody control1,
CommcntBOARD
NOTE:
See “Procedures Manual For Groundwater
Monitoring At Solid Waste Disposal Facilities-,”
EPA 530/CW-61l, Auguot 1977 and “Methods for Chemical
Analysis of Water and Wastes-,-”1, EPA 600/4-79- 020, t~arch
l979incorporated by reference
in
35
Ill. Adm.
Code 720.111,
for discussions
of sampling and analysis procedures.
b)
The owner or operator muotshall determine the concentration or
value of the following parameters in groundwater samples in
accordance with paragraphosubsections
(C)
and
(d)
of thin
scctionbelow:
1)
Parameters characterizing the suitability of the groundwater
as
a drinking water supply,
as specified in Section
725.Appendix -~4-~Fç.
2)
Parameters extablishing groundwater quality-~-j.
A)
Chloride1,
B)
Iron1,
C)
Manganese1,
141
D)
Phenols1,
E)
Sodium~ and
F)
Sulfate1,
CommcntBOARD
NOTE:
These parameters are to be used as
a basis
for comparison in the event a groundwater
quality assessment
is required under Section
725.193(d).
3)
Parameters used as
indicators of groundwater contamination:
A)
pH1,
B)
Specific Conductance1,
C)
Total Organic Carbon,
and
D)
Total Organic Halogen1,
c)
Establishing background concentrations:
1)
For all monitoring wells, the owner or operator muntshall
establish initial background concentrations or values of all
parameters specified in paragrapheubsection
(b) of thin
occtionabove.
HeThe owner or operator muntshall
do this
quarterly for one year.
2)
For each of the indicator parameters specified in
paragrapheubsection (b)(3)
above, the owner or operator
shall obtain at least four replicate measurements muot be
obtained for each sample and determine the initial
background arithmetic mean and variance munt be determined
by pooling the replicate measurements for the respective
parameter concentrations or values in samples obtained from
upgradient wells during the first year.
d)
After the first year, the owner or operator shall sample all
monitoring wells munt be camplod and analyze the samples analyzed
with the following frequencies:
1)
Samples collected to establish groundwater quality must be
obtained and analyzed for the parameters specified in
paragraphsubsection (b)(2) of this seotionabove at
least
annually.
2)
Samples collected to indicate groundwater contamination must
be obtained and analyzed for the parameters specified
in
paragraphsubsection (b)(3)
of thin sectionabove at
least
semi—annually.
e)
The owner or operator shall determine the e~levationof the
groundwater surface at each monitoring well muot be determined
each time a sample
is obtained.
(Source:
Amended
at
19
Ill.
Reg.
________,
effective
_____________________
Section 725.194
Recordkeeping and Reporting
a)
Unless the groundwater is monitored to satisfy the requirements of
Section 725.193(d) (4),
the owner or operator muotshall:
142
1)
Keep records of the analyses required in Section 725.192(c)
and
(d),
the associated groundwater surface elevations
required in Section 725.192(e)1, and the evaluations required
in Section 725.193(b) throughout the active life of the
facility and1, for disposal facilities, also throughout the
post—closure care period an well and
2)
Report the following groundwater monitoring information to
the DircotorAgency:
A)
During the first year when initial background
concentrations are being established for the facility:
concentrations or values of the parameters listed in
Section 725.192(b) (1)
for each groundwater monitoring
well1, within
15 days after completing each quarterly
analysis.
The owner or operator muotshall
separately
identify for each monitoring well any parameters whose
concentration or value has been found to exceed the
maximum contaminant levels listed
in Section
725.Appendix ~-I-C.
B)
Annually:
concentrations or values of the parameters
listed
in Section 725.192(b) (3)
for each groundwater
monitoring well,
along with the required evaluations
for these parameters under Section 725.193(b).
The
owner or operator muotshall separately
identify any
significant differences from initial background found
in the upgradient wells,
in accordance with Section
725.193(c)(1).
During the active life of the
facility, the owner or operator shall submit this
information muct be nubmittod as part of the annual
report required under Section 725.175.
C)
As part of the annual report required under Section
725.175:
results of the evaluation of groundwater
surface elevations under Section 725.193(f)
and a
description of the response to the evaluation, where
applicable.
b)
If the groundwater
is monitored to satisfy the requirements of
Section 725.193(d) (4)1, the owner or operator muotshall:
1)
Keep records of the analyses and evaluations specified in
the
plan-,- whiohthat satisf-~ee~
the requirements of Section
725.193(d) (3) throughout the active life of the facility
and,
for disposal facilities,
also throughout the
post—closure care period an well
and
2)
Annually,
until final closure of the facility,
submit to the
DirectorAgency
a report
containing the results of 4~e~Q
groundwater quality assessment program whichthat includes,
but
is not limited to, the calculated
(or measured)
rate of
migration of hazardous waste or hazardous waste constituents
in the groundwater during the reporting period.
The owner
or operator shall submit tThis report munt be nubmitted as
part of the annual report required under Section 725.175.
(Source:
Amended at
19
Ill. Reg.
________,
effective
______
SUBPART
I:
USE AND MANAGEMENT OF CONTAINERS
143
Section 725.271
Condition of Containers
If a container holding hazardous waste is not in good condition or if
it
begins to leak,
the owner or operator muctshall transfer the hazardous waste
from this container to
a container that is in good condition or manage the
waste in some other way that
it complies with the requirements of this Part.
(Source:
Amended at
19 Ill. Reg.
_______,
effective
_____________________
Section
725.272
Compatibility of Waste with Container
The owner or operator muotahall use
a container made of or lined with
materials ~hichthat will not react with and are otherwise compatible with the
hazardous waste to be stored,
so that the ability of the container to contain
the waste is not impaired.
(Source:
Amended at
19
Ill. Reg.
_______,
effective
____________________
Section 725.274
Inspections
The owner or operator muntshall inspect areas where containers are stored at
least weekly,
looking for leaks and
for deterioration caused by corrosion or
other factors.
CommentBOARD
NOTE:
See Section 725.271 for remedial action required
if
deterioration or leaks are detected.
(Source:
Amended at
19
Ill.
Reg.
_______,
effective
_____________________-
Section 725.278
Air Emission Standards
The owner or operator shall manage all hazardous waste placed in a container
in accordance with the requirements of 724.Subpart
CC.
(Source:
Added at
19 Ill. Reg.
________,
effective
_____________________
SUBPART J: TANK SYSTEMS
Section 725.301
Generators
of
100 to 1000
kg/mo-T-
a)
The requirements of this Section apply to small quantity
generators ef-that generate more than 100 kg but less than 1000 kg
of hazardous waste in a calendar month,
that accumulate hazardous
waste in tanks for less than 180 days
(or 270 days
if the
generator must ship the waste greater than 200 miles),
and that do
not accumulate over 6,000 kg on—site at any time.
b)
~.gGeneratore of between 100 and 1000 kg/mo hazardous waste shall
comply with the following general operating requirements:
1)
Treatment or storage of hazardous waste in tanks must comply
with Section
725.117(b)--j.
2)
Hazardous wastes or treatment reagents must not be placed in
a tank
if they could cause the tank or
its inner liner to
rupture,
leak,
corrode1, or otherwise
fail before the end of
its intended
life-ri
3)
Uncovered tanks must be operated to ensure at least
60
centimeters
(2 feet)
of freeboard-, unless the tank is
equipped with
a containment structure
(e.g.1, dike or
144
trench),
a drainage control
system1, or a diversion structure
(e.g.,
standby tank)
with a capacity that equals or exceeds
the volume of the top 60 centimeters
(2
feet)
of the
tank-s-i.
and
4)
Where hazardous waste is continuously fed into a tank,
the
tank must be equipped with a means to stop this inflow
(e.g., waste feed cutoff system or by—pass system to a
stand-by tank).
BOARD
NOTE:
These systems are intended to be used in the
event of
a leak or overflow from the tank due to a system
failure
(e.g.,
a malfunction in the treatment process,
a
crack in the tank,
etc.).
C)
~~Generatore
of between 100 and 1000 kg/mo accumulating hazardous
waste
in tanks shall inspect, where present:
1)
Discharge control equipment (e.g., waste feed cutoff
systems, by—pass systems,
and drainage systems)
at least
once each operating day,
to ensure that
it
is
in good
working order;
2)
Data gathered from monitoring equipment
(e.g., pressure
and
temperature gauges)
at least once each operating day to
ensure that the tank is being operated according to its
design;
3)
The level of waste
in the tank at least once each operating
day to ensure compliance with subsection (b)(3) above
4)
The construction materials of the tank at least weekly to
detect corrosion or leaking
of fixtures or seams;
and
5)
The construction materials
of-1- and the area immediately
surrounding-, discharge confinement structures
(e.g., dikes)
at least weekly to detect erosion or obvious signs of
leakage
(e.g., wet
spots or dead vegetation).
BOARD NOTE:
As required by Section 725.115(c), the owner or
operator must remedy any deterioration or malfunction the
owner or operator finds.
d)
~.gGeneratore of between 100 and 1000 kg/mo accumulating hazardous
waste in tanks shall, upon closure of the facility, remove all
hazardous waste from tanks,
discharge control equipment and
discharge confinement structures.
BOARD
NOTE:
At
closure,
as throughout the operating period,
unless the owner or operator demonstrates,
in accordance with
35
Ill. Adm.
Code 72l.103(e~) or
(4e), that any solid waste removed
from the tank
is not a hazardous waste,
the owner or operator
becomes
a generator of hazardous waste and must manage it in
accordance with all applicable requirements of
35
Ill.
Adm. Code
722,
7231,
and 725.
e)
~Generatore
of between 100 and 1000 kg/mo shall comply with the
following special requirements for ignitable or reactive waste:
1)
Ignitable or reactive waste must not be placed in a tank-,
unless:
145
A)
The waste
is treated, rendered1, or mixed before or
immediately after placement in a tank so that;
i)
The resulting waste, mixture1, or dissolution of
material no longer meets the definition of
ignitable or reactive waste under 35 Ill.
Adm.
Code
721.121
or
721.123,
and
ii)
Section 725.117(b)
is complied with;—e*
B)
The waste
is stored or treated in such a way that
it
is
protected
from
any
material
or
conditions
that
may
cause
the
waste
to
ignite
or
react;
or
C)
The tank is used solely for emergencies1,
2)
The
owner
or
operator
of
a
facility
whichthat
treats
or
stores ignitable or reactive waste
in covered tanks shall
comply with the buffer zone requirements for tanks contained
in
Tables
2—1
through
2—6
of
the
National
Fire
Protection
Association’s “Flammable and Combustible Liquids Code,”
incorporated by reference in 35
Ill.
Adm.
Code
720.111.
f)
~gGeneratore
of between 100 and 1000 kg/mo shall comply with the
following special requirements for incompatible wastes:
1)
Incompatible wastes-, or incompatible wastes and materials
(see
Appendix
E
for
examples)
must
not
be
placed
in
the
same
tank-,- unless Section 725.117(b)
is
complied with.
2)
Hazardous waste must not be p1ace~in an unwashed tank
whiohthat previously held an incompatible waste or material-,
unless
Section 725.117(b)
is complied with.
(Source:
Amended
at
19
Ill.
Reg.
_______,
effective
_____________________
Section 725.302
Air Emission Standards
The owner or operator shall manage all hazardous waste placed
in
a tank in
accordance
with
the
requirements
of
724.Subparts
AA,
BB,
and
CC.
(Source:
Amended at
19
Ill. Reg.
________,
effective
______________________
SUBPART
K:
SURFACE IMPOUNDMENTS
Section
725.325
Waste
Analysis
and
Trial
Tests
In
addition
to
the
waste
analyses
required
by
Section
725.113,
whenever
a
surface
impoundment
is
to
be
used
to:
a)
Chemically
treat
a
hazardous
waste
whiohthat
is
substantially
different
from
waste
previously
treated
in
that
impoundment;
or
b)
Chemically treat hazardous waste with
a substantially different
process than and previously used in that
impoundment--1, the owner
or operator must,
before treating the different waste or using the
different
process:
1)
Conduct
waste
analyses
and
trial
treatment
tests
(e.g.,
bench
scale
or
pilot
plant
scale
tests);
or
146
2)
Obtain written, documented information e-~ similar
treatment of similar waste under similar operating
conditions--1, to show that this treatment will comply with
Section 725.117(b).
OommcntBOARD
NOTE:
As required by Section 725.1131, the
waste analyses plan must include analyses needed to comply
with Sections 725.329 and 725.330.
As required by Section
725.173, the owner or operator muntshall place the results
from each waste analysis and trial test,
or the documented
information in the operating record of the facility.
(Source:
Amended at
19
Ill. Reg.
,
effective
______________________
Section 725.331
Air Emission Standards
The owner or operator shall manage
all hazardous waste placed
in
a surface
impoundment
in accordance with the requirements of 724.Subpart CC.
(Source:
Added at
19 Ill. Reg.
________,
effective
______________________
SUBPART
L:
WASTE PILES
Section 725.352
Waste Analysis
a)
In addition to the waste analyses required by Section 725.1131, the
owner or operator muotshall analyze
a representative sample of
waste from each incoming movement before adding the waste to any
existing pile unless:
1)
The only wastes the facility receives whichthat are amenable
to piling are compatible with each other1, or
2)
The waste received
is compatible with the waste in the pile
to which
it
is to be added.
b)
The analysis conducted must be capable of differentiating between
the types of hazardous waste the owner or operator places in
piles1, so that mixing of
incompatible waste does not inadvertently
occur.
The analysis must include a visual comparison of color and
texture.
CommcntBOARD NOTE:
As required by Section 725.1131, the waste
analysis plan must include analyses needed to comply with Sections
725.356 and 725.357.
As required by Section 725.173, the owner
or operator must place the results of this analysis in the
operating record of the facility.
(Source:
Amended at
19
Ill. Reg.
________,
effective
______________________
SUBPART
N:
LAND TREATMENT
Section 725.378
Unsaturated
Zone (Zone of Aeration) Monitoring
a)
The owner or operator muntshall have in writing1, and muntshall
implement1, an unsaturated zone monitoring plan whichthat
is
designed to:
1)
Detect the vertical migration of hazardous waste and
hazardous waste constituents under the active portion of the
147
land treatment
facility1, and
2)
Provide information on the background concentrations
of the
hazardous waste and hazardous waste constitients
in similar
but untreated soil nearbyt~.~his
background monitoring
must be conducted before or in conjunction with the
monitoring required under paragraphsubsection
(a)(l)
of thin
cootionabove.
b)
The unsaturated zone monitoring plan must include,
at a minimum:
1)
Soil monitoring using soil cores1, and
2)
Soil—pore water monitoring using devices1, such as
lysimeters.
c)
To comply with paragrapheubsection
(a)(l) of thin occtionabove,
the owner or operator must demonstrate
in his unsaturated zone
monitoring plan that:
1)
The depth at which soil and soil—pore water samples are to
be taken is below the depth to which the waste
is
incorporated into the soil;
2)
The number of soil and soil—pore water samples to be taken
is based on the variability of:
A)
The hazardous waste constituents
(as identified in
Section 725.373(a)
and(b))
in the waste and in the
soil-1-1, and
B)
The soil
type-(-s-)-;
and
3)
The frequency and timing of soil and soil—pore water
sampling is based on the frequency,
time1, and rate of waste
application, proximity to ground water1, and soil
permeability.
d)
The owner or operator muotshall keep at the facility ~
unsaturated zone monitoring plan and the rationale used in
developing this plan.
e)
The owner or operator muntehall analyze the soil and soil—pore
water samples for the hazardous waste constituents that were found
in the waste during the waste analysis under Section 725.373(a)
and
(b).
CommcntBOARD NOTE:
As required by Section
725.1731,
the owner or
operator must place all data and information developed by the
owner or operator under this e~ectionmuot be placed in the
operating record of the facility.
(Source:
Amended at 19
Ill. Reg.
________,
effective
_____________________
SUBPART
P: THERMAL TREATMENT
Section 725.477
Monitoring and Inspections
The owner or operator muntehall conduct,
as
a minimum,
the following
monitoring and inspections when thermally treating hazardous waste:
148
a)
Existing instruments whichthat relate to temperature and emission
control
(if an emission control device is present) must be
monitored at least every 15 minutes.
Appropriate corrections to
maintain steady state or other appropriate thermal treatment
conditions must be made immediately either automatically or by the
operator.
Instruments whichthat relate to temperature and
emission control would normally include those measuring waste
feed,
auxiliary fuel feed,
treatment process temperature and
relevant process flow and level controls.
b)
The stack plume (emissions), where present, must be observed
visually at least hourly for normal appearance
(color and
opacity).
The operator must immediately make any indicated
operating corrections necessary to return any visible emissions to
their normal appearance.
C)
The complete thermal treatment process and associated equipment
(pumps,
valves,
conveyors, pipes,
etc.) must be inspected at
least
daily for
leaks,
spills
and fugitive emissions,
and all emergency
shutdown controls and system alarms must be checked to assure
proper operation.
(Source:
Amended at
19
Ill. Reg.
________,
effective
_____________________
SUBPART
Q:
CHEMICAL,
PHYSICAL AND BIOLOGICAL TREATMENT
Section 725.501
General Operating Requirements
a)
Chemical,
physical or biological treatment of hazardous waste must
comply with Section 725.117(b).
b)
Hazardous waste or treatment reagents must not be placed
in the
treatment process or equipment
if they could cause the treatment
process or equipment to rupture,
leak,
corrode1, or otherwise fail
before the end of its intended life.
C)
Where hazardous waste
is continuously fed into
a treatment process
or equipment, the process or equipment must be equipped with a
means to stop this inflow
(e.g.,
a waste feed cutoff system or
bypass system to a standby containment device).
CommentBOARD NOTE:
These systems are intended to be used
in the
event of
a malfunction in the treatment process or equipment.
(Source:
Amended at 19
Ill. Reg.
________,
effective
______________________-
Section 725.502
Waste Analysis and Trial Tests
a)
In addition to the waste
analysis required by Section 725.113,
paragraphsubsection
(b)
above applies whenever:
1)
A hazardous waste whichthat
is substantially different from
waste previously treated in
a treatment process or equipment
at the facility is to be treated in that process or
equipment1, or
2)
A substantially different process from any previously used
at the facility is to be used to chemically treat hazardous
waste.
b)
To show that this proposed treatment will meet all applicable
149
requirements of Section 725.501(a)
and
(b), the owner or operator
must,
before treating the different waste or using the different
process or equipment:
1)
Conduct waste analyses and trial treatment tests
(e.g.,
bench scale or pilot plant scale tests)i-1, or
2)
Obtain written, documented information on similar treatment
of similar waste under similar operating conditions.
CommontBOARD NOTE:
As required by Section 725.113, the
waste analysis plan must include analyses needed to comply
with Sections 725.505 and 725.506.
As required by Section
725.173, the owner or operator muatehall place the results
from each waste analysis and trial test,
or the documented
information,
in the operating record of the facility.
(Source:
Amended at 19 Ill.
Reg.
________,
effective
_____________________)
Section 725.503
Inspections
The owner operator of a treatment facility muntshall
inspect, where present:
a)
Discharge control and safety equipment
(e.g., waste feed cutoff
systems,
bypass systems, drainage systems1, and pressure relief
systems)
at least once each operating day to ensure that
it
is
in
good working order;
b)
Data gathered from monitoring equipment
(e.g., pressure
and
temperature gauges) at least once each operating day to ensure
that the treatment process or equipment
is being operated
according to its design;
c)
The construction materials of the treatment process or equipment
at
least weekly to detect
corrosion or leaking of fixtures or
seams;
and
d)
The construction materials of,
and the area immediately
surrounding,
discharge confinement structures
(e.g.,
dikes)
at
least weekly to detect erosion or obvious
signs of leakage
(e.g.,
wet spots or dead vegetation).
CommentBOARD NOTE:
As required by Section 725.115(c),
the owner
or operator must remedy any deterioration or malfunction hej~
finds.
(Source:
Amended at
19
Ill.
Reg.
,
effective
_____________________
Section 725.504
Closure
At closure,
all hazardous waste and hazardous waste residues must be removed
from treatment processes or equipment,
discharge control
equipment1, and
discharge
confinement structures.
CommcntBOARD NOTE:
At closure,
as throughout the operating period,
unless the
owner or operator can demonstrate,
in accordance with Seotion35
Ill.
Adm. Code
721.103(c) or
(d)1, that any solid waste removed from his treatment process or
equipment
is not
a hazardous waste, the owner or operator becomes
a generator
of hazardous waste and must manage
it
in accordance with all applicable
requirements of Partn35 Ill.
Adm. Code 722,
7231,
and 725.
(Source:
Amended at
19 Ill.
Reg.
________,
effective
______________________
150
Section 725.505
Special Requirements for Ignitable or Reactive Waste
Ignitable or reactive waste must not be placed
in
a treatment process or
equipment unless:
a)
The waste
is treated,
rendered or mixed before or immediately
after placement in the treatment process or equipment so that
1)
The resulting waste, mixture or dissolution of material no
longer meets the definition of ignitable or reactive waste
under Section 721.121 or 721.1231, and
2)
Section 725.117(b)
is complied with; or
b)
The waste is treated in such a way that it
is protected from any
material or conditions whiahthat may cause the waste to ignite or
react.
(Source:
Amended at
19
Ill. Reg.
________,
effective
______________________-
Section 725.506
Special Requirements for Incompatible Wastes
a)
An owner or operator shall not place i-I-ncompatible wastes or
incompatible wastes and materials (see Section
725.Appendix ~E for
examples) muot not be placed in the same treatment process or
equipment unless
it complies with Section 725.117(b)
in complied
with.
b)
An owner or operator shall not place hHazardous waste muot not be
placed in unwashed treatment equipment whichthat previously held
an incompatible waste or material, unless
it complies with Section
725.117(b)
in complied with.
(Source:
Amended at
19
Ill.
Reg.
,
effective
_____________________
SUBPART AA: AIR EMISSION STANDARDS FOR PROCESS VENTS
Section 725.933
Standards: Closed—vent Systems and Control Devices
a)
Compliance Required.
1)
Owners or operators of closed—vent
systems and control
devices used to comply with provisions of this Part shall
comply with the provisions of this Section.
2)
The owner or operator of an existing facility whethat cannot
install
a closed-vent system and control device to comply
with the provisions of this Subpart on the effective date
that the facility becomes subject to the provisions of
this
Subpart shall prepare an implementation schedule that
includes dates by which the closed—vent system and control
device will be installed and in operation.
The controls
must be installed as soon as possible,
but the
implementation schedule may allow up to 18 months after the
effective date that the facility becomes subject to this
Subpart for installation and startup.
All units that begin
operation after December 21,
1990,
must comply with the
rules immediately
(i.e., must have control devices installed
and operating on startup of the affected
unit); the 2-year
implementation schedule does not apply to these units.
151
b)
A control device
involving vapor recovery
(e.g.,
a condenser or
adsorber) must be designed and operated to recover the organic
vapors vented to
it with an efficiency of 95 weight percent or
greater unless the total organic emission limits
of Section
725.932(a)(l) for all affected process vents
is
attained at
an
efficiency less than 95 weight percent.
C)
An enclosed combustion device
(e.g.,
a vapor incinerator,
boiler1,
or process heater)
must be designed and operated to reduce the
organic emissions vented to it by 95 weight percent or greater; to
achieve a total organic compound concentration of 20 ppmv,
expressed as the sum of the actual compounds,
not carbon
equivalents, on a dry basis corrected to
3 percent oxygen;
or to
provide
a minimum residence time of 0.50 seconds at
a minimum
temperature of 760~C.
If
a boiler or process heater
is used as
the control device, then the vent stream must be introduced into
the flame combustion zone of the boiler or process heater.
d)
Flares
1)
A flare must be designed for and operated with no visible
emissions as determined by the methods specified in
subsection (e)(l)
below except for periods not to exceed a
total of
5 minutes during any
2 consecutive hours.
2)
A flare must be operated with
a flame present
at all times,
as determined by the methods specified in subsection
(f)(2)(c)
below.
3)
A flare must be used only if the net heating value of the
gas being combueted is 11.2 NJ/scm (300 Btu/scf) or greater
if the flare
is
steam—assisted or air—assistedt1, or
if the
net heating value of the gas being combusted
is 7.45 NJ/scm
(200 Btu/scf) or greater if the flare is nonassisted.
The
net heating value of the gas being combuated must be
determined by the methods specified in subsection
(e)(2)
below.
4)
Exit Velocity.
A)
A steam—assisted or nonassisted flare must be designed
for an~operated with an exit velocity,
as determined
by the methods specified in subsection
(e)(3)
below,
less than 18.3
rn/s
(60 ft/s), except as provided in
subsections
(d)(4)(B) and
(d)(4)(C)
below.
B)
A steam—assisted or nonassisted flare designed
for and
operated with an exit velocity,
as determined by the
methods specified in
subsection (e)(3)
below,
equal to
or greater than 18.3 m/s
(60 ft/s)
but less than 122
m/s
(400 ft/s)
is allowed if the net heating value of
the gas being combusted
is greater than 37.3 MJ/scm
(1000 Btu/scf).
C)
A steam—assisted or nonassisted flare designed
for and
operated with an exit velocity,
as determined by the
methods specified in subsection (e)(3)
below,
less
than the velocity, V as determined by the method
specified
in subsection
(e)(4) and less than 122 m/s
(400 ft/s)
is allowed.
5)
An air—assisted
flare must be designed and operated with an
152
exit velocity less than the velocity,
V as determined by the
method specified in subsection
(e)(5) below.
6)
A flare used to comply with this Section must be steam—
assisted,
air—assisted1, or nonassisted.
e)
Compliance determination and equations.
1)
Reference Method 22
in 40 CFR 60,
incorporated by reference
in
35
Ill.
Adm. Code 720.111, must be used to determine the
compliance of a flare with the visible emission provisions
of this Subpart.
The observation period
is 2 hours and must
be used according to Method 22.
2)
The net heating value of the gas being combusted in
a flare
must be calculated using the
following equation:
Hr=KXE C~xH1
H
—
K
SUM(Ci
Hi)
Where:
HT
is the net heating value of the sample in NJ/scm;
where the net enthalpy per mole of
of fgas
is based on
combustion at 25~C and 760 mm Hg, but the standard
temperature for determining the volume corrersponding
to
1 mole is 20° C.
K
=
1.74x101 E
7
(1/ppm)(g mel/scm) (MJ/kcal)
where
standard temperature for
(g mel/scm) 20~C.
SU~(Xi)EX~
means the sum of the values of X for each
component
i,
from i=l to
n.
C~ is the concentration of sample component
i in ppm
on
a wet basis,
as measured for organics by Reference
Method 18
in 40
CFR 60,
and for carbon monoxide, by
ASTM Dl946~Q, incorporated by reference in
35 Ill.
Adm.
Code 720.111.
H~1is the net heat of combustion of sample component
i,
kcal/gmol at 25~C and 760 mm Hg.
The heats of
combustion must be determined using ASTM D_2382~,
incorporated by reference
in
35 Ill. Adm. Code
720.111,
if published values are not available or
cannot be calculated.
3)
The actual
exit velocity of a flare must be determined by
dividing the volumetric flow rate
(in units of standard
temperature and pressure),
as determined by Reference
Methods 2,
2A,
2C,
or 2D
in 40 CFR
60,
incorporated by
reference in 35
111. Adm. Code 720.111,
as appropriate, by
the unobstructed
(free)
cross—sectional area of the flare
tip.
4)
The maximum allowed velocity
in
rn/s,
V for
a flare complying
with subsection
(d)(4)(C)
above must be determined by the
153
following equation:
HT+28.
8
Log13V~=
31.7
LOC(V)
—
(H
+
28.8)
/
31.7
Where:
means logarithm to the base 10
ET
is the net heating value as determined in
subsection
(e)(2)
above.
5)
The maximum allowed velocity
in m/s, V for an air—assisted
flare must be determined by the following equation:
tT=8
.706-t-O.7084H~
V
=
8.706
+
0.708411
Where:
HT is the net heating value as determined in
subsection
(e)(2)
above.
f)
The owner or operator shall monitor and inspect each control
device required to comply with this Section to ensure proper
operation and maintenance of the control device by implementing
the following requirements:
1)
Install, calibrate,
maintain1, and operate according to the
manufacturer’s specifications a flow indicator that provides
a record of vent stream flow from each affected process
vent
to the control device at least once every hour.
The flow
indicator sensor must be installed in the vent stream at the
nearest feasible point to the control device inlet but
before being combined with other vent streams.
2)
Install,
calibrate, maintain1, and operate according to the
manufacturer’s specifications a device to continuously
monitor control device operation as specified below:
A)
For
a thermal vapor incinerator,
a temperature
monitoring device equipped with a continuous recorder.
The device must have accuracy of
+~
1 percent of the
temperature being monitored
in ~C
or
+± 0.50
C,
whichever
is greater.
~Ihe temperature sensor must be
installed at
a location in the combustion chamber
downstream of the combustion zone.
B)
For
a catalytic vapor incinerator,
a temperature
monitoring device equipped with a continuous recorder.
The device must be capable of monitoring temperature
at two locations and have an accuracy of +~.1percent
of the temperature being monitored in C or
+±
0.5~.C,
whichever
is greater.
One temperature sensor must be
installed
in the vent stream at the nearest feasible
154
point to the catalyst bed inlet and a second
temperature sensor must be installed in the vent
stream at the nearest feasible point to the catalyst
bed outlet.
C)
For a flare,
a heat sensing monitoring device equipped
with a continuous recorder that indicates the
continuous ignition of the pilot flame.
D)
For a boiler or process heater having a design heat
input capacity less than 44 NW,
a temperature
monitoring device equipped with
a continuous recorder.
The device must have an accuracy of
+±
1 percent of
the temperature being monitored in °C or
4±
0.5°C,
whichever is greater.
The temperature sensor must be
installed at a location
in the furnace downstream of
the combustion zone.
E)
For
a boiler or process heater having
a design heat
input capacity greater than or equal
to 44 MW,
a
monitoring device equipped with a continuous recorder
to measure
e—parameter-(-s-)- that indicates good
combustion operating practices are being used.
F)
For
a condenser, either:
i)
A monitoring device equipped with
a continuous
recorder to measure the concentration level of
the organic compounds in the exhaust vent stream
from the condenser;
or
ii)
A temperature monitoring device equipped with
a
continuous recorder.
The device must be capable
of monitoring temperature
at two locations and
have an accuracy of
+~
1 percent of the
temperature being monitored in ~C
or
+~
0.5~C,
whichever is greater.
One temperature sensor
must be installed at
a location
in the exhaust
vent stream from the condenser, and
a second
temperature sensor must be installed at
a
location in the coolant
fluid exiting the
condenser.
G)
For a carbon adsorption system such as
a fixed—bed
carbon adsorber that regenerates the carbon bed
directly in the control device,
either:
i)
A monitoring device equipped with a continuous
recorder to measure the concentration level of
the organic compounds in the exhaust vent stream
from the carbon bed; or
ii)
A monitoring device equipped with a continuous
recorder to measure
a parameter that indicates
the carbon bed is regenerated on
a regular,
predetermined time cycle.
3)
Inspect the readings
from each monitoring device required by
subsection (f)(l)
and j~j.(2) above at least once each
operating day to check control device operation and,
if
necessary,
immediately implement the corrective measures
necessary to ensure the control device operates
in
155
compliance with the requirements of
this Section.
g)
An owner or operator using a carbon adsorption system such as a
fixed—bed carbon adsorber that regenerates the carbon bed directly
onsite
in the control device shall replace the existing carbon in
the control device with fresh carbon at
a regular, predetermined
time interval that is no longer than the carbon service life
established as
a requirement of Section 725.935(b) (4) (C) (vi).
h)
An owner or operator using a carbon adsorption system1, such as
a
carbon canister1, that does not regenerate the carbon bed directly
onsite in the control device shall replace the existing carbon in
the control device with
fresh carbon on a regular basis by using
one of the following procedures:
1)
Monitor the concentration level of the organic compounds
in
the exhaust vent stream from the carbon adsorption system on
a regular schedule, and replace the existing carbon with
fresh carbon immediately when carbon breakthrough
is
indicated.
The monitoring frequency must be daily or at an
interval no greater than 20 percent of the time required to
consume the total carbon working capacity established as
a
requirement
of Section 725.935(b)(4) (C) (vii), whichever
is
longer.
2)
Replace the existing carbon with fresh carbon at
a regular,
predetermined time interval that
is
less than the design
carbon replacement interval established as a requirement of
Section 725.935(b) (4) (C) (vii).
i)
An owner or operator of an affected facility seeking to
comply
with the provisions of this Part by using
a control device other
than a thermal vapor incinerator, catalytic vapor
incinerator,
flare,
boiler, process heater,
condenser1, or carbon adsorption
system is required to develop documentation including sufficient
information to describe the control device operation and identify
the process parameter or parameters that indicate proper operation
and maintenance of the control device.
j)
Closed vent systems.
1)
Closed-vent
systems must be designed for and operated with
no detectable emissions,
as indicated by an instrument
reading of less than 500 ppm above background and by visual
inspections, as determined by the methods
specified at
Section 725.934(b).
2)
Closed—vent systems must be monitored to determine
compliance with this Section during the initial leak
detection monitoring, which must be conducted by the date
that the facility becomes subject to the provisions of this
Section annually,
and at other times as specified by the
Agency pursuant to Section 725.930(c).
For the annual
leak
detection monitoring after the initial
leak detection
monitoring,
the owner or operator
is not required to monitor
those closed—vent
system components that continuously
operate in vacuum service or those closed—vent system
joints,
seams,
or other connections that
are permanently or
semi—permanently sealed
(e.g.,
a welded
joint between two
sections of metal pipe or
a bolted and gasketed pipe
flange).
156
3)
Detectable emissions, as
indicated by an instrument reading
greater than 500 ppm and visual
inspections, must be
controlled as soon as practicable,
but not later than
15
calendar days after the emission is detected.
4)
A first attempt at repair must be made no later than
5
calendar days after the emission is detected.-s-
k)
Closed—vent systems and control devices used to comply with
provisions of this Subpart must be operated at all times when
emissions may be vented to them.
fl
The owner or operator using
a carbon adsorption system shall
document that all carbon removed from the control device
is
managed in one of the following manners:
fl
It
is regenerated or
reactivated in a thermal treatment unit
that
is permitted under
35
Ill. Adm.
Code 724.Subpart X or
725.Subpart P
~
It
is incinerated by a process that
is permitted under 35
Ill. Adm.
Code 724.Subpart 0 or 725.Subpart
0; or
~j.
It
is burned in
a boiler or industrial furnace that
is
permitted under
35
Ill.
Adm. Code 726.Subpart
H.
(Source:
Amended at
19
Ill.
Reg.
_______,
effective
_____________________
SUBPART BB: AIR EMISSION STANDARDS FOR EQUIPMENT
LEAKS
Section 725.963
Test Methods and Procedures
a)
Each owner or operator subject to the provisions of this Subpart
shall comply with the test methods and procedures requirements
provided
in this Section.
b)
Leak detection monitoring,
as required in Sections 725.952 through
725.962, must comply with the following requirements:
1)
Monitoring must comply with Reference Method 21 in 40 CFR
60,
incorporated by reference in 35
Ill.
Adm. Code 720.111.
2)
The detection instrument must meet the performance criteria
of Reference Method 21.
3)
The
instrument must be calibrated before use on each day of
its use by the procedures specified in Reference Method 21.
4)
Calibration gases must be:
A)
Zero air
(less than 10 ppm of hydrocarbon in air).
B)
A mixture of methane or n-hexane and air
at
a
concentration
of approximately,
but less than1, 10,000
ppm methane or n-hexane.
5)
The instrument probe must be traversed around all potential
leak
interfaces as close to the interface as possible as
described in Reference Method 21.
C)
When equipment
is tested for compliance with no detectable
157
emissions, as required in Sections 725.952(e),
725.953(i),
725.9541, and 725.957(f),
the test must comply with the following
requirements:
1)
The requirements of subsections (b)(1) through
j~j.(4)
above
apply.
2)
The background level must be determined as set forth in
Reference Method
21.
3)
The instrument
probe must be traversed around all potential
leak interfaces as close to the interface as possible
as
described in Reference Method 21.
4)
This arithmetic difference between the maximum concentration
indicated by the instrument and the background level
is
compared with 500 ppm for determinifig compliance.
d)
In accordance with the waste analysis plan required by Section
725.113(b),
an owner or operator of a facility shall determine,
for each piece of equipment, whether the equipment contains or
contacts a hazardous waste with organic concentration that equals
or exceeds
10 percent by weight using the following:
1)
Methods described in ASTM Methods D 2267~.~,E 168-88,
E
169—87,
E
l68,or
E 260—85, incorporated by reference in 35
Ill.
Adni. Code 720.111;
2)
Method 9060 or 8240 of SW—846,
incorporated by reference in
35
Ill. Adm.
Code 720.111; or
3)
Application of the knowledge
of the nature of the hazardous
wastestream or the process by which it was produced.
Documentation of a waste determination by knowledge
is
required.
Examples of documentation that must be used to
support
a determination under this provision include
production process information documenting that no organic
compounds are used,
information that the waste
is generated
by a process that
is
identical to a process at the same or
another facility that has previously been demonstrated by
direct measurement to have
a total organic content less than
10 percent,
or prior speciation analysis results on the same
wastestream where
it
is also documented that no process
changes have occurred since that analysis that could affect
the waste total organic concentration.
e)
If an owner or operator determines that
a piece of equipment
contains or contacts
a hazardous waste with organic concentrations
at least 10 percent by weight, the determination can be revised
only after following the procedures
in subsection
(d)(1) or j~j(2)
above
-
f)
When an owner or operator and the Agency do not agree on whether
a
piece of equipment contains or contacts
a hazardous waste with
organic concentrations
at
least
10 percent by weight, the
procedures in subsection
(d)(1)
or .~j(2)above must be used to
resolve the dispute.
g)
Samples used in determining the percent organic content must be
representative of the highest total
organic content hazardous
waste that is expected to be contained in or contact the
equipment.
158
h)
To determine
if pumps or valves
are in light liquid service,
the
vapor pressures of constituents must either be obtained from
standard reference texts or be determined by ASTM D—_2879-86,
incorporated by
reference
in 35
Ill. Adm. Code 720.111.
i)
Performance tests to determine
if
a control device achieves 95
weight percent organic emission reduction must comply with the
procedures of Section 725.934(c)(1) through j~).(4).
(Source:
Amended
at
19
Ill.
Reg.
________,
effective
_____________________
SUBPART CC:
AIR EMISSION STANDARDS FOR TANKS,
SURFACE IMPOUNDMENTS~AND CONTAINERS
Section 725.980
Applicability
~j.
The requirements of this Subpart apply, effective December
6,
1995,
to owners and operators of all facilities that treat,
store,
or dispose of hazardous waste
in tanks,
surface impoundments,
or
containers subiect to either 725.Subparts
I.
3,
or K.
excePt as
Section 725.101 and subsection
(b) below provide otherwise.
BOARD NOTE:
U.S. EPA adopted these regulations at
59
Fed.
Req.
62896
(Dec.
6,
1994), effective June
6,
1995.
At
60
Fed.
Req.
26828
(MaY 19,
1995), U.S. EPA delayed the effective date until
December
6,
1995.
If action by
U.S. EPA or a decision
of
a
federal court changes the effectiveness of these regulations, the
Board does not
intend that the 725.Subpart
CC rules be enforceable
to the extent that they become more stringent that the federal
regulations upon which they are based.
~).
The requirements of this Subpart do not apply to the following
waste management units
at
the
facility:
fl
~ waste management unit that holds hazardous waste placed
in
the unit before December
6,
1995 and in which no hazardous
waste
is
added to the unit on or after this date.
2.).
A container that has
a design capacity
less than or
equal
to
0.1 m3
(3.5 ft~or 26.4 gal).
~j.
A tank in which an owner or operator has stopped adding
hazardous waste and the owner or operator has begun
implementing or completed closure Pursuant to an approved
closure plan.
4.).
A surface impoundment
in which an owner or operator has
stopped adding hazardous waste (except to implement an
approved closure plan)
and the owner or operator has begun
implementing or completed closure Pursuant to an approved
closure plan.
~J.
A waste management unit that
is used solely for on—site
treatment or storage of hazardous waste that
is generated as
the result pf implementing remedial activities required
pursuant to the Act or Board regulations or under the
corrective action authorities of RCRA sections 3004(u),
3004(v)
or 3008(h); CERCLA authorities; or similar federal
or state authorities.
tj~c~t-~ n1,r~~r,Qm~nt-
nrl
t~th~it~
~ ~
ii,~~r1
c-~r~1
~1
‘i
fr~r
f~h~
159
management of radioactive mixed waste in accordance with all
applicable regulations under the authority of the Atomic
Energy Act
(42 U.S.C.
2011 et seq.)
and the Nuclear Waste
Policy Act.
~J
For the owner and operator of a facility subject to this
Subpart
who has received
a final RCRA permit prior to December
6,
1995,
the following requirements apply:
jj.
The requirements of
35
Ill. Adm. Code 724.Subpart CC must be
incorporated into the permit when the permit
is reissued,
renewed,
or modified in accordance with the requirements of
35
Ill. Adm.
Code 703 and 705.
~j.
Until the date when the permit
is reissued,
renewed,
or
modified in accordance with the requirements of
35
IlL. Mm.
Code 703 and 705, the owner and operator
is subject to the
requirements of this Subpart.
(Source:
Added at
19
Ill. Reg.
_______,
effective
_____________________
Section 725.981
Definitions
As used in this Subpart and
in
35
Ill. Adm.
Code
724,
all terms
not defined
herein shall have the meaning given to them
in the Act
and
35 Ill. Adm.
Code
720 through 726.
“Average volatile organic concentration”
or “average VO
concentration” means the mass—weighted average volatile organic
concentration of
a hazardous waste, as determined in accordance
with the requirements of Section 725.984.
“Cover” means
a device or system that is placed on or over a
hazardous waste such that the entire hazardous waste surface area
is enclosed and sealed to reduce air emissions to the atmosphere.
A cover may have openings such
as access hatches, sampling ports,
and gauge wells that are necessary for operation,
inspection,
maintenance, or repair of the unit on which the cover
is installed
provided that each opening is closed and sealed when not
in use.
Examples of covers include a fixed roof installed on a tank,
a
floating membrane cover installed on
a surface impoundment,
a lid
installed on
a drum, or an enclosure
in which an open container
is
placed during waste treatment.
“External floating roof” means a pontoon or double—deck type
floating roof
that rests on the
surface of
a hazardous waste being
managed in
a tank that has no fixed roof.
“Fixed roof” means a rigid cover that is
installed
in
a stationary
position so that
it does not move with fluctuations
in the level
of the hazardous waste placed in
a tank.
“Floating membrane cover” means a cover consisting of
a synthetic
flexible membrane material that rests upon and is supported by the
hazardous waste being managed
in a surface impoundment.
“Floating roof” means
a pontoon—type or double—deck—type cover
that rests upon and
is supported by the hazardous waste being
managed in
a tank, and is equipped with a closure seal or seals to
close the space between the cover edge and the tank wall.
“Internal floating roof” means a floating roof that rests or
160
floats on the surface
(but not necessarily
in complete contact
with it)
of
a hazardous waste being managed in a tank that has a
fixed
roof.
“Liquid—mounted seal” means a foam or liquid-filled primary seal
mounted in contact with the hazardous waste between the tank wall
and the floating roof,
continuously around the circumference of
the tank.
“Maximum organic vapor pressure” means the equilibrium partial
pressure exerted by the hazardous waste contained
in
a tank,
determined at the temperature equal to either:
The local maximum monthly average temperature as reported by
the National Weather Service, when the hazardous waste
is
stored_or_treated
at ambient temperature, or
The highest calendar—month average temperature
of the
hazardous waste,
when the hazardous waste
is
stored at
temperatures above the ambient temperature
or when the
hazardous waste
is stored or treated at temperatures below
the ambient temperature.
“No detectable organic emissions” means no escape of organics from
a device or system to the atmosphere,
as determined:
By an instrument reading less than 500 parts per million by
volume
(ppmv) above the background level at each joint,
fitting,
and seal, when measured in accordance with the
requirements of Method
21
in 40 CFR 60.
Appendix A,
and
By no visible openings or defects in the device or system
such as rips,
tears,
or gaps.
“Point of waste origination” means
as
follows:
When the facility owner or operator
is the generator of the
hazardous waste,
the “point of waste origination” means the
Point where a solid waste produced by a system,
process,
or
waste management unit
is determined to be a hazardous waste,
as defined
in 35
Ill. Adm. Code 721.
BOARD NOTE:
In this case,
this term
is being used in
a
manner similar to the use
of the term “point of generation”
in air standards established for waste management operations
under authority of the
federal Clean Air Act in 40 CFR 60,
61,
and
63.
When the facility owner and operator are not the generator
of the hazardous waste,
“point of waste origination” means
the point where the owner or operator accepts delivery or
takes possession of the hazardous waste.
“Point of waste treatment” means the Point where
a hazardous waste
exits a waste management unit used to destroy,
degrade,
or remove
organics in the hazardous waste.
“Vapor—mounted seal”
means
a foam—filled primary seal mounted
continuously around the circumference of the tank so that there is
an annular vapor space underneath the seal.
The annular vapor
space is bounded by the bottom of the primary seal, the tank wall,
the hazardous waste surface,
and the floatina roof.
161
“Volatile organic concentration” or “VO concentration’s means the
fraction by weight of organic compounds
in a hazardous waste
expressed in terms of parts per million
(ppmw),
as determined by
direct measurement, using Method 25D, or by knowledge of the
waste,
in accordance with the requirements of Section 725.984.
“Waste determination” means performing all applicable procedures
in accordance with the requirements of Section 725.984 to
determine whether
a hazardous waste meets standards specified in
this Subpart.
Examples of a waste determination include
performing the procedures in accordance with the requirements of
Section 725.984 to determine the average
‘10
concentration of a
hazardous waste
at the point of waste origination, determining the
average VO concentration of a hazardous waste at the point of
waste treatment and comparing the results to the exit
concentration limit specified for the process used to treat the
hazardous waste,
determining the organic reduction efficiency and
the_organic biodegradation efficiency for a biological process
used to treat
a hazardous waste and comparing the results to the
applicable standards,
or determining the maximum volatile organic
vapor pressure for a hazardous waste
in
a tank and comparing the
results to the applicable
standards.
‘Waste stabilization process” means any physical or chemical
process used to either reduce the mobility of hazardous
constituents
in
a hazardous waste or eliminate
free liquids as
determined by Test Method 9095
(Paint Filter Liquids Test)
in
“Test Methods for Evaluating Solid Waste, Physical/Chemical
Methods”,
incorporated by reference in Section
720.111.
A waste
stabilization process includes mixing the hazardous waste with
binders or other materials and curing the resulting hazardous
waste and binder mixture.
Other synonymous terms used to refer to
this process are “waste fixation”
or “waste solidification”.
(Source:
Added
at
19
Ill. Reg.
________,
effective
______________________
Section 725.982
Schedule for Implementation of Air Emission Standards
~j.
Owners
or operators of facilities existing on December
6,
1995 and
subject to 725.Subparts
I,
3,
and K shall meet the
following
requirements:
fl
The owner or operator shall
install and begin operation of
all control
equipment
required
by this Subpart by December
6,
1995,
except
as provided
in subsection
(a)(2)
below.
21
When control equipment required by this Subpart cannot be
installed and in operation by December
6,
1995,
the owner or
operator shall:
~j
Install and begin operation of the control equipment
as
soon as possible, but
in no case later than
December
8,
1997.
~j
Prepare an implementation schedule that includes the
following information:
specific calendar dates for
award of contracts or issuance of purchase orders for
the control equipment,
initiation of on—site
installation of the control equipment,
completion of
the control equipment installation,
and performance of
any testing to demonstrate that the installed
equipment meets the applicable standards of this
162
Subpart.
~.
For facilities subject to the recordkeeping
requirements of Section 725.173, the owner or operator
shall enter the implementation schedule specified
in
subsection
(a)(2)(B) above
in the operating record no
later than December
6,
1995.
pj.
For facilities not subject to Section 725.173 above,
the owner or operator shall enter the implementation
schedule
specified in subsection
(a)(2)(B)
of this
section
in a permanent, readily available file located
at the facility no later than December
6,
1995.
~J.
An owner or operator of facilities
in existence on the effective
date of statutory or regulatory amendments under the Act that
render the facility subject to 725.Subparts
I,
3, or K shall meet
the following requirements:
jj
The owner or operator shall install and begin operation of
all control equipment required by this Subpart by the
effective date of the amendment, except as provided
in
subsection
(b)(2) below.
21
When control equipment required by this Subpart cannot be
installed and begin operation by the effective date of the
amendment,
the owner or operator shall:
~j.
Install and operate the control equipment as soon as
possible, but in no case later than 30 months after
the effective date of the amendment.
~j.
For facilities subject to the recordkeepinq
requirements of Section 725.173,
enter and maintain
the implementation schedule specified
in subsection
(a)(2)(B)
above
in the operating record no later than
the effective date of the amendment, or
~j.
For facilities not subject to Section 725.173, the owner or
operator shall enter and maintain the implementation
schedule specified in subsection (aU2)(B)
above in
a
permanent, readily available file,
located at the facility
site,
no later than the effective date of the amendment.
2.).
The Agency may elect to extend the implementation date for control
eaui~mentat
a facility,
on a case by case basis,
to
a date later
than December
8,
1997:
fl.
When special circumstances that are beyond the facility
owner’s or operator’s control delay installation or
operation of control equipment,
and
2.).
The owner or operator has made all reasonable and prudent
attempts to comply with the requirements of this Subpart.
(Source:
Added at 19
Ill.
Reg.
________,
effective
_____________________
Section 725.983
Standards:
General
~j.
This Section applies to the management of hazardous waste in
tanks,
surface impoundments,
and containers subject to this
Subpart.
163
~j.
The owner or operator shall control
air emissions from each waste
management unit in accordance with standards specified in Sections
725.985 through Section 725.988, as applicable to the waste
management unit,
except
as provided for
in subsection
(c)
below.
91
A waste management unit
is exempted from standards specified in
Section 725.985 through Section 725.988, provided that all
hazardous waste placed
in the waste management unit is determined
by the owner or
operator
to meet either of the following
conditions:
fl
The average VO concentration of the hazardous waste at the
point of waste origination
is
less than 100 parts per
million by weight (ppmw).
The average VO concentration must
be determined by the procedures specified in Section
725.984(a).
21
The organic content
of the hazardous waste has been reduced
by
art
organic destruction or removal process that achieves
any one of the following conditions:
~j.
The process removes or destroys the organics contained
in the hazardous waste to such a level that the
average VO concentration of the hazardous waste at the
point of waste treatment
is less than the exit
concentration limit
(C,) established for the process.
The average VO concentration of the hazardous waste at
the point of waste treatment and the exit
concentration limit for the process must be determined
using the procedures specified in Section 725.984(b).
~J
The process removes or destroys the organics contained
in the hazardous waste to such a level that the
organic reduction efficiency
(Ri
for the process
is
equal
to or greater than 95 percent,
and the average
VO concentration
of the hazardous waste at the point
of waste treatment
is less than 50 ppmw.
The organic
reduction efficiency for the process and the average
VO concentration of the hazardous waste at the point
of waste treatment must
be determined using the
procedures specified in Section 725.984(b).
~j
The process removes or destroys the organics contained
in the hazardous waste to such a level that the actual
organic mass removal rate
(MR)
for the process
is
greater than the required organic mass removal rate
(RJ4R) established for the process.
The required
organic mass removal rate and the actual organic mass
removal
rate for the process must be determined using
the procedures
specified in Section 725.984(b).
QJ.
The process
is a biological process that destroys or
degrades the organics contained in the hazardous waste
so that
either of the following conditions
is met:
.jj
The organic reduction efficiency
(RI
for the
process is equal to or greater than 95 percent,
and the organic biodegradation efficiency (R~J
for the process is equal to or greater than 95
percent.
The organic reduction efficiency and
the organic biodegradation efficiency for the
process must be determined in accordance with
164
the procedures specified in Section 725.984(b).
Lii
The total
actual organic mass biodegradation
rate
(MR~J
for all hazardous waste treated
by
the process
is equal to or greater than the
required organic mass removal rate
(RMR).
The
required organic mass removal rate and the
actual organic mass biodegradation rate for the
process must be determined using the procedures
sDecified in Section 725.984(b).
~j.
The process is one that removes or destroys the
organics contained in the hazardous waste and meets
all of the following conditions:
j).
All of the materials entering the process are
hazardous wastes.
jj).
From the point
of waste origination through the
point where the hazardous waste enters the
process,
the hazardous waste
is continuously
managed in waste management units that use air
emission controls
in accordance with the
standards specified
in Section 725.985 through
Section
725.988,
as
applicable to the waste
management unit.
iii)
The average VO concentration of the hazardous
waste at the point of waste treatment
is less
than the lowest average VO concentration at the
ppint
of waste origination determined
for each
of
the individual hazardous waste streams
entering the process or 100 ppmw, whichever
value
is lower.
The average VO concentration of
each individual hazardous waste stream
at the
point of waste origination must be determined
using the procedure specified in Section
725.984(a).
The average VO concentration of the
hazardous waste at the point of waste treatment
must be determined using the procedure specified
in Section 725.984(b).
fi
A hazardous waste incinerator for which the owner or
operator has either:
Jj.
Been issued a final Permit under
35
Ill. Adm.
Code 703 and
705,
and the owner or operator
designs and operates the unit
in accordance with
the requirements of 35
Ill. Adm. Code
724.Subpart
0; or
LjJ.
The owner or operator has certified compliance
for the unit with the interim status
requirements of 725.Subpart
0.
Q~j
A boiler or industrial furnace for which the owner or
operator has either:
jj.
Been iaeuad a final permit under
35
Ill. Adm.
Code 703
and
705,
and the owner or operator
designs and operates the unit in accordance with
the reguirements of 35
Ill.
Adrn.
Code
165
726.Subpart H,
or
jjJ
The owner or operator has certified compliance
for the unit with the interim status
requirements of 35
Iii.. Adm. Code 726.Subpart H.
~j
When
a process
is used for the purpose of treating a hazardous
waste to meet one of the sets of conditions specified in
subsections
(c)(2)(A) through
(c)(2)(E)
above, each material
removed from or exiting the process that
is not
a hazardous waste
but which has an average VO concentration equal to or greater than
100 ppmw must be managed in a waste management unit in accordance
with the requirements
of subsection
(b)
above.
~j
The Agency may at any time perform or request that the owner or
operator perform a waste determination for
a hazardous waste
managed in a tank.
surface impoundment, or container that
is
exempted from using air emission controls under the provisions of
this Section as follows:
fl
The waste determination for average VO concentration of
a
hazardous waste
at the point of waste origination must be
performed using direct measurement
in accordance with the
applicable requirements of Section 725.984(a).
The waste
determination for a hazardous waste at the point of waste
treatment must be performed
in
accordance with the
an~licablerequirements of Section 725.984(b).
2.).
Where the owner or operator
is
requested to perform the
waste determination,
the Agency may elect to have an
authorized representative observe the collection of the
hazardous waste samples used for the analysis.
~J.
Where the results of the waste determination performed or
requested by the Agency do not agree with the results of a
waste determination performed by the owner or operator using
knowledge of the waste,
then the results of the waste
determination performed
in accordance with the requirements
of subsection
(e)(1) above must be used to establish
compliance with the requirements of this Subpart.
4.).
Where the owner or operator has used an averaging period
greater than one hour for determining the average VO
concentration of a hazardous waste at the point of waste
origination,
the Agency may elect to establish compliance
with this Subpart by performing or requesting that the owner
or operator perform a waste determination using direct
measurement, based on waste
samples collected within
a
1—
hour period as
follows:
i.).
The average VO concentration of the hazardous waste at
the point of waste origination must be determined by
direct measurement in accordance with the reguirements
of Section 725.984(a).
~j
Results of the waste determination performed or
requested by the Agency showing that the average
‘10
concentration of the hazardous waste at the point of
waste origination
is equal to or greater than 100 ppmw
shall constitute noncompliance with this Subpart,
except in a case as provided for
in subsection
(e)(4)(C)
below.
Where the average VO concentration of the hazardous
waste
at the point of waste origination previously has
been determined by the owner or operator using an
averaging period greater than one hour to be less than
100 ppmw but because of normal operating process
variations the VO concentration of the hazardous waste
determined by direct measurement for any given 1—hour
period may be equal to or greater than 100 ppmw,
information that was used by the owner or operator to
determine the average VO concentration of the
hazardous waste (e.g.,
test results, measurements,
calculations, and other documentation) and recorded in
the facility records
in accordance with the
requirements
of Sections 725.984(a)
and 725.990 must
be considered by the Agency together with the results
of the waste determination performed or requested by
the Agency in establishing compliance with this
Subpart.
(Source:
Added at
19
Ill. Reg.
________,
effective
______________________
Section 725.984
Waste Determination Procedures
~j
Waste determination procedure for volatile organic
(VO)
concentration of a hazardous waste at the point of waste
origination.
11
An owner or operator shall determine the average VO
concentration at the point of waste origination for each
hazardous waste placed
in a waste management unit exempted
under the provisions of Section 725.983(c)(l)
from using air
emission controls
in accordance with standards specified
in
Section 725.985 through Section 725.988,
as applicable to
the waste management unit.
2.).
When the facility owner or operator
is the generator of the
hazardous waste, the owner or operator shall determine the
average VO concentration of the hazardous waste using either
direct measurement,
as specified in subsection
(al(S)
below,
or knowledge of the waste,
as specified in subsection
(a)(6)
below,
for each hazardous waste generated as
follows:
~j
When the hazardous waste is generated as part of
a
continuous process, the owner or operator shall:
fl
Perform an initial waste determination of the
average VO concentration of the waste stream
before the first time any portion of the
material in the waste stream
is placed in a
waste management unit subject to this Subpart
and thereafter update the information used for
the waste determination
at least once every
12
months following the date of the initial waste
determination;
and
LU.
Perform
a new waste determination whenever
changes to the source generating the waste
stream are reasonably likely to cause the
average VO concentration of
the hazardous waste
to increase to a level that
is equal to or
greater than the applicable VO concentration
limits specified
in Section 725.983.
91
166
167
~j.
When the hazardous waste
is generated as part of
a
batch process that
is performed repeatedly but not
necessarily continuously, the owner or operator shall:
ii.
Perform an initial waste determination of the
average VO concentration for one or more
representative waste batches generated by the
process,
before the first time any portion of
the material
in the batches
is Placed
~rt
a waste
management unit subject to this Subpart,
and
thereafter update the information used for the
waste determination at least once every 12
months following the date of the initial waste
determination; and
LjI
Perform a new waste determination whenever
changes to the process generating the waste
batches are reasonably likely to cause the
average
‘10 concentration of the hazardous waste
to increase to
a level that is
equal to or
greater than the applicable VO concentration
limits specified
in Section 725.983.
~J.
When the facility owner and operator
is not the generator of
the hazardous waste, the owner or operator shall determine
the average VO concentration of the hazardous waste using
either direct measurement,
as specified in subsection
(al(S)
below,
or knowledge of the waste,
as specified
in subsection
(a)(6)
below,
for each hazardous waste entering the facility
as follows:
~j.
When the hazardous waste enters the facility as a
continuous flow of material through a pipeline or
other means
(e.g., wastewater stream), the owner or
operator shall:
Li.
Perform an initial waste determination of the
waste stream before the first time any portion
of the material
in the waste stream
is placed in
a waste management unit subject to this Subpart,
and thereafter update the information used for
the waste determination
at
least once every
12
months following the date of the initial waste
determination;
and
jjj.
Perform a new waste determination whenever
changes to the source generating the waste
stream are reasonably likely to cause the
average VO concentration of the hazardous waste
to increase to
a level that
is equal to or
greater than the applicable VO concentration
limits specified in Section 725.983.
~J
When the hazardous waste enters the facility in a
container, the owner or operator shall perform a waste
determination
for the material held
in each container.
4.).
Where the average VO concentration of the hazardous waste
is
determined by the owner or operator to be less than 100
ppmw, but because of normal operating variations in the
source
or
process
generating
the
hazardous
waste
the
VO
concentration of the hazardous waste may be equal to or
168
greater than 100
ppmw
at any given time during the averaging
period,
the owner or operator shall prepare and enter in the
facility operating record
information that specifies the
following:
~j
The maximum and minimum VO concentration values for
the
hazardous
waste
that
occur
during
that
averaging
period
used
for
the
waste
determination
~j
The
operating
conditions
or
circumstances
under
which
the VO concentration of the hazardous waste will be
equal to or greater than 100 ppmw;
and
91
The
information
and
calculations
used
by
the
owner
or
operator to determine the average VO concentration of
the
hazardous
waste.
iL
Procedure
for using direct measurement
to determine average
‘10 concentration of a hazardous waste at the point of waste
origination.
~j.
The owner or operator shall identify and record the
point of waste origination for the hazardous waste.
All waste
samples used to determine the average VO
concentration of the hazardous waste must be collected
at this point.
~J.
The
owner
or
operator
shall
designate
and
record
the
averaging
period
to
be
used
for
determining
the
average VO concentration for the hazardous waste.
The
averaging period must not exceed one year.
An initial
waste determination must be performed for each
averaging period.
91
The
owner
or
operator
shall
identify
each
discrete
quantity of the material composing the hazardous waste
represented by the averaging period designated in
subsection
(a)(S)(B)
above.
An example of
a discrete
quantity of material composing
a hazardous waste
generated as part of
a continuous process
is the
quantity of material generated during a process
operating mode defined by
a specific set of operating
conditions that are normal for the process.
An
example of
a discrete quantity of material composing a
hazardous
waste
generated
as
part
of
a
batch
process
that is performed repeatedly but not necessarily
continuously
is the total quantity of material
composing a single batch generated by the process.
An
example of
a discrete quantity of material composing a
hazardous waste delivered to
a facility
in
a container
is the total quantity of material held in the
container.
~J.
The following procedure must be used measure the VO
concentration
for each discrete quantity of material
identified in subsection (a)(5)(C)
above:
11
A sufficient number of samples, but in no case
fewer than four, must be collected to represent
the organic composition for the entire discrete
quantity of hazardous waste being tested.
All
of the samples must be collected within
a 1-hour
169
period.
Sufficient
information
must
be
prepared
and
recorded
to
document
the
waste
quantity
represented
by
the
samples
and,
as
applicable,
the operating conditions for the source or
process generating the hazardous waste
represented by the samples.
Li.).
Each sample must be collected in accordance with
the
requirements
specified
in
“Test
Methods
for
Evaluating Solid Waste, Physical/Chemical
Methods”,
incorporated
by reference in Section
720.111.
iii)
Each collected sample must be prepared and
analyzed in accordance with the requirements of
Method 25D in 40 CFR 60, Appendix
A,
incorporated by reference
in
35
Ill.
Adm.
Code
720.111.
jyj.
The measured VO concentration for the discrete
quantity of hazardous waste must be determined
by using the results for all samples analyzed in
accordance with subsection
(al(S) (DI (iii) above
and the following equation:
n
C=-~-x
E
C.
fl
1=1
1
Where:
9...~
Measured VO concentration of the
discrete quantity of hazardous
waste,
in
ppmw.
i=
Individual sample “i” of the
hazardous
waste
collected
in
accordance with the requirements of
SW—846.
n=
Total number of samples of hazardous
waste collected
(at least
4) within
a 1—hour period.
C~
VO
concentration
measured
by
Method
25D
for sample “i”,
in ppmw.
fl.j.
The average VO concentration of the hazardous waste
must be determined using the following procedure:
j).
When the facility owner or operator
is the
generator of the hazardous waste,
a sufficient
number of VO concentration measurements for the
hazardous waste must be performed in accordance
with the requirements
of subsection
(a)(5’,(D)
above
to
represent
the
complete
range
of
hazardous waste organic compositions and
quantities that occur during the entire
averaging period due to normal variations in the
operating conditions for each process operating
170
mode identified for the source or process
generating the hazardous waste.
j~j).
When the facility owner or operator
is not the
generator
of
the
hazardous
waste,
a
sufficient
number of
‘10 concentration measurements for the
hazardous waste must be performed in accordance
with the requirements
of subsection
(a)(5)(D)
above to represent the com~1eterange of
hazardous waste organic compositions and
quantities that occur in the hazardous waste as
received at the facility during the entire
averaging period.
iii)
The
average
VO
concentration
of
the
hazardous
waste at the
point
of waste origination must be
calculated by using the results for all VO
measurements performed in accordance with
subsection
(a)(5)(D)
above and the following
equation:
Cave-~-X
E
(Q~xC~)
QT
J1
Where:
~
Average VO concentration of the
hazardous waste at the point of
waste origination,
in
ppmw.
j..~
Individual discrete quantity “j”
of
the hazardous waste for which
a
‘10
concentration measurement
is
determined in accordance with the
reauirements of subsection
(a)(5)(D)
above.
m=
Total number of VO concentration
measurements
determined
in
accordance with the requirements of
subsection
(a)(5)(D)
above
for
the
averaging period.
Mass of the discrete quantity of the
hazardous waste represented by C~
in kg.
Q1~=
Total mass of the hazardous waste
for the averaging period,
in kg.
Measured VO concentration of
discrete quantity
“i”
for the
hazardous waste determined in
accordance with the requirements of
subsection (a)(5)(D)
above,
in
ppmw.
~j
Procedure for using knowledge of the waste to determine the
average VO concentration of a hazardous waste at
the Point
of waste origination.
171
~).
The owner or operator shall identify and record the
point of waste origination for the hazardous waste.
All
information
used
to
determine
the
averaae
VO
concentration of the hazardous waste must be based on
the hazardous waste composition at this point.
fi
The
owner
or
operator
shall
designate
and
record
the
averaging period to be used for determining the
averaae
VO
concentration
for
the
hazardous
waste.
The
averaging period must not exceed one year.
An initial
waste determination must be performed for each
averaging period.
91
The owner or operator shall prepare and record
sufficient information that documents the average VO
concentration for the hazardous waste.
Information
may be used that
is prepared by either the facility
owner or operator or by the generator of the hazardous
waste.
Examples of information that may be used as
the basis for knowledge of the waste include:
organic
material balances for the source or process generating
the waste; VO concentration measurements for the same
type of waste performed
in accordance with the
procedure specified in subsection
(a)(5)(D)
above;
previous individual organic constituent test data for
the waste that are still applicable to the current
waste management practices; documentation that the
waste
is generated by a process for which no organics—
containing materials are used:
previous test data for
other locations managing the same type of waste;
or
other knowledge based on manifests,
shipping papers,
or waste certification notices.
~J.
If test data other than VO concentration measurements
performed in accordance with the procedure specified
in subsection (a)(5)(D)
above are used
as the basis
for knowledge of the waste,
then the owner or operator
shall document the test method, sampling protocol, and
the means by which sampling variability and analytical
variability are accounted for in the determination of
the average VO concentration.
For example,
an owner
or operator may use individual organic constituent
concentration test data that are validated in
accordance with Method 301 in 40 CFR 63, Appendix
A,
incorporated by reference in 35
Ill. Adm. Code
720.111,
as the basis for knowledge of the waste.
Waste determination procedures
for treated hazardous waste.
fl
An owner or operator shall perform the applicable waste
determination for each treated hazardous waste placed in a
waste management unit exempted under the provisions of
Section 725.983(c) (2) from using air emission controls in
accordance with standards specified in Section 725.985
through Section 725.988,
as applicable to the waste
management unit.
21
The owner or operator shall perform a waste determination
for each discrete quantity of treated hazardous waste as
follows:
~j
When the hazardous waste
is treated by
a continuous
172
process. the owner or operator shall:
jJ.
Perform an initial waste determination for the
treated waste stream before the first time any
portion
of
the
material
in
the
waste
stream
is
placed in a waste management unit subject to
this Subpart,
and thereafter update the
information used for the waste determination at
least once every 12 months following the date of
the initial waste determination; and
LU.
Perform a new waste determination whenever
changes
to
the
hazardous
waste
streams
fed
to
the process are reasonably likely to cause the
characteristics of the hazardous waste at the
point of waste treatment to change to levels
that fail to achieve the applicable conditions
specified in Section 725.983(c) (2).
~j
When the hazardous waste
is treated by a batch process
that
is performed repeatedly but not necessarily
continuously,
the owner or operator shall:
Li
Perform an initial waste determination for the
treated hazardous waste in one or more
representative batches treated by the process,
and thereafter update the information used for
the waste determination at least once every
12
months following the date of the initial waste
determination; and
JJJ.
Perform a new waste determination whenever
changes to the hazardous waste treated by the
process are reasonably likely to cause the
characteristics of the hazardous waste at the
point of waste treatment to change to levels
that
fail to achieve the applicable conditions
specified in Section 725.983(c)(2).
~
The owner or operator shall designate and record the
specific provision
in Section 725.983(c)(2)
for which the
waste determination is being performed.
The waste
determination for the treated hazardous waste must be
performed using the applicable procedures
specified in
subsections
(b)(4) through
(b)(10) below.
4.).
Procedure to determine the average VO concentration of a
hazardous waste at the point of waste treatment.
~j
The owner or operator
shall identify and record the
point of waste treatment for the hazardous waste.
All
waste samples used to determine the average VO
concentration of the hazardous waste must be collected
at this point.
~
The owner or operator shall designate and record the
averaging period to be used for determining the
average VO concentration
for the hazardous waste.
The
averaging period must not exceed one year.
An initial
waste determination must be performed for each
averaging period.
173
91
The owner or operator shall identify each discrete
quantity of the material composing the hazardous waste
represented by the averaging period designated
in
subsection (b)(4)(B)
above.
p.).
The following procedure shall be used measure the VO
concentration for each discrete quantity of material
identified in subsection
(b)(4)(C)
above:
LI
A sufficient number of samples, but in no case
fewer than four samples, must be collected to
represent the organic composition for the entire
discrete quantity of hazardous waste being
tested.
All of the samples must be collected
within
a 1—hour period.
Sufficient information
must be prepared and recorded to document the
waste quantity represented by the
sarnoles and,
as applicable,
the operating conditions for the
process treating the hazardous waste represented
by the samples.
LU.
Each sample must be collected in accordance with
the requirements specified in “Test Methods for
Evaluating Solid Waste,
Physical/Chemical
Methods”,
incorporated by reference in
35
Ill.
Adm. Code 720.111.
iii)
Each collected sample must be prepared and
analyzed
in accordance with the requirements of
Method 25D
in 40 CFR 60, Appendix A,
incorporated by reference in 35 Ill.
Adm. Code
720.111.
Li~
The measured VO concentration for the discrete
quantity of hazardous waste must be determined
by using the results for all samples
analyzed in
accordance with subsection
(b) (4) (El (iii) above
and the following equation:
n
C=-~.x
E
C1
fl
1=1
Where:
C=
Measured ‘10 concentration of the
discrete
quantity
of
hazardous
waste,
in ppmw.
i=
Individual sample
“i” of the
hazardous
waste
collected
in
accordance
with
the
requirements
of
SW—846.
n=
Total number of samples of hazardous
waste collected
(at least
41
within
a_1—hour period.
4~
VO concentration measured by Method
25D
for sample
“i”,
in ppmw.
174
~j.
The average VO concentration of the hazardous waste at
the point
of waste treatment must be determined using
the following procedure:
Li.
When the facility owner or operator is the
generator of the hazardous waste,
a sufficient
number of VO concentration measurements for the
hazardous waste must be performed in accordance
with the requirements of subsection
(b)(4)(D)
above to represent the complete range of
hazardous waste organic compositions and
quantities treated by the process during the
entire_averaging period.
LU.
The average VO concentration of the hazardous
waste at the point of waste treatment must be
calculated by using the results for all VO
measurements performed in accordance with
subsection
(b)(4UD)
above and the following
equation:
1
m
C~0=—x
E
(Q~xC~)
0T
j-1
Where:
~
Average VO concentration of the hazardous
waste at the point of waste origination,
in ppmw.
.L~
Individual discrete quantity
“j” of the
hazardous waste for which a
‘10
concentration measurement is determined
in
accordance with the requirements of
subsection (b)(4)(D)
above.
m=
Total number of VO concentration
measurements determined in accordance with
the requirements of subsection
(b)(4)(D)
above for the averaging period.
Q~
Mass of the discrete quantity
of the
hazardous waste represented by C~, in kg.
QT=
Total mass of the hazardous waste for the
averaging period,
in kg.
Measured
‘10
concentration of discrete
quantity
“j”
for
the
hazardous
waste
determined
in
accordance
with
the
requirements of subsection (b)(4)(D)
above,
in ppmw.
~).
Procedure to determine the exit concentration limit
(C,)
for
a treated hazardous waste.
~j
The point of waste origination
for each hazardous
waste treated by the process at the same time must be
identified.
175
~).
If
a single hazardous waste stream is
identified in
subsection
(b)(5)(Al
above. then the exit
concentration limit
(C.) must be 100 ppmw.
9.).
If
more than one hazardous waste stream
is identified
in subsection
(b)(5)(A)
above, then the VO
concentration of each hazardous waste stream at the
point of waste origination must be determined in
accordance with the requirements of subsection
(a)
above.
The exit concentration limit
(C,) must be
calculated by using the results determined for each
individual hazardous waste stream and the following
equation:
in
n
E
(Q~x~~)
+
E
(Q~x1OOppmw)
x=1
y=i
In
n
EQ~+Eo~
x=1
y—1
Where:
4~
Exit concentration limit for treated
hazardous waste,
in
ppmw.
x=
Individual hazardous waste stream
“x’
that
has
a VO concentration less than 100 ppmw
at
the point of waste origination,
as
determined in accordance with the
requirements of Section 725.984(a).
~
Individual hazardous waste stream “v” that
has
a VO concentration equal to or greater
than_100
ppmw
at the point of waste
origination,
as determined
in accordance
with the requirements
of Section
725.984(a).
~
Total number of
“x”
hazardous waste
streams treated by process.
n—
Total number of “y” hazardous waste
streams treated by process.
~
Annual mass quantity of hazardous waste
stream
“x”,
in kg/yr.
Q~=
Annual mass quantity of hazardous waste
stream
“y”,
in kg/yr.
Q,~
Averaae VO concentration of hazardous
waste stream “x”
at the point of waste
origination, as determined in accordance
with the requirements
of
Section
725.984(a),
in
ppmw.
~j.
Procedure to determine the organic reduction efficiency
(RI
176
for a treated hazardous waste.
~j.
The organic reduction efficiency for a treatment
process must be determined based on results
for
a
minimum of three consecutive runs.
The sampling time
for each run must be one hour.
~J.
The Point
of each hazardous waste stream entering the
process and each hazardous waste
stream
exiting the
process that is to be included in the calculation of
the organic reduction efficiency for the process must
be identified.
9.).
For each run, the
following information must be
determined for each hazardous waste stream identified
in subsection (b)(6)(B)
above, using the following
procedures:
LI.
The mass quantity of each hazardous waste stream
entering the process
(Qj
and the mass quantity
of each hazardous waste stream exiting the
process
(p~~)must be determined.
JJJ.
The VO concentration of each hazardous waste
stream entering the process
(Cf) during the run
must be measured in accordance with the
requirements of subsections
(a) (5) (D) (ii through
(a)(5)(D)(iv) below.
The VO concentration of
each hazardous waste stream exiting the process
-
(C.) during the run must be determined in
accordance with the requirements of subsection
(b)(4’,(D)
below.
Samples must be collected as
follows:
For
a continuous process, the samples
of the hazardous waste entering and samples of
the hazardous waste exiting the process must be
collected concurrently.
For
a batch process,
the
samples
of the hazardous waste entering the
process must be collected
at the time that the
hazardous waste
is placed in the process.
The
samples of the hazardous waste exiting the
process must be collected
as soon as practicable
after the time when the process stops operation
or the final treatment cycle ends.
p.).
The waste volatile organic mass flow entering the
process
(E’.)
and the waste volatile organic mass flow
exiting the process
(E.) must be calculated by using
the results determined in accordance with subsection
(b)(6)(C)
above and the following equations:
Eb=_!.~E
(QbJxCbj)
Ea_2_~E (Q8~~8~)
177
Where:
~
Waste volatile organic mass flow exiting
process,
in kg/hr.
&.~
Waste volatile organic mass flow entering
process,
in kg/hr.
flL.~
Total number of runs (at least 3)
.L.~
Individual run
‘“I”
Mass quantity of hazardous waste entering
process during run
“j”,
in kg/hr.
~
Average mass quantity of waste exiting
process during run
“j”,
in kg/hr.
Measured VO concentration of hazardous
waste exiting process during run
“i”,
as
determined in accordance with the
requirements
of
Section
725.984(b)
(4)
(Dl,
in ppmw.
Measured VO concentration of hazardous
waste entering process during run “Y’,
as
determined in accordance with the
requirements of Section 725.984
(a)(5)(D)(i) through
(a)(5)(D)(iv),
in
ppmw.
~
The organic reduction efficiency of the process must
be calculated by using the results determined in
accordance with subsection
(b)(6)(D)
above and the
following equation:
Eb~E
axlOO
Eb
Where:
R=
Organic reduction efficiency,
percent.
~
Waste volatile organic mass
flow entering
process
as determined in accordance with
the requirements of subsection
(b)(6)(D)
above,
in kg/hr.
~
Waste volatile organic mass flow exiting
process as determined in accordance with
the requirements of subsection
(b)(6’j(D)
above,
in kg/hr.
2.).
Procedure to determine the organic biodegradation efficiency
jJfor
a treated hazardous waste.
~j
The fraction of organics biodegraded
~
must be
determined using the procedure specified
in 40 CFR 63.
Appendix C,
incorporated by reference in 35
Ill.
Adm.
178
Code 70.111.
~j.
The organic biodegradation efficiency must be
calculated by using the following equation:
RbjQ=Fbicx
100
Where
~
Organic biodegradation efficiency,
in
percent.
~
Fraction of organic biodeqraded as
determined
in accordance with the
requirements of subsection
(b)(7)(A)
above.
~J.
Procedure to determine the required organic mass removal
rate
(RMR)
for
a treated hazardous waste.
~J.
The point of waste origination for each hazardous
waste treated by the process at the same time must be
identified.
~J.
For each hazardous waste stream identified in
subsection (b)(8)(A) above,
the VO concentration of
the hazardous waste stream at the point of waste
origination must be determined in accordance with the
requirements
of
subsection
(a)
above.
91
For each individual hazardous waste stream that has
a
volatile organic concentration equal to or greater
than 100 ppmw at the point of waste origination as
determined in accordance with the requirements of
subsection (b)(8)(B) above,
the average volumetric
flow rate of hazardous waste at the point of waste
origination and the density of the hazardous waste
stream must be determined.
P.).
The required organic mass removal rate for the
hazardous waste must be calculated by using the
results
determined
for
each
individual
hazardous
waste
stream in accordance with the requirements of
subsections
(b)(8)(B)
and
(b)(8)(C)
above and the
following equation:
(~
-l0opprnw)
RMRE
Vxkx
‘
y—i
~
-‘
106
Where:
RMR
=
Required
organic
mass
removal
rate,
in
kg/hr.
y~
Individual hazardous waste stream
“y” that has
a
volatile organic concentration equal to or
greater than 100 ppmw at
the point of waste
origination,
as determined
in accordance with
179
the requirements of Section 725.984(a).
n=
Total number of
“v” hazardous waste streams
treated
by
process.
V~=
Average volumetric flow rate of hazardous waste
stream “y”
at the point of waste origination,
in
m3/hr.
k~=
Density of hazardous waste stream “v”,
in
kg/rn3
Average VO concentration of hazardous waste
stream
“y”
at the Point of waste origination
as
determined in accordance with the requirements
of Section 725.984(a),
in ppmw.
~J
Procedure to determine the actual organic mass removal rate
(MR)
for a treated hazardous waste.
~1
The actual organic mass removal rate must be
determined based on results for
a minimum of three
consecutive runs.
The sampling time for each run must
be one hour.
~j
The waste volatile organic mass flow entering the
process
(Bk)
and the waste volatile organic mass flow
exiting the process
(E.) must be determined in
accordance with the requirements of subsection
(b)(6)(D)
above.
91
The actual organic mass removal rate must be
calculated by using the results determined
in
accordance with the requirements of subsection
(b)(9)(B)
above and the following equation:
MREbEa
-
Where:
MR
=
Actual organic mass removal
rate,
in
kg/hr.
~
Waste volatile organic mass flow entering
process,
as determined in accordance with
the requirements of
subsection
(b)(6)(D)
above,
in kg/hr.
~
Waste volatile organic mass flow exiting
process,
as
determined
in
accordance
with
the requirements of subsection
(bl(6)(D)
above,
in kg/hr.
~Qj
Procedure to determine the actual organic mass
biodegradation rate
(MRMO)
for
a treated hazardous waste.
~j
The actual organic mass biodegradation rate must be
determined based on results for a minimum of three
consecutive runs.
The sampling time for each run must
be one hour.
180
~
The waste organic mass flow entering the process (E~J
must be determined in accordance with the requirements
of subsection
(b)(6)(D) above.
91
The fraction of organic biodegraded
(Fbi,)
must be
determined using the procedure specified in 40 CFR 63,
Appendix C, incorporated by reference in 35 Ill.
Adm.
Code 720.111.
flJ.
The actual organic mass biodegradation rate must be
calculated by using the mass flow rates and fraction
of organic biodegraded determined in accordance with
the requirements of
subsections
(b)(10)(B)
and
(b) (101 (C)
above and the following equation:
~bio
EbxFbi
a
Where:
Actual organic mass biodegradation
rate,
in kg/hr.
~
Waste
organic
mass
flow
entering
process,
as
determined
in
accordance
with
the
requirements
of
subsection
(b) (6)
(Di
above,
in
kg/hr.
~
Fraction of organic biode~raded, as
determined in accordance with the
requirements of subsection
(b)(1O)(C)
above.
~).
Procedure to determine the maximum organic vapor pressure of
a
hazardous
waste
in
a
tank.
fl.
An
owner
or
operator
shall
determine
the
maximum
organic
vapor pressure for each hazardous waste placed in
a tank
using
air
emission
controls
in
accordance
with
standards
specified
in
Section
725.985(c).
21
An
owner
or
operator
shall
use
either
direct
measurement,
as
specified
in
subsection
(c)(3)
above,
or
knowledge
of
the
waste,
as specified by subsection (c)(4)
above,
to determine
the
maximum
organic
vapor
pressure
that
is
representative
of
the
hazardous
waste
composition
stored
or
treated
in
the
tank.
fl
To
determine
the
maximum
organic
vapor
pressure
of
the
hazardous
waste
by
direct
measurement,
the
following
procedure must be used:
a.).
Representative
samples
of
the
waste
contained
in
the
tank must be collected.
Sampling must be conducted in
accordance with the requirements specified in “Test
Methods for Evaluating Solid Waste, Physical/Chemical
Methods”,
incorporated by reference in 35
Ill.
Adm.
Code 720.111.
~).
Any
of
the
following
methods
may
be
used
to
analyze
the
samples
and
compute
the
maximum
organic
vapor
181
pressure,
as appropriate:
LI
Method
25E in 40 CFR 60,
Appendix A,
incorporated by reference in
35 Ill.
Adm.
Code
720.111
Lj).
Methods described in
American
Petroleum
Institute
Publication
2517,
incorporated
bi
reference
in
35
Ill.
Adm.
Code 720.111;
iii)
Methods
obtained
from
standard
reference
texts
~).
ASTM Method
D 2879—92,
incorporated by reference
in
35
Ill.
Adm.
Code 720.111);
or
~1
Any other method a~~rovedby the Agency for this
use_by_the owner or operator.
4.).
To
determine
the
maximum
organic
vapor
pressure
of
the
hazardous waste by knowledge, sufficient information must be
prepared_and recorded that documents the maximum organic
vapor
pressure
of
the
hazardous
waste
in
the
tank.
Examples
of information that may be used include:
documentation that
the
waste
is
generated
by
a
process
for
which
no
organics—
containing
materials
are
used
or
that
the
waste
is
generated
by
a
process
for
which
at
other
locations
it
previously
has
been determined by direct measurement that the waste maximum
organic vapor pressure
is less than the maximum vapor
pressure
limit
for
the
appropriate
design
capacity
category
specified for the tank.
(Source:
Added at
19
Ill. Reg.
________,
effective
_____________________
Section
725.985
Standards:
Tanks
~
This
Section
applies
to
owners
and
operators
of
tanks
sublect
to
this
Subpart
into
which
any
hazardous
waste
is
placed
except
for
the following tanks:
A tank
in which all hazardous waste entering the tank meets
the
conditions
specified
in
Section
725.983(ci;
or
21
A tank used for biological treatment of hazardous waste
in
accordance with the requirements of Section
725.983(c) (21 (D).
~?).
The
owner
or
operator
shall
place
the
hazardous
waste
into
one
of
the
following
tanks:
LI.
A tank equipped with a cover
(e.g.,
a fixed roof)
that is
vented through a closed—vent system to a control device in
accordance
with
the
requirements
specified
in
subsection
(d)
below
2.).
A tank equipped with a fixed roof and internal floating roof
in accordance with the requirements of Section 725.991
~J
A tank equipped with an external floating roof in accordance
with the requirements
of
Section 725.991;
or
4.).
A pressure tank that
is designed to operate as
a closed
system
such
that
the
tank
operates
with
no
detectable
182
organic emissions
at
all times that hazardous waste is in
the
tank
except
as
provided
for
in
subsection
(g)
below.
gJ
As
an
alternative
to
complying
with
subsection
(bI
above,
an
owner
or operator may Place hazardous waste in a tank equipped with
a
cover
(e.g.,
a fixed roof) meeting the requirements specified in
subsection
(d)(1) below when the hazardous waste is determined to
meet all
of the following conditions:
j).
The
hazardous
waste
is
neither
mixed,
stirred,
agitated,
nor
circulated within the tank by the owner or operator using
a
process that results in splashing,
frothing, or visible
turbulent
flow
on
the
waste
surface
during
normal
process
operations
2.).
The hazardous waste in the tank is not heated by the owner
or
operator
except
during
conditions
requiring
that
the
waste be heated to prevent the waste from freezing or to
maintain adequate waste flow conditions
for continuing
normal
process
operations
i.).
The hazardous waste
in the tank is not treated by the owner
or operator using a waste stabilization process or a process
that produces an exothermic reaction;
and
4.).
The maximum organic vapor pressure of the hazardous waste in
the tank as determined using the procedure specified
in
Section 725.984(c)
is less than the following applicable
value:
~j
If the tank design capacity is equal to or greater
than 151
m3
(5333
ft3 or 39,887 gal),
then the maximum
organic
vapor
pressure
must
be
less
than
5.2
kPa
(0.75
psia or 39 mm Hg)
~J.
If the tank design capacity is equal to or greater
than 75
m3 but less than 151
in
(5333
ft
or 39,887
gal),
then the maximum organic vapor pressure must be
less than 27.6 kPa (4.0 psia or 207 mm Hg); or
p.).
If the tank design capacity is
less than
75 m
(2649
ft
or 19,810 gal),
then the maximum organic vapor
pressure must be less than 76.6 kPa
(11.1 psia or 574
mm Hg).
~J.
To comply with subsection
(b)(l)
above,
the owner or operator
shall
design,
install,
operate,
and
maintain
a
cover
that
vents
the organic vapors emitted from hazardous waste
in the tank
through a closed—vent system connected to
a control device.
fl.
The cover must be designed and operated to meet the
following requirements:
~J.
The cover and all cover openings
(e.g., access
hatches,
sampling
ports,
and
gauge
wells)
must
be
designed to operate with no detectable organic
emissions
when
all
cover
openings
are
secured
in
a
closed,
sealed
position.
~j
Each cover opening must be secured in
a closed,
sealed
position
(e.g.,
covered
by
a
gasketed
lid
or
cap)
at
all
times
that
hazardous
waste
is
in
the
tank
except
183
as provided for in subsection
(f) below.
21
The
closed—vent
system
and
control
device
must
be
designed
and operated
in accordance with the requirements of Section
725. 988.
~).
The owner and operator shall
install, operate,
and maintain
enclosed pipes or other closed systems for the transfer of
hazardous waste as described
in subsection (e)(l)
or
(e)(2)
below.
LI
fl
Add,
remove,
inspect,
or sample the material
in the tank
2.).
Inspect,
maintain,
repair,
or
replace
equipment
located
inside
the
tank;
or
~).
Vent gases or vapors from the tank to
a closed—vent system
connected
to
a
control
device
that
is
designed
and
operated
in accordance with the requirements of Section 725.988.
gj.
One or more safety devices that vent directly to the atmosphere
may
be
used
on
the
tank,
cover,
closed—vent
system,
or
control
device provided each safety device meets all
of the following
conditions:
fl
The safety device
is not used for planned or routine venting
of organic vapors from the tank or the closed—vent system
connected to a control device;
and
2.).
The safety device remains in
a closed,
sealed position at
all
times
except
when
an
unplanned
event
requires
that
the
device open for the Purpose of preventing physical damage or
permanent deformation of the tank,
cover,
closed—vent
system,
or
control
device
in
accordance
with
good
engineering
and
safety
practices
for
handling
flammable,
combustible,
explosive,
or
other
hazardous
materials.
An
example of an unplanned event is a sudden power outage.
(Source:
Added at
19
Ill.
Reg.
,
effective
BOARD NOTE:
U.S. EPA considers a drain system that meets the
requirements
of
40
CFR
61.346(a)(l)
or
(b)(1)
through
(b)(3)
to
be
a “closed-system”.
The Board intends that this meaning be
included in the use of that term for the purposes of this Subpart.
U
Transfer all hazardous waste to the tank from another tank,
surface
impoundment,
or
container
subject
to
this
Subpart,
except
for those hazardous wastes that meet the conditions
specified
in
Section
725.983(c);
and
2.)..
Transfer
all
hazardous
waste
from
the
tank
to
another
tank,
surface impoundment,
or container subject to this Subpart,
except
for those hazardous wastes that meet the conditions
specified
in
Section
725.983(c).
Each cover opening must be secured
in
a closed,
sealed position
(e.g., covered by a gasketed lid) at all times that hazardous
waste
is
in the tank except when
it
is necessary to use the cover
opening
to:
Section 725.986
Standards:
Surface
Impoundments
~j
This
Section
applies
to
owners
and
operators
of
surface
184
impoundments
sublect
to
this
Subpart
into
which
any
hazardous
waste
is placed except for the following surface impoundments:
fl.
A surface impoundment
in which all hazardous waste entering
the
surface
impoundment
meets
the
conditions
specified
in
Section 725.983(c);
or
21
A
surface
impoundment
used
for
biological
treatment
of
hazardous
waste
in
accordance
with
the
requirements
of
Section
725.983(c)(2)(iv).
~J.
The owner or operator shall place the hazardous waste into a
surface
impoundment
equipped
with
a
cover
(e.g.,
an
air—supported
structure or a rigid coverl
that
is vented through
a closed—vent
system to
a control device meeting the requirements specified
in
subsection
(dl
below.
gj.
As
an alternative
to complying with subsection
(bI
above,
an owner
or
operator
may
place
hazardous
waste
in
a
surface
impoundment
equipped
with
a
floating
membrane
cover
meeting
the
requirements
specified
in
subsection
(e)
below
when
the
hazardous
waste
is
determined to meet all of the following conditions:
fl.
The
hazardous
waste
is
neither
mixed,
stirred,
agitated,
nor
circulated within the surface impoundment by the owner or
operator using a process that results
in splashing,
frothing,
or visible turbulent flow on the waste surface
during normal process operations
2.).
The hazardous waste
in the surface impoundment
is not heated
by the owner or operator;
and
1).
The hazardous waste
in the surface impoundment
is not
treated by the owner or operator using a waste stabilization
process or
a process that produces an exothermic reaction.
~j
To comply with subsection
(b)(1)
above, the owner or operator
shall
design,
install,
operate,
and
maintain
a
cover
that
vents
the_organic vapors emitted from hazardous waste in the surface
impoundment through
a closed-vent system connected to a control
device.
U
The
cover
must
be
designed,
installed,
operated,
and
maintained
to
meet
the
following
requirements:
~j.
The cover and
all cover openings
(e.g., access
hatches,
sampling
ports,
and
gauge
wells)
must
be
designed to operate with no detectable organic
emissions
when
all
cover
openings
are
secured
in
a
closed,
sealed
position.
~).
Each cover opening must be secured in the closed,
sealed
position
(e.g.,
covered
by
a
gasketed
lid
or
cap)
at
all
times
that
hazardous
waste
is
in
the
surface
impoundment,
except as provided for in
subsection
(g)
below.
p.).
The closed—vent system
and control device must be
designed and operated
in accordance with Section
725.988.
~j
To comply with subsection
(cI
above, the owner or operator shall
185
design,
install,
operate,
and
maintain
a
floating
membrane
cover
that meets all of the following requirements:
fl
The
floating
membrane
cover
must
be
designed,
installed,
and
operated such that at all times when hazardous waste is
in~
the surface impoundment, the entire surface area of the
hazardous
waste
is
enclosed
by
the
cover,
and
any
air
spaces
underneath the cover are not vented to the atmosphere except
during conditions specified in subsection
(h)
below.
2.).
The floating membrane cover and all cover openings
(e.g.,
access hatches,
sampling ports,
and gauge wells) must be
designed
to
operate
with
no
detectable
organic
emissions
when
all
cover
openings
are
secured
in
a
closed,
sealed
position.
fl
Each cover opening must be secured in
a closed,
sealed
position
(e.g., covered by
a gasketed lid or cap) at all
times
that
hazardous
waste
is
in
the
surface
impoundment
except as provided for
in subsections
(g)(l) through
(g)(3)
below.
4.).
The
synthetic
membrane
material
used
for
the
floating
membrane cover must be either:
~j.
High density polyethylene with
a thickness no less
than 2.5 mm;
or
~
A material
or
a composite of different materials
determined to have the following properties:
LI
Organic permeability properties that are
equivalent to those of the material specified in
subsection
(e)(4)(A)
above;
and
jj).
Chemical and physical properties that maintain
the material integrity for as long as the cover
is
in use.
Factors that must be considered in
selecting
the
material
include:
the
effects
of
contact
with
the
waste
managed
in
the
impoundment,
weather
exposure,
and
cover
installation
and
operation
practices.
fi
The owner
or operator shall install,
operate,
and maintain
enclosed
pipes
or
other
closed
systems
for
the
transfer
of
hazardous waste as described in subsection (f)(l)
or
(f’i(2)
below.
BOARD NOTE:
U.S. EPA considers a drain system that meets the
requirements of 40 CFR 6l.346(a)(1)
or
(b)(l) through
(b)(3) to be
a “closed—system”.
The Board intends that this meaning be
included in the use of that term for the purposes of this Subpart.
U
Transfer all hazardous waste to the surface impoundment from
another tank,
surface impoundment,
or container subject to
this Subpart, except for those hazardous wastes that meet
the conditions specified in Section 725.983(c);
and
21
Transfer all hazardous waste from the surface impoundment to
another tank,
surface impoundment,
or container subject to
this Subpart, except
for those hazardous wastes that meet
the conditions specified in Section 725.983(c).
186
gj
Each cover opening must be secured
in the closed,
sealed position
(e.g.,
covered by
a gasketed lid or
cap)
at all times that
hazardous waste
is in the surface impoundment except when
it
is
necessary to use the cover opening to:
U
Add,
remove,
inspect,
or sample the material
in the surface
impoundment
2.).
Inspect,
maintain, repair,
or replace equipment located
underneath the cover
~
Remove treatment residues from the surface impoundment in
accordance with the requirements of 35
Ill. Adm. Code
728.104;
or
4.).
Vent aases or vapors from the surface impoundment to
a
closed—vent system connected to
a control device that
is
designed and operated
in accordance with the requirements of
Section 725.988.
~j.
One
or
more
safety
devices
that
vent
directly
to
the
atmosphere
may be installed on the cover,
closed—vent system,
or control
device provided each device meets all of the following conditions:
fl.
The safety device
is not used for planned or routine venting
of organic vapors from the surface impoundment or the
closed—vent system connected to a control device; and
2.).
The
safety
device
remains
in
a
closed,
sealed
position
at
all times except when an unplanned event requires that the
device open for the purpose of preventing physical damage or
permanent deformation
of the cover, closed—vent
system, or
control device
in accordance with good engineering and
safety practices for handling flammable,
combustible,
explosive,
or other hazardous materials.
An example of
an
unplanned event is a sudden power outage.
(Source:
Added at
19
Ill.
Reg.
________,
effective
_____________________
Section 725.987
Standards:
Containers
~
This Section applies to the owners
and operators of containers
having design capacities greater than 0.1
in3
(3.5 ft
or 26.4 gal)
subject to this
Subpart
into
which
any
hazardous
waste
is
placed,
except
for a container in which all hazardous waste entering the
container meets the conditions specified in Section 725.983(c).
~j
An
owner
or
operator
shall
manage
hazardous
waste
in
containers
using the following procedures:
U
The owner or operator shall place the hazardous waste into
one of the following containers,
except when a container
is
used for hazardous waste treatment
as required by subsection
(b)(2)
below:
~J.
A container that is equipped with
a cover that
operates with no detectable organic emissions when all
container openings
(e.g.,
lids,
bungs,
hatches,
and
sampling ports) are secured in
a closed,
sealed
position.
The owner or operator shall determine that
a container operates with no detectable emissions by
testing each opening on the container for leaks
in
187
accordance
with
Method
21
in
40
CFR
60.
Appendix
A,
incorporated by reference in
35 Ill.
Adm. Code
720.111,
the
first
time
any
portion
of
the
hazardous
waste
is placed into the container.
If
a leak is
detected and cannot be repaired immediately, the
hazardous waste must be removed from the container and
the container not used to meet the requirements of
this subsection until the leak is
repaired and the
container
is retested.
fl.).
A container having
a design capacity less than or
equal to 0,46 m3
(16.2
ft
or 121.5 gal) that is
equipped with a cover and complies with all applicable
U.S.
Department of Transportation regulations on
packaging hazardous waste for transport under 49 CFR
178, incorporated by reference in 35
Ill.
Adm. Code
720.111.
LI
A container that
is managed in accordance with
the requirements of 49 CFR 178 for the purpose
of complying with this Subpart
is
not
subject to
any
exceptions
to
the
49
CFR
178
regulations,
except
as
noted
in
subsection
(bl(l)(B)(ji)
above.
Lii
A lab pack that
is managed in accordance with
the requirements of 49 CFR 178 for the purpose
of complying with this Subpart may comply with
the exceptions for combination packagings
specified in
49 CFR 173.12(b).
91
A container that
is attached to or forms
a part of any
truck,
trailer,
or railcar and that has been
demonstrated within the preceding 12 months to be
organic
vapor
tight
when
all
container
openings
are
in
a closed,
sealed position
(e.g., the container hatches
or lids are gasketed and latched).
For the purpose of
meeting the requirements of this subsection,
a
container
is organic vapor tight
if the container
sustains a pressure change of not more than 0.75 kPa
(0.11
psig
or
5.6
mm
Hg)
within
5
minutes
after
it
is
pressurized to
a minimum of 4.5 kPa
(0.65 psig or 33.7
mm
Hg).
This
condition
is
to
be
demonstrated
using
the pressure test specified
in Method 27 of 40 CFR 60,
Appendix
A,
incorporated by reference in 35
Ill. Adm.
Code 720.111,
and a pressure measurement device that
has
a precision of ±2.5 mm water and that
is capable
of
measuring
above
the pressure at which the container
is to be tested
for vapor tightness.
2.)..
An owner or operator treating hazardous waste in
a container
by either a waste stabilization process,
any process that
requires the
addition of heat to the waste,
or any process
that produces an exothermic reaction must meet the following
requirements:
i.).
Whenever
it
is necessary for the container to be open
during the treatment process,
the container must be
located inside an enclosure that
is vented through a
closed—vent system to
a control device.
~j
The enclosure must be a structure that is designed and
188
operated
in accordance with the following
requirements:
JJ.
The enclosure must be
a structure that
is
designed and operated with sufficient airflow
into the structure to capture the organic vaPors
emitted
from
the
hazardous
waste
in
the
container
and
vent
the
vapors
through
the
closed—vent
system
to
the
control
device.
Lii.
The
enclosure
may
have
permanent
or
temporary
openings
to
allow
worker
access,
passage
of
containers
through
the
enclosure
by
conveyor
or
other
mechanical
means,
entry
of
permanent
mechanical or electrical equipment, or to direct
airflow into the enclosure.
The pressure drop
across
each
opening
in
the
enclosure
must
be
maintained at
a pressure below atmospheric
pressure such that whenever an open container
is
placed inside the enclosure no organic vapors
released from the container exit the enclosure
through the opening.
The owner or operator
shall determine that an enclosure achieves this
condition by measuring the pressure drop across
each opening in the enclosure.
If the pressure
within the enclosure
is equal to or greater than
atmospheric pressure then the enclosure does not
meet the requirements of this Section.
4.).
The closed-vent system and control device must be
designed and operated in accordance with the
requirements of Section 725.988.
~j
An owner or operator transferring hazardous waste into
a
container having a design capacity greater than 0.46 m3
(16.2
ft3 or 121.5 gal)
shall meet the following
requirements:
~l.
Hazardous waste transfer by pumping must be performed
using a conveyance system that uses
a tube
(e.g.,
pipe,
hose)
to
add
the
waste
into
the
container.
During transfer of the waste into the container,
the
cover must remain in place and all container openings
must be maintained in a closed,
sealed position except
for those openings through which the tube enters the
container and as provided for in subsection
(c)
below.
The tube must be positioned
in a manner such that
either the:
LI
Tube outlet continuously remains submerged below
the waste surface
at all times waste
is flowing
through_the tube;
jj).
Lower
bottom
edge
of
the
tube
outlet
is
located
at
a distance no greater than two inside
diameters of the tube or 15.25 cm
(0.50 ft or
6.0
in), whichever distance
is greater, from the
bottom of the container at
all times waste is
flowing through the tube; or
iii)
Tube
is connected to a permanent port mounted on
the bottom of the container so that the lower
189
edge of the port opening inside the container
is
located at
a distance equal to or less than
15.25 cm
(0.50
ft or 6.0
in)
from the container
bottom.
~J.
Hazardous waste transferred by a means other than
pumping must be performed such that during transfer of
the waste into the container, the cover remains in
place and all container openings are maintained in a
closed,
sealed position except
for those openings
through which the hazardous waste
is added and as
provided for
in subsection
(d) below.
~
Each container opening must be maintained in a closed,
sealed
position
(e.g., covered by a gasketed lid)
at all times that
hazardous waste is
in the container except when
it
is necessary to
use the opening to:
U
Add,
remove,
inspect, or sample the material
in the
container
2.).
Inspect, maintain,
repair,
or replace equipment located
inside the container; or
~).
Vent gases or vapors from a cover
located over or enclosing
an open container to
a closed—vent system connected to
a
control device that
is designed and operated
in accordance
with the requirements of Section 725.988.
~j.
One or more safety devices that vent directly to the atmosphere
may be used on the container, cover,
enclosure,
closed—vent
system,
or control device provided each device meets all of the
following conditions:
fl.
The safety device is not used for planned or routine venting
of organic vapors from the container,
cover,
enclosure, or
closed—vent system connected to a control device; and
2.)..
The safety device remains
in a closed, sealed position at
all times except when an unplanned event requires that the
device open for the purpose of preventing physical damage or
permanent deformation
of the container,
cover,
enclosure,
closed—vent system, or control device in accordance with
good engineering and safety practices for handling
flammable,
combustible,
explosive,
or other hazardous
materials. An example of an unplanned event
is
a sudden
power outage.
(Source:
Added at 19
Ill.
Reg.
________,
effective
_____________________
Section 725.988
Standards:
Closed—vent Systems and Control Devices
~J.
This Section applies to each closed—vent system and control device
installed and operated by the owner or operator to control air
emissions in accordance with standards of this Subpart.
fl.).
The closed—vent system must meet the following requirements:
U
The
closed—vent
system
must
route
the
gases,
vapors,
and
fumes emitted from the hazardous waste in the waste
management unit to a control device that meets the
requirements specified
in
subsection
(c)
below.
190
2.).
The closed—vent system must be designed and operated in
accordance with the requirements specified in Section
725.933(j).
~J.
If the closed—vent
system contains one or more bypass
devices that could be used to divert
all or a portion of the
gases,
vapors,
or fumes
from entering the control device,
the owner or operator shall meet the following requirements:
~J.
For each bypass device except as provided for in
subsection
(b)(3)(B) below,
the owner or operator
shall either:
LI
Install,
calibrate, maintain, and operate a flow
indicator at the inlet to the bypass device that
indicates at least once every 15 minutes whether
gas, vapor,
or fume flow is present
in the
bypass device; or
LU.
Secure the valve installed at the inlet to the
bypass device in the closed position using a
car—seal or
a lock—and—key
type
configuration.
The owner or operator shall visually inspect the
sea,
or closure mechanism at least once every
month to verify that the valve
is maintained
in
the closed position.
~J.
Low leg drains,
high point bleeds,
analyzer vents,
open—ended valves or lines,
and safety devices are not
subject to the requirements of subsection
(b)(3)(A)
above.
,ç~).
The control device must meet the following requirements:
U
The control device must be one of the following devices:
~j,
A control device designed and operated to reduce the
total organic content
of the inlet vapor stream vented
to the control device by at
least 95 percent by
weight
~J.
An enclosed combustion device designed and operated in
accordance with the requirements of Section
725.933(c);
or
p.).
A flare designed and operated in accordance with the
requirements of Section 725.933(d).
2.).
The control device must be operating at all times when
gases,
vapors,
or fumes are vented from the waste management
unit through the closed—vent system to the control device.
~J.
The owner or operator using
a carbon adsorption system to
comply with subsection
(c)(l)
above shall operate and
maintain the control device in accordance with the following
requirements:
~j
Following the initial startup of the control device,
all activated carbon in the control device must be
replaced with fresh carbon on a regular basis in
accordance with the requirements of Section 725.933(g)
or 725.933(h).
191
fl.).
All carbon removed from the control device must be
managed in accordance with the requirements of Section
725.933(1).
4.).
An owner or operator using a control device other than a
thermal vapor
incinerator,
flare,
boiler,
process heater,
condenser,
or carbon adsorption system to comply with
subsection
(c)(1)
above shall operate and maintain the
control device in accordance with the requirements of
Section 725.933(i).
~j.
The owner or operator shall demonstrate that
a control
device achieves the performance requirements of subsection
(c)(1)
above as follows:
~J
An owner or operator shall demonstrate using either a
performance test,
as specified in subsection
(c)(5)(C)
below,_or_a design analysis,
as specified in
subsection
fc)(5)(D)
below, the performance of each
control device except
for the following:
LI
A flare
J~J.,).
A boiler or process heater with a design heat
input capacity of 44 megawatts or greater;
Lii)
A boiler or process heater into which the vent
stream
is introduced with the primary fuel
)~y~.).
A boiler or process heater burning hazardous
waste
for which the owner or operator has been
issued a final permit
35
Ill.
Adm. Code 703
and
705 and that
is designed and operated in
accordance with the requirements of
35
Ill.
Adm.
Code 726,Subpart H;
or
y.).
A boiler or process heater burning hazardous
waste
for which the owner or operator has
certified compliance with the interim status
requirements of
35
Ill.
Adrn.
Code 726.Subpart H.
a,).
An owner or operator shall demonstrate the performance
of each flare
in accordance with the requirements
specified in Section 725.933(e).
p.).
For a performance test conducted to meet the
requirements of subsection
(c)(5)(A)
above,
the owner
or operator shall use the test methods
and procedures
specified in Section 725.934(c)(1)
through
(c)(4).
p.~
For
a
design
analysis
conducted
to
meet
the
requirements of subsection
(c)(5)(A)
above,
the design
analysis must meet the requirements specified in
Section 725.935(b) (4) (C).
~J
The owner or operator shall demonstrate that
a carbon
adsorption
system achieves the performance
requirements of subsection
(c)(1)
above based on the
total quantity of organics vented to the atmosphere
from all carbon adsorption system equipment that
is
used for organic adsorption,
organic desorption or
carbon regeneration,
organic recovery,
and carbon
192
disposal.
fi
If the owner or operator and the Agency do not agree on
a
demonstration of control device performance using
a design
analysis,
then the disagreement must be resolved using the
results of a performance test performed by the owner or
operator
in accordance with the requirements of subsection
(c)(5)(C)
above.
The Agency may choose to have an
authorized representative observe the performance test.
(Source:
Added at
19
Ill. Reg.
________,
effective
______________________
Section 725.989
Inspection and Monitoring Requirements
~J,,
This Section applies to an owner or operator using air emission
controls
in accordance with the requirements of Sections 725.985
through 725.988.
~).
Each cover used
in accordance with requirements of Sections
725.985
through 725.987 must be visually inspected and monitored
for detectable organic emissions by the owner or operator using
the procedure specified
in subsection
(f) below,
except as
follows:
fl
An owner or operator
is exempted from performing the cover
inspection and monitoring requirements specified in
subsection
(f) below for the following tank covers:
~j
A tank internal floating roof that
is inspected and
monitored in accordance with the requirements of
Section 725.991;
or
a,).
A tank external floating roof that
is inspected and
monitored in accordance with the requirements of
Section 725.991.
21
If
a tank is buried partially or entirely underground,
an
owner or operator is required to perform the cover
inspection and monitoring requirements specified
in
subsection
(f) below only for those portions of the tank
cover and those connections to the tank cover or tank body
(e.g.,
fill ports, access hatches,
gauge wells,
etc.)
that
extend to or above the ground surface and can be opened to
the atmosphere.
~j,.
An owner or operator is exempted from performing the cover
inspection and monitoring requirements
specified in
subsection
(f) below for a container that meets all
requirements specified in either Section 725.987(b) (1) (B)
or
(b) (1) (C’,.
4.),,
An owner or operator
is exempted from performing the cover
inspection and monitoring requirements
specified in
subsection
(f) below for an enclosure used to control
air
emissions from containers in accordance with the
requirements
of Section 725.987(b) (2).
flj,,
Each closed—vent system used
in accordance with the requirements
of Section 725.988 must be inspected and monitored by the owner or
operator
in accordance with the procedure specified
in Section
725.933(1).
193
~j.
Each control device used in accordance with the requirements of
Section 725.988 must be inspected and monitored by the owner or
operator
in
accordance
with
the
procedure
specified
in
Section
725.933(f).
f,,).
The
owner
or
operator
shall
develop
and
implement
a
written
plan
and schedule to perform all inspection and monitoring requirements
of this section.
The owner or operator shall incorporate this
plan and schedule into the facility inspection plan required under
35
Ill.
Adm.
Code 725.115.
LI
Inspection
and
monitoring
of
a
cover
in
accordance
with
the
requirements of subsection
(b)
above must be performed as follows:
U
The
cover
and
all
cover
openings
must
be
initially
visually
inspected and monitored
for detectable organic emissions on
or before the date that the tank,
surface impoundment,
or
container using the cover becomes subject to the provisions
of this Subpart and at other times as requested by the
Agency.
21
At least once every
6 months following the initial visual
inspection and monitoring for detectable organic emissions
required under subsection
(f)(1)
above,
the owner and
operator shall visually inspect and monitor the cover and
each cover opening except for following cover openings:
~j
A cover opening that has continuously remained
in a
closed,
sealed position for the entire period since
the last time the cover opening was visually inspected
and monitored for detectable emissions
fl,,,).
A cover opening that
is designated as unsafe to
inspect
and
monitor
in
accordance
with
subsection
(f)(5) below
p.).
A cover opening on
a cover installed and placed in
operation before December
6,
1994 that
is designated
as difficult to
inspect and monitor
in accordance with
subsection (f)(6)
below.
~J.
To visually inspect
a cover,
the owner or operator shall
view
the
entire
cover
surface
and
each
cover
opening
in
a
closed,
sealed position for evidence of any defect that may
affect the ability of the cover or cover opening to continue
to operate with
no detectable organic emissions.
A visible
hole, gap,
tear,
or split in the cover surface or a cover
opening is defined as
a leak that must be repaired in
accordance with subsection
(f)(7)
below.
4.).
To monitor
a cover for detectable organic emissions,
the
owner or operator shall use the following procedure:
~J.
Method
21
in 40 CFR 60,
appendix A,
incorporated by
reference
in 35 Ill.
Adm. Code 720.111, to test each
cover seal and cover connection for detectable organic
emissions.
Seals on floating membrane covers must be
monitored around the entire perimeter of the cover at
locations a~acedno arsater than
3 meters apart.
~J
For all cover connections and seals except for the
seals around a rotating shaft that passes through
a
194
cover opening,
if the monitoring instrument indicates
detectable organic emissions
(i.e.,
an instrument
concentration reading greater than 500 ppmv plus the
background
level),
then
a
leak
is
detected.
Each
detected leak must be repaired in accordance with
subsection
(f)(7)
below.
4.).
For the seals around a rotating shaft that passes
through a cover opening,
if the monitoring instrument
indicates
a concentration reading greater than 10,000
ppmv, then
a leak
is detected.
Each detected leak
must be repaired
in accordance with subsection
(f)(7)
below.
fi
An owner or operator may designate
a cover as an unsafe to
inspect and monitor cover
if all of the following conditions
are met:
~j.
The owner or operator determines that inspection or
monitoring of
the cover would expose
a worker to
dangerous, hazardous,
or other unsafe conditions.
~j.
The owner or operator develops
and implements a
written plan and schedule to inspect the cover using
the procedure specified
in subsection (f)(3)
above and
monitor the cover using the procedure specified
in
subsection
(f)(4) below as
frequently as practicable
during those times when a worker can safely access the
cover.
,~,).
An owner or operator may designate a cover installed and
placed
in operation before December
6,
1994,
as
a difficult
to inspect and monitor cover
if all of the following
conditions are met:
~j.
The owner or operator determines that inspection or
monitoring the cover requires elevating
a worker to a
height greater than
2 meters
(6.6
ft)
above
a support
surface; and
~j.
The owner and operator develops and
implements a
written plan and schedule to inspect the cover using
the procedure specified in subsection
(f)(3)
above,
and to monitor the cover using the procedure specified
in subsection
(f’,(4)
above
at
least once
per
calendar
year.
fl
When a leak
is detected by either of the methods specified
in subsection
(f)(3)
or (f)(4)
above,
the owner or operator
shall repair the leak
in the following manner:
~J.
The owner or operator shall make a first attempt at
repairing
the
leak
no
later
than
5
calendar
days
after
the leak is detected.
Repair of the leak must be
completed as soon as practicable,
but no later than 15
calendar days after the leak
is detected.
If repair
of the leak cannot be completed within the 15—day
period,
except as provided
in subsection
(f)(7)(B)
below,
then the owner or operator
shall not add
hazardous waste to the tank,
surface impoundment,
or
container on which the cover is installed until the
repair of the leak
is completed.
195
~j.
Repair
of
a
leak
detected
on
a
cover
installed
on
a
tank or surface impoundment may be delayed beyond
15
calendar days
if the owner or operator determines that
both of the following conditions occur:
ii.
Repair of the leak requires
first emptying the
contents of the tank or surface impoundment;
and
LU.
Temporary removal of the tank or surface
impoundment from service will result in the
unscheduled cessation of production from the
process
unit
or
operation
of
the
waste
management unit that
is generating the hazardous
waste managed in the tank or surface
impoundment.
p.).
Repair of a leak determined by the owner or operator
to meet the conditions specified in subsection
(f)(7)(B)
above must be performed at the next time the
process,
system,
or waste management unit that
is
generating the hazardous waste managed in the tank or
surface impoundment
stops operation for any reason.
(Source:
Added at 19
Ill.
Reg.
________,
effective
_____________________
Section 725.990
Recordkeeping Requirements
k.).
Each owner or operator of
a facility subject to requirements
in
this Subpart shall record and maintain the following information
as applicable:
U
Documentation for each cover installed on a tank in
accordance with the requirements of Section 725.985(b) (2) or
725.985(b) (3) that includes information prepared by the
owner
or
operator
or
provided
by
the
cover
manufacturer
or
vendor describing the cover design,
and certification by the
owner or operator that the cover meets the applicable design
specifications as listed in Section 725.991(c).
2..).
Documentation for each floating membrane cover installed on
a surface impoundment
in accordance with the requirements of
Section 725,986(c)
that
includes information prepared by the
owner or operator or provided by the cover manufacturer or
vendor describing the cover design,
and certification by the
owner or operator that the cover meets the specifications
listed in Section 725.986(e).
~J,,
Documentation for each enclosure used to control air
emissions
from containers
in accordance with the
requirements of Section 725.987(b)(2)(A) that includes
information prepared by the owner or operator or provided by
the manufacturer or vendor describing the enclosure design,
and certification by the owner or operator that the
enclosure meets the specifications listed in Section
725.987(b) (2) (B).
4_I
Documentation for each
closed—vent system and control device
installed
in accordance with the requirements of Section
725.988 that includes:
a.).
Certification that
is signed and dated by the owner or
operator stating that the control device is designed
196
to operate at the performance level documented by a
design analysis,
as specified in subsection
(al(4’UB)
below,
or by performance tests,
as specified in
subsection
(a)(4)(C)
below, when the tank,
surface
impoundment, or container
is or would be operating at
capacity
or
the
highest
level
reasonably
expected
to
occur.
fl.).
If
a
design
analysis is used, then design
documentation
as specified in Section 725.935(b) (4).
The documentation must
include information prepared by
the owner or operator or provided by the control
device manufacturer or vendor that describes the
control device design in accordance with Section
725.935(b)(4)(C)
and
certification
by
the
owner
or
operator that the control equipment meets the
applicable specifications.
p.).
If performance tests are used,
then
a performance test
plan as specified
in Section 725.935(b) (3)
and all
test results.
P.).
Information
as required by Sections 725.935(c) (1)
and
725.935(c) (2).
~_I
Records for all Method
27 tests performed by the owner or
operator for each container used to meet the requirements of
Section 725.987(b)(l)(C).
Records
for all visual inspections conducted
in accordance
with the requirements of Section 725.989.
fl
Records for all monitoring for detectable organic emissions
conducted in accordance with the requirements of Section
725.989.
~
Records of the date of each attempt to repair a leak,
repair
methods applied,
and the date of successful repair.
Records
for
all
continuous
monitoring
conducted
in
accordance with the requirements of Section 725.989.
).QJ
Records
of
the
management
of
carbon
removed from a carbon
adsorption
system conducted in accordance with Section
725.988(c)
(3)
(B).
.)JJ
Records for
all
inspections of each cover installed on a
tank
in accordance with the requirements of Section
725.985(b)(2)
or Section 725.985(b) (3)
that includes
information as
listed
in Section 725.991(c).
~j
An owner or operator electing to use air emission controls for
a
tank in accordance with the conditions
specified in Section
725.985(c)
shall record the following information:
LI.
The date and time each waste sample is collected for direct
measurement of maximum organic vapor pressure
in accordance
with Section 725.984(c).
2.1
The results of each determination
for the maximum organic
vapor pressure
of the waste in the tank performed
in
accordance with Section 725.984(c).
197
~_I
The records specifying the tank dimensions and design
capacity.
,ç_I
An owner or operator electing to use air emission controls for a
tank
in
accordance
with
the
requirements
of
Section
725.991
shall
record the information required by Section 725.991(c).
~j.
An owner or operator electing not to use air emission controls for
a particular tank,
surface impoundment, or container subject to
this Subpart in accordance with the conditions specified in
Section 725.983(c)
shall record the information used by the owner
or operator for each waste determination (e.g., test results,
measurements,
calculations,
and
other
documentation)
in
the
facility operating
log.
If analysis results for waste samples are
used for
the waste determination, then the owner or operator shall
record
the
date,
time,
and
location
that
each
waste
sample
is
collected in accordance with applicable requirements of Section
725. 984.
~,).
An owner
or operator electing to comply with requirements
in
accordance with Section 725.983(c) (2) (F)
or 725.983(c)(2)(E)
shall
record the identification number
for the
incinerator, boiler, or
industrial furnace
in which the hazardous waste
is treated.
LI
An owner or operator designating
a cover
as unsafe to inspect and
monitor pursuant to Section 725.989(f)(5)
or difficult to inspect
and
monitor
pursuant
to
Section
725.989(f)(6)
shall
record
in
a
log that
is kept
in the facility operating record the following
information:
fl.
A list of identification numbers for tanks with covers that
are
designated
as
unsafe
to
inspect
and
monitor
in
accordance with the requirements of Section 725.989(f)(5),
an explanation for each cover stating why the cover
is
unsafe to inspect and monitor,
and the plan and schedule for
inspecting and monitoring each cover.
2.).
A list of identification numbers
for tanks with covers that
are_designated
as difficult to inspect and monitor in
accordance with the requirements of Section 725.989(f)(6),
an explanation for each cover stating why the cover
is
difficult to
inspect and monitor,
and the plan and schedule
for inspecting and monitoring each cover.
g,).
All
records
required
by
subsections
(a)
through
(f)
above,
except
as required in subsections
(a)(1)
through
(a)(4)
above,
must be
maintained
in the operating record
for a minimum of
3 years.
All
records required by subsections
(a)(1) through
(a)(4) above must
be maintained in the operating record until the air emission
control equipment
is replaced or otherwise no longer
in service.
fl,).
The owner or operator of
a facility that
is subject to this
Subpart and to the control device standards
in 40 CFR
60, Subpart
VV, or
40 CFR 61, Subpart V.
incorporated by reference in 35
Ill.
Adm.
Code
270.111,
may
elect
to
demonstrate
compliance
with
the
applicable Sections of this Subpart by documentation either
pursuant to this Subpart,
or pursuant to the provisions of
40 CFR
60,
Subpart VV or 40 CFR 61,
Subpart V.
to the extent that the
documentation required by 40 CFR 60 or 61 duplicates the
documentation required by this Section.
(Source:
Added at
19 Ill. Reg.
________,
effective
______________________
198
Section 725.991
Alternative Tank Emission Control Requirements
,~j.
This Section applies to owners and operators of tanks electing to
comply
with
Section
725.985(b)
(2)
or
(b)(3).
fl.
The owner or operator electing to comply with Section
725.985(b)(2)
shall design,
install, operate,
and maintain a
fixed_roof
and
internal
floating
roof
that
meet
the
following requirements.
~&).
The
fixed
roof
must
comply
with
the
requirements
of
Section 725.985(d)(1).
The internal floating roof
must rest or float on the waste surface
(but not
necessarily in complete contact with
it)
inside a tank
that has a fixed roof.
The internal floating roof
must be floating on the waste surface at all times,
except
during
initial
fill
and
during
those
intervals
when the tank
is completely emptied or subsequently
emptied and refilled.
When the roof
is resting on the
leg_supports,
the process of filling,
emptying,
or
refilling must be continuous and must be accomplished
as rapidly as possible.
~_I
Each internal
floating roof must be equipped with one
of_the_following closure devices between the wall of
the tank and the edge of the internal floating roof:
LI
A foam— or liquid—filled seal mounted
in contact
with the waste
(liquid—mounted seal).
A liquid—
mounted seal means a foam— or liquid—filled seal
mounted in contact with the waste between the
wall of the tank and the floating roof
continuously around the circumference of the
tank.
Li.).
Two seals mounted one above the other so that
each forms a continuous closure that completely
covers the space between the wall of the tank
and the edge of the internal floating roof.
The
lower seal may be vapor—mounted, but both must
be continuous.
iii)
A mechanical
shoe seal.
A mechanical shoe seal
is_a_metal sheet held vertically against the
wall of the tank by springs or weighted levers
and
is connected by braces to the floating roof.
A flexible coated fabric
(envelope)
spans the
annular space between the metal
sheet and the
floating roof.
91
Each opening
in
a noncontact internal floating roof
except for automatic bleeder vents (vacuum breaker
vents)
and the rim space vents is to provide
a
projection below the waste surface.
p_I
Each opening in the internal floating roof except
for
leg sleeves,
automatic bleeder vents,
rim space vents,
column wells,
ladder wells,
sample wells,
and stub
drains
is to be equipped with a cover or lid that
is
to be maintained in
a closed position at all times
(i.e.,
no visible gap),
except when the device
is
in
actual use.
The cover or lid must be equipped with
a
199
gasket.
Covers
on
each
access
hatch
and
automatic
gauge float well must be bolted, except when they are
in use.
i.).
Automatic bleeder vents must be equipped with a gasket
and are to be closed
at all times when the roof is
floating,
except when the roof is being floated off or
is_being landed on the roof leg supports.
fi
Rim space vents must be equipped with
a gasket and are
to be set to open only when the internal floating roof
is not floating or at the manufacturer’s recommended
setting.
~J.
Each penetration of
the internal floating roof for the
purpose of sampling must be
a sample well.
The sample
we..
must have a slit fabric cover that covers
at
least
90 percent of the opening.
~j).
Each penetration of the internal floating roof that
allows for passage of
a column supporting the fixed
roof must have
a flexible fabric sleeve seal or a
gasketed sliding cover.
fl
Each penetration of the internal floating roof that
allows for passage of a ladder must have a gasketed
sliding cover.
2.).
The owner or operator electing to comply with Section
725.985(b) (3)
shall design,
install, operate,
and maintain
an external floating roof that meets the following
requirements:
~_I
Each
external
floating
roof
must
be
equipped
with
a
closure device between the wall of the tank and the
roof edge.
The closure device is to consist of two
seals,
one above the other.
The lower seal is
referred to
as the primary seal,
and the upper seal is
referred
to
as
the
secondary
seal.
LI
The primary seal must be either a mechanical
shoe 9eal or a liquid—mounted seal.
Except
as
provided in subsection
(b)(2)(D)
below, the seal
must completely cover the annular space between
the edge of the floating roof and tank wall.
LU.
The secondary seal must completely cover the
annular space between the external floating roof
and the wall
of the tank in a continuous fashion
except as allowed in subsection
(b)(2)(D)
below.
.~J.
Except
for automatic bleeder vents and rim space
vents,
each opening in a noncontact external
floating
roof must provide
a projection below the waste
surface.
Except for automatic bleeder vents,
rim
space vents,
roof drains,
and leg sleeves, each
opening
in
the
roof
is
to
be
equipped
with
a
gasketed
cover,
seal,
or
lid that
is to be maintained in a
closed position at all times
(i.e.,
no visible gap),
except when the device is in actual use.
Automatic
bleeder vents are to be closed at all times when the
roof
is floating, except when the roof
is being
200
floated off or
is being landed on the roof leg
supports.
Rim vents are to be set to open when the
roof
is
being
floated
off
the
roof
leg
supports
or
at
the manufacturer’s recommended setting.
Automatic
bleeder vents and rim space vents are to be gasketed.
Each emergency roof drain
is to be provided with a
slotted membrane fabric cover that covers at least
90
percent of the area of the opening.
p.).
The roof must be floating on the waste at all times
(i.e.,
off the roof leg supports),
except during
initial
fill until the roof is lifted off leg supports
and when the tank is completely emptied and
subsequently refilled.
The process of filling,
emptying, or refilling when the roof is resting on the
leg supports must be continuous and must be
accomplished as rapidly as possible.
1).
The owner or operator may elect to comply with Section
725.985(b) (2)
or (b)(3)
using an alternative means of
emission limitation
for which U.S. EPA has published
a
Federal Register notice in accordance with the requirements
of
40 CFR 60.114b permitting
its use as an alternative means
for the purpose of compliance with 40 CFR 60.ll2b.
h,).
Monitoring and inspection of the control equipment described in
subsection
(a)
above must be conducted as
follows:
U
After installation,
owners and operators of internal
floating roofs shall:
i.).
Visually inspect the internal floating roof, the
primary seal,
and the secondary seal
(if one
is in
service),
prior to filling the tank with waste.
If
there are holes,
tears,
or other openings in the
primary seal,
the secondary seal,
or the seal fabric,
or defects
in the internal floating roof,
or both, the
owner or operator shall repair the items before
filling the tank.
fl,).
For tanks equipped with
a liquid—mounted or mechanical
shoe primary seal, visually inspect the internal
floating roof and the primary seal or the secondary
seal
(if
one
is
in
service)
through
manholes
and
roof
hatches_on_the fixed roof at least once every 12
months after initial fill.
If the internal floating
roof
is not resting on the surface of the waste inside
the tank,
or there
is liquid accumulated on the roof,
or the seal
is detached,
or there are holes or tears
in the seal fabric, the owner or operator shall repair
the items or empty and remove the tank from service
within
45 days.
If a failure that
is detected during
inspections required in this subsection cannot be
repaired within 45 days and
if the tank cannot be
emptied within 45 days.
the Agency may grant the owner
or operator a provisional variance pursuant to Section
35(b)
of the Act that extends this time for up to 30
days.
Such
a
request
for
an
extension
must
comply
with 35
Ill. Adm. Code 180, and it must document that
alternate capacity
is unavailable and specify a
schedule of actions the owner or operator will take
that will assure that the control
equipment will be
201
repaired or the tank will be emptied as soon as
possible.
4.).
For tanks equipped with
a double-seal system
as
specified in subsection
(a)(1)(A)(ii)
above:
LI.
Visually inspect the tank,
as specified in
subsection
(b)(1)(D) below,
at
least every
5
years; or
Li.).
Visually inspect the tank as specified in
subsection
(b)(1)(B)
above.
pj.
Visually
inspect
the
internal
floating
roof,
the
primary seal, the secondary seal (if one
is
in
service),
gaskets, slotted membranes,
and sleeve seals
(if any)
each time the tank
is emptied and degassed.
If the internal floating roof has defects; the primary
seal has holes,
tears,
or other openings
in the seal
or the seal fabric; the secondary seal has holes,
tears,
or other openings
in the seal or the seal
fabric; the gaskets no longer close off the waste
surfaces from the
atmosphere;
or the slotted membrane
has more than 10 percent open area,
the owner or
operator shall repair the items as necessary,
so that
none of the conditions specified
in this subsection
exist before refilling the tank with waste.
In
no
event may inspections conducted
in accordance with
this provision occur at intervals greater than
10
years,
in the case of tanks conducting the annual
visual inspection
as specified
in subsection
(b)(1)(B)
above, or
at
intervals no greater than
5 years,
in the
case of tanks specified in subsection
(b)(1Y(C)
above.
~J.
Notify the Agency
in writing at least
30 days prior to
the filling or refilling of each tank for which an
inspection is required by subsections
(b)(1)(A)
and
(b)(1)(D)
above,
to afford the Agency the opportunity
to have an observer present.
If
the inspection
required by subsection
(b)(l)(D)
above
is not planned
and the owner or operator could not have known about
the inspection 30 days in advance of refilling the
tank,
the owner or operator shall notify the Agency at
least
7 days prior to the refilling of the tank.
Notification must be made by telephone
immediately
followed by written documentation demonstrating why
the inspection was unplanned.
Alternatively,
this
notification,
including the written documentation,
may
be made
in writing and sent by express mail so that it
is received by the Agency at least
7 days prior to the
refilling.
2.).
After installation, the owner or operator of an external
floating roof shall:
a,).
Determine the gap areas and maximum gap widths between
the primary seal
and the wall of the tank and between
the secondary seal and the wall
of the tank according
to the following
frequency:
LI.
Measurements of gaps between the tank wall and
the primary seal (seal gaps)
must be performed
202
during the hydrostatic testing of the tank or
within
60 days of the initial fill with waste
and at least once every five years thereafter.
LU.
Measurements of gaps between the tank wall and
the secondary seal must be performed within 60
days
of
the
initial
fill
with
waste
and
at
least
once per year thereafter.
iii)
If any tank ceases to hold waste for
a period of
one year or more,
subsequent introduction of
waste
into the tank must be considered an
initial fill for the purposes of subsections
(b)(2)(A)(i)
and
(b)(2)(A)(ii)
above.
~).
Determine the gap widths and areas
in the primary and
secondary seals
individually by the following
procedures:
LI
Measure
seal
gaps,
if
any,
at
one
or
more
floating roof levels when the roof
is
floating
off the roof
leg supports.
jj).
Measure seal gaps around the entire
circumference of the tank in each place where a
0.32—cm diameter uniform probe passes freely
(without forcing or binding against the seal)
between the seal and the wall of the tank and
measure the circumferential distance of each
such location.
iii)
Determine the total
surface area of each gap
described
in subsection (b)(2)(B)(ii’,
above by
using probes of various widths to measure
accurately the actual distance from the tank
wall to the seal and multiplying each such width
by its respective circumferential distance.
4.
Add the gap surface area of each gap location for the
primary seal and the secondary seal individually and
divide the sum for each seal by the nominal diameter
of the tank and compare each ratio to the respective
standards
in subsection (b)(2)(D) below.
p_I
Make necessary repairs or empty the tank within 45
days of identification in any inspection for seals not
meeting the following requirements:
LI
The accumulated area of gaps between the tank
wall and the mechanical
shoe or liquid—mounted
primary seal must not exceed 212
cm
per meter
(10.0
in2 per foot)
of tank diameter,
and the
width of any portion of any gap must not exceed
3.81 cm
(1.50
in).
One end of the mechanical
shoe
is to extend
into the waste contained in
the tank,
and the other end is to extend a
minimum vertical distance of
61 cm
(24.0 in)
above the waste surface.
There are to be no
holes, tears,
or other openings in the shoe,
seal fabric,
or seal envelope.
Lii.
The secondary seal
is to meet the following
203
requirements:
The secondary seal
is to be
installed above the primary seal so that
it
completely covers the space between the roof
edge and the tank wall
except as provided
in
subsection
(b)(2)(B)(iii) above.
The
accumulated area of gaps between the tank wall
and the secondary seal must not exceed 21.2 cm2
per meter
(1.00
in2 per foot)
of tank diameter,
and the width of any portion of any gap must not
exceed 1.27 cm (0.500 in).
There are to be no
holes,
tears,
or other openings in the seal or
seal fabric.
~j.
If
a failure that is detected during inspections
required
in subsection
(b)(2)(A)
above cannot be
repaired within 45 days and
if
the
tank
cannot
be
emptied within 45
days,
the Agency may grant the owner
or operator a provisional variance pursuant to Section
35(b) of the Act that extends this time for up to
30
days.
Such a request for an extension must comply
with 35
Ill. Adm. Code 180,
and
it must include
a
demonstration of the unavailability of alternate
capacity and a specification of a schedule that will
assure that the control equipment will be repaired or
the tank will be emptied as soon as possible.
fl
Notify the Agency
30 days
in advance of any gap
measurements required by subsection (b)(2)(A)
above,
to afford the Agency the opportunity to have an
observer present.
91
Visually inspect the external floating roof, the
primary seal,
secondary seal,
and fittings each time
the vessel
is emptied and degassed.
LI.
If the external floating roof has defects, the
primary seal has holes,
tears,
or other openings
in the seal or the seal fabric, or the secondary
seal has holes,
tears,
or other openings
in the
seal or the seal fabric, the owner or operator
shall repair the items as necessary so that none
of the conditions specified
in this subsection
exist before filling or refilling the tank with
waste.
Li.).
For all the inspections required by this
subsection,
the owner or operator shall notify
the Agency in writing
at least 30 days prior to
the filling or refilling of each tank to afford
the_Agency the opportunity to inspect the tank
prior
to
refilling.
If
the
inspection
required
by this subsection
is not planned and the owner
or operator could not have known
about the
inspection
30 days
in advance of refilling the
tank, the owner or operator shall notify the
Agency at
least seven days prior to the
refilling of the tank.
Notification must be
made by telephone immediately followed by
written documentation demonstrating why the
inspection was unplanned.
Alternatively, this
notification,
including the written
documentation, may be made
in writing and sent
204
by
express
mail
so
that
it
is
received
by
the
A~encvat least seven days prior to the
refilling.
~j.
Owners and operators that elect to install and operate the control
equipment in subsection
(a)
above shall
include the following
information
in the operating record
in accordance with the
requirements
of Section 725.990(a) (1)
and
(a)(11):
LI.
Internal floating roof.
~J.
Documentation that describes the control equipment
design and certifies that the control equipment meets
the specifications of subsections
(a)(1) and
(b)(1)
above.
fl.).
Records of each inspection performed as required by
subsections
(b)(1)(A) through
(b)(l)(D)
above.
Each
record must
identify the tank on which the inspection
was performed and must contain the date the tank was
inspected and the observed condition of each component
of the control equipment
(seals, internal floating
roof, and fittings).
~.
If any of the conditions described in subsection
(b)(1HB) above are detected during the annual visual
inspection required by subsection
(b)(1)(B) above, the
records must identify the tank, the nature of the
defects, and the date the tank was emptied or the
nature of and date the repair was made.
p.).
After each inspection required by subsection
(b)(1)(C)
above that finds holes or tears
in the seal or seal
fabric,
or defects
in the internal floating roof,
or
other control equipment defects
listed in subsection
(b)(l)(B) above, the records must identify the tank
and the reason
it did not meet the specifications of
subsection
(a’i(l) or
(b) (1) (C) above and describe each
repair made.
2.).
External floating roof.
i,).
Documentation that describes the control equipment
design and certifies that the control equipment meets
the specifications of subsections
(a)(2)
and
(b)(2)(B)
through
(b)(2)(D) above.
~J.
Records of each gap measurement performed as
required
by subsection (bU2)
above.
Each record must identify
the tank in which the measurement was performed,
the
date of measurement,
the raw data obtained
in the
measurement, and the calculations described in
subsections
(b)(2)(B)
and
(b)(2)(C)
above.
4.).
Records for each seal
gap measurement that detects
gaps exceeding the limitations specified by subsection
(b)(2)(D)
above that identifies the tank, the date the
tank was emptied or the repairs made,
and the nature
of the repair.
(Source:
Added at
19 Ill. Reg.
________,
effective
_____________________
205
SUBPART
DD:
CONTAINMENT
BUILDINGS
Section 725.1102
Closure and ~Post eClosure—eCare
a)
At closure of a containment building,
the owner or operator must
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. Adm.
Code 721.l03(ee)
applies.
The closure plan,
closure activities,
cost estimates for closure,
and financial responsibility for
containment buildings must meet all of the requirements specified
in 725.Subparts G and H.
b)
If,
after removing or decontaminating all residues and making all
reasonable efforts to effect removal or decontamination of
contaminated components,
subsoils,
structures,
and equipment as
required in subsection
(a)
above,
the owner or operator finds that
not all contaminated subsoils can be practicably removed or
decontaminated,
he must close the facility and perform post—
closure care
in accordance with the closure and post—closure
requirements that apply to landfills
(35
111. Adm. Code 725.310).
In addition,
for the purposes of closure,
post-closure, and
financial responsibility,
such a containment building
is then
considered to be a landfill,
and the owner or operator must meet
all
the
requirements
for
landfills
specified
in
725.Subparts
G
and
H.
(Source:
Amended at
19
Ill. Reg.
,
effective
_____________________
TITLE
35:
ENVIRONMENTAL PROTECTION
SUBTITLE G:
WASTE DISPOSAL
CHAPTER
I:
POLLUTION
CONTROL
BOARD
SUBCHAPTER
c:
HAZARDOUS
WASTE
OPERATING
REQUIREMENTS
PART
726
STANDARDS
FOR
THE
MANAGEMENT
OF
SPECIFIC
HAZARDOUS
WASTE
AND
SPECIFIC TYPES
OF
HAZARDOUS
WASTE MANAGEMENT FACILITIES
SUBPART C:
RECYCLABLE
MATERIALS
USED
IN A MANNER
CONSTITUTING DISPOSAL
Section
726.120
Applicability
726.121
Standards
applicable
to
generators
and
transporters
of
materials
used
in
a
manner
that
constitutes
disposal
726.122
Standards applicable to storers, who are not the ultimate users,
of materials that are to be used in a manner that constitutes
disposal
726.123
Standards e~pplicableto ~*jisereof ffiMaterials that are
~tJsed
in a
manner that e4onstitutes 4Q,isposal
SUBPART
D:
HAZARDOUS
WASTE
BURNED
FOR
ENERGY
RECOVERY
Sect ion
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)
206
Standards applicable to burners of hazardous waste fuel
(Repealed)
Conditional exemption for spent materials and by—products
exhibiting a characteristic of hazardous waste (Repealed)
SUBPART
E:
USED OIL BURNED FOR ENERGY RECOVERY (Repealed)
Applicability
(Repealed)
Prohibitions
(Repealed)
Standards applicable to generators of used oil burned for energy
recovery
(Repealed)
Standards applicable to marketers of used oil burned for energy
recovery
(Repealed)
Standards applicable to burners of used oil burned for energy
recovery
(Repealed)
SUBPART
F:
RECYCLABLE
MATERIALS
UTILIZED
FOR PRECIOUS METAL
RECOVERY
Section
726.170
Applicability and requirements
SUBPART G:
SPENT LEAD-ACID BATTERIES BEING RECLAIMED
Section
726.180
Applicability and requirements
SUBPART H:
HAZARDOUS WASTE BURNED IN BOILERS
AND INDUSTRIAL FURNACES
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
726.Appendix A
726.Appendix B
726.Appendix C
726.Appendix D
726.Appendix E
726.Appendix F
726.Appendix G
726.Appendix H
726.Appendix
I
726.Appendix
3
726.Appendix K
726.Appendix L
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
Reference Air Concentrations
Risk
Specific
Doses
Stack Plume Rise
Health—Based Limits
for Exclusion of Waste-Derived Residues
Potential PIC8 for Determination of Exclusion of Waste—
Derived
Residues
Methods Manual for Compliance with BIF Regulations
Guideline on Air Quality Models
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
Mercury—Bearing Wastes That May Be Processed
in Exempt
Mercury Recovery Units
Exempt Quantities for Small Quantity Burner Exemption
726.
135
726. 136
Section
726.140
726.141
726.142
726.143
726.144
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
726.Appendix M
726.Table A
207
AUTHORITY:
Implementing
Section
22.4
and
authorized
by
Section
27
of
the
Environmental Protection Act
(415 ILCS 5/22.4 and
27.
SOURCE:
Adopted in R85-22
at 10
Ill. Reg.
1162, effective January
2,
1986;
amended in R86—1 at
10 Ill.
Reg.
14156, effective August
12,
1986;
amended in
R87-26 at
12
Ill.
Reg.
2900,
effective January 15,
1988; amended in R89—1 at
13
Ill.
Reg.
18606, effective November 13,
1989;
amended in R90—2
at
14 Ill.
Reg.
14533,
effective
August
22,
1990;
amended
in
R90—11
at
15
Ill.
Reg.
9727,
effective
June
17,
1991;
amended
in
R9l—13
at
16
Ill.
Reg.
9858,
effective
June
9,
1992;
amended in R92—10 at
17
Ill.
Reg.
5865,
effective March 26,
1993;
amended in R93—4 at 17
Ill.
Reg.
20904, effective November 22,
1993;
amended
in
R94—7
at
18
Ill.
Reg.
12500,
effective
July
29,
1994;
amended
in
R95—6 at 19
Ill.
Reg.
________,
effective
_____________________
SUBPART C:
RECYCLABLE MATERIALS USED IN A
MANNER
CONSTITUTING DISPOSAL
Section 726.120
Applicability
a)
The regulations of this Subpart apply to recyclable materials that
are applied to or placed on the
land-i.~
1)
Without mixing with any other substance(s); or
2)
After mixing or combination with any other substance(s).
These materials will be referred to throughout this Subpart
as “materials used in a manner that constitutes disposal.”
b)
Products
produced
for
the
general
public’s
use
that
are
used
in
a
manner that constitutes disposal and that contain recyclable
materials are not presently subject to regulation under this
Subpart
if the recyclable materials have undergone a chemical
reaction in the course of producing the products
so as to become
inseparable by physical means and
if such products meet the
applicable treatment standards in 35
Ill.
Adm.
Code 728.Subpart
D
(or
applicable
prohibition
levels
in
35
Ill.
Adm.
Code
728.132
or
728.139, where no treatment standards have been established)
for
each
recycable
material
(i.e.
hazardous
waste)
that
they
contain.
Commercial
fertilizers that are produced for the general public’s
use
that
contain
recyclable
materials
also
are
not
presently
subject to regulation, provided they meet the same treatment
standards
or
prohibitions
levels
for
each
recyclable
material
they
contain.
However,
zinc—containing
fertilizers
using
hazardous
waste
K061
that
are
produced
for
the
general
public’s
use
are
not
presently subject to regulation under this Subpart.
ç).
Anti-skid
and deicing uses in
a manner constituting disposal of
slags that are generated from high temperature metals recovery
(HTMR)
processing
of
hazardous
wastes
1(061,
1(062,
and
F006
are
not
covered by the exemption in subsection
(b)
above,
and such uses of
these
materials
remain
subject
to
regulation.
(Source:
Amended at 19
Ill.
Reg.
________,
effective
______________________
Section
726.123
Standards
a~pplicable
to
i~sers
of
mMaterials
that
are
~jsed
in a m~annerthat e4onstitutes ~flisposal
a)
Owners
or
operators
of
facilities
that
use
recyclable
materials
in
a
manner
that
constitutes
disposal
are
regulated
under
all
applicable provisions of
35
Ill.
Adm. Code 702,
703,
and 705;
35
Ill.
Adm.
Code 724.Subparts
A through
N;
and 35 Ill. Adm. Code
208
725.Subparts
A
through
N~L35
Ill.
Adm.
Code
728;
and
35
Ill.
Adm.~
Codc
702,
703
and
705,
and
the
notification
requirement
under
Section
3010
of
the
Resource
Conservation
and
Recovery
Act.
(These
requirements
do
not
apply
to
products
whiohthat
contain
these
recyclable
materials
under
the
provisions
of
Section
726.120(b)).
b)
The
use
of
waste
or
used
oil
or
other
material~7~whichthat
is
contaminated with dioxin or any other hazardous waste (other than
a
waste
identified
solely
on
the
basis
of
ignitability)7
for
dust
suppression
or
road
treatment
is
prohibited..).
(Source:
Amended
at
19
Ill.
Reg.
________,
effective
______________________
SUBPART
H:
HAZARDOUS
WASTE
BURNED
IN
BOILERS
AND
INDUSTRIAL
FURNACES
Section
726.200
Applicability
The regulations
of this Subpart apply to hazardous waste burned or
processed in a boiler or industrial furnace
(BIF)
(as defined in
35
Ill. Mm.
Code 720.110)
irrespective of the purpose of burning
or processing, except
as provided by subsections
(b),
(c),
(d)4.
and
(f)7
below.
In
this
Subpart,
the
term
“burn”
means
burning
for energy recovery or destruction7 or processing for materials
recovery or
as an ingredient.
The emissions standards of Sections
726.204,
726.205,
726.2064, and 726.207 apply to facilities
operating under interim status or under a
RCRA
permit3, as
specified in Sections 726.202 and 726.203.
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 72l.Subpart
C.
Such
used
oil
is
subject
to
regulation
under
35
Ill.
Adm.
Code
7394,
rather
than
this
Subpart;
2)
Gas
recovered
from
hazardous
or
solid
waste
landfills4,
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) (Efl) through
(a)(3)(HF)7 and hazardous wastes that are subject to the
special requirements for conditionally exempt small quantity
generators
under
35
Ill.
Adm.
Code 721.105; and
4)
Coke
ovens,
if
the
only
hazardous
waste
burned
is
~
Ht~azardousWwaste ~no. 1(0877 decanter tank tar sludge from
coking operations.
c)
Owners
and
operators
of
smelting,
melting4,
and
refining
furnaces
(including
pyrometallurgical
devices
such
as
cupolas,
sintering
machines,
roasters and foundry furnaces,
but not including cement
kilns, aggregate kilns4, 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
209
or operator of
a metal recovery furnace or mercury recovery
furnace shall comply with the following requirements, except
that an owner or operator of a lead or a nickel—chromium
recovery
furnace7
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)7
below:
A)
Provide
a
one-time
written
notice
to
the
Agency
indicating the following:
i)
The
owner
or
operator
claims
exemption
under
this subsection;
ii)
The hazardous waste is burned solely for metal
recovery consistent with the provisions of
subsection
(c)(2)7
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 comply 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
720.1114,
or
alternative
methods
that
meet
or
exceed
the
SW—846
method
performance capabilities.
If SW—846 does not
prescribe a method for a particular determination, the
owner or operator shall use the best available method;
and
C)
Maintain
at
the
facility
for
at
least
three
years
records
to
document
compliance
with
the
provisions
of
this subsection including limits on levels of toxic
organic constituents and Btu value of the waste,
and
levels of recoverable metals in the hazardous waste
compared to normal nonhazardous waste feedetocks.
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
72l.Appendix H7 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 prohibited4, 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
210
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)7 above.
3)
To
be
exempt
from
Sections
726.202
through
726.211,
an
owner
or operator of a lead4, GE—nickel—chromium,
or mercury
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
specifying whether the owner or operator claims an exemption
for each waste under this subsection or subsection (c)(1)7
above.
The owner or operator shall comply with the
requirements of subsection (c)(l)7 above7 for those wastes
claimed
to
be
exempt
under
that
subsection
and
chall
oomp-ly
with the following requirements bclow for those wastes
claimed to be exempt under this subsection-’j
A)
The hazardous wastes listed in Sections 726.Appendices
1(4,
and
L,
and
M
and
baghouse bags used to capture
metallic dusts emitted by steel manufacturing are
exempt
from
the
requirements
of
subsection
(c)(1)7
above,
provided that:
i)
A
waste
listed
in
Section
726.Appendix
K
must
contain recoverable levels of lead’r~Aa waste
listed in Section 726.Appendix L must contain
recoverable levels of nickel or chromium.~...,~.
waste listed in Section 726.Appendix M must
contain recoverable
levels of mercury and
contain less that 500 ppm of 35
Ill. Adm. Code
261.Appendix H organic constituents, and
baghouse bags used to capture metallic dusts
emitted by steel manufacturing must contain
recoverable levels of metal;
and
ii)
The waste does not exhibit the Toxicity
Characteristic of
35
Ill. Adm. Code 721.124 for
an organic constituent; and
iii)
The waste is not
a hazardous waste listed in 35
Ill.
Adm.
Code 721.Subpart D because
it
is
listed for an organic constituent4, 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)7 above7 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 (~Q)(l)(B),-
above,
and records to document compliance with
subsection
(c)(3)-,. above7 must be kept for at
least three years.
211
B)
The Agency may decider on a case—by—case baais~that
the toxic organic constituents
in a material listed in
Section 726.Appendix K~or Soction 726.Appendix
L,
or
726.Appendix M that contains a totalconcentration
of
more than 500 ppm toxic organic compounds listed in 35
Ill.
Adm.
Code 721.Appendix H may pose
a hazard to
human health and the environment when burned in a
metal recovery furnace exempt from the requirements of
this Subpart.
In that aituationUnder these
circumstances,
after adequate notice and opportunity
for comment, the metal recovery furnace will become
subject to the requirements of this Subpart when
burning that material.
In making the hazard
determination, the Agency shall consider the following
factors:
i)
The concentration and toxicity of organic
constituents
in the material;
and
ii)
The level
of destruction of toxic organic
constituents provided by the furnace;
and
i~ii)
Whether the acceptable ambient levels
established in Section 726.Appendieee~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~er—ruthenium,
or any combination of these metals-,-
are conditionally exempt from reg ulation 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 this
Section-~-~
B)
The hazardous waste is burned for legitimate recovery
of precious metal~-~
and
C)
The owner or operator will comply with the sampling
and analysis and recordkeeping requirements of this
Section,-j
2)
Sample and analyze the hazardous wastes
as necessary~to
document that the waste is burned for recovery of
212
economically significant amounts of precious
metal4., using
procedures specified by Test Methods
for Evaluating Solid
Waste,
Physical/Chemical Methods,
SW—846,
incorporated by
reference in
35
Ill.
Adm. Code 720.1114, 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)
Maintain4, at the facility for at least three years4, records
to document that all hazardous wastes burned are burned for
recovery of economically significant amounts of precious
metal.
g)
~breviations
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,
cadmium4, and
chromium.
“CO” means carbon monoxide.
“Continuous monitor”
is
a monitor whichthat continuously
samples the regulated parameter without interruption,
~that
evaluates the detector response at least once each
15
seconds, and that computes and records the average value
at least every 60 seconds.
“DRE” means destruction or removal efficiency.
“cu m” or
“rn3” means cubic meters.
“E” means
“ten to the_power”.
For example,
“XE—Y” means
“X
times ten to the —Y power”.
“Feed rates”
are measured
as specified in Section
726.202(e) (6).
“Good engineering practice stack height”
is as defined by 40
CFR 51.100(u),
incorporated by reference in 35
Ill.
Adrn.
Code 720.111.
“H~means hydrocarbon.
“HCl” means hydrogen chloride gas.
“Hourly rolling average” means the arithmetic mean of the 60
most recent tone—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
213
concentration.
“Noncarcinogenic metals” means
antimony, barium,
lead,
mercury, thallium4, 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.
RACe
are specified in Section 726.Appendix
D.
“RSD” means risk—specific dose,
the acceptable ambient level
for the carcinogenic metals for purposes of this Subpart.
RSDs are specified
in Section 726.Appendix E.
“SSU” means
“Saybolt Seconds Universal”,
a unit of viscosity
measured by ASTM D_88~ or D2l6l~i, 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
Congenera”
in Section 726.Appendix
I
(“cyc”).
“~g” means microgram.
(Source:
Amended at
19
Ill.
Reg.
________,
effective
______________________
Section 726.Appendix A
Tier
I and Tier
II Feed Rate and Emissions Screening
Limits for Metals
214
I-A
Tier
I
and Tier
II
Feed Rate and Emissions Screening Limits for
Noncarcinogenic Metals
for Facilities in Noncomplex Terrain
(Values for urban areas
TESH
(m)
Antimony
Barium
Lead
Mercury
Silver
Thallium
(g/hr)
(g/hr)
(g/hr)
(g/hr)
(g/hr)
(g/hr)
4
6Q.E+01
l,-0000.E-44
1-r8.E+01
6-rO.Ef01
6rOO.E102
6-~-0.E+0l
4
6
6-~-84,E+0l
l~,~1O00.&4~OL
2-1-04,E-4-Ol
4
6,-8.E+0l
6-r80.E+02
6-,-8.E+0l
8
7~-64,E+0l
1r3000.B~4 2-r3.E+0l
4
7-r6.E+01
7~-60.E+02
7,-6.E+Ol
10
8-~-64,E+0l
1,-4000.E4-G
2-,-6.E+01
4
8-~-6.E±Ol
8-~-60.E+02
8-1-6.E+0l
12
9-r64,E+01
1’r7000.~+G3-~-0.Ef0l
4
9-r6.E+01
9~60.Ef02
9,-6.E+0l
14
1-,-1E+02
1-,-8000.E+O
3-,,-4.E+Ol
4
l-,-lE+02
1-,rlOO.E+03
l-rlE+02
16
1-r3Q~Ef02
2-~-1000.E+G3-r6.E+Ol
4
1-~-30.E+02
l--300.E+03
l-r30.E+02
18
1-~-4Q~E+02 2-,~-4000.E+O 4-1-3.E+Ol
4
l-r40.E+02
l~400.E+03 l-1-4E+02
20
1r6Q4,E+02
2r7000.B+G
4-r6.E+Ol
4
1-~-60.E~02
1,600.E+03
l-r60.E+02
22
1-,-8~E+02
3-,-0000.E44
5-~,-4.E+0l
4
l-r8Q~E+02
1-r800.E+03
1-1-8E+02
24
2,-OE+02
3-~-4000.B446~-0~E+0l
4
2-~-0Q~E+02
2--000.Ef
03
2-r0Q~E+02
26
2-r3Q4,E+02
3r9000.B44
6-r-8.E+01
4
2~~-30.E+02 2-r300.E+03
2-~-30.E+02
28
2-~-6Q~E+02
4-,-3000.B+G
7,-8.E+Ol
4
2-r6Q~EI02
2r600.E+03
2-r-6E+02
30
3-,rOO.E+02
5r0000.E+O
9-rO.E+0l
4
3vOE+02
3~0
E+03
3~00.E+02
35
4,-00.Et02
6--6000.S44
l~-10.E+02
4
4-rOO.E+02
4~000.E+03 4r00.E+02
40
4r6E+02
7~8000.E+O
1-r40.E+02
4
4~60.E+02
4~600.E+03
4~60.E+02
45
6-~-0Q~E+02 1--0O000.~-4- l-8Q~E+02
~&
6,-OE+02
6--000.Et03
6-~-00.E+02
50
7-1~8Q4,E+02
1-~-30000.~+ 2-~-3Q~E+02
~&
7-~-8Q~E+02
7-,-8
E+03
7-r80.E+02
55
9-T-60.E+02
1-,r-70000.E+
3rOO.E+02
G4
9~60.E+02
9r600.E+03
9~r60.E+02
60
1-~-2E+03
2-,-00O00.E~l-
3-~-6Q~E+02
~&
l-,-200.E+03
1-1-2000.E+O
4
l-1-2QQ~E+03
65
1-r5QQ~E+03 2~50000.B+ 4--30.Et02
~&
l,500.E+03
l~5000.B+~
4
l~500.E+03
70
1,-7E+03
2~-80000.E+ 5-rOQ4,E+02
4~
l-r7QQ~E+03 1-r7000.~+O
4
1~r7QQ4,E+03
75
l,-9Q~E+O3 3-~-20000.B+ 5-r80.E+02
G&
1-~9Q~E103l,’9000.E+~
4
1r9E+03
80
2-,r2E+03
3-r60000.~+
6-r40.E+02
~&
2-r200.E+03
2-,-2000.E44
4
2-r200.E+03
85
2-~-5QQ~,Ef
03
4-~00000.~+ 7-~-60.E+02
~,
2,-500.g+03
2,~-5000.B-~4
4
2-,-500.Ef03
90
2-~-8QQ4,E+03 4-~-60000.&+ 8-T-2~~E+02
O.&
2--8QQ4,E-+0-3
2-,-8000.~+~
4
2-~-800.E+03
95
3r2E+03
5’~4OOOO.E+ 9r60.E+02
G&
3~200.E+O3 3~2000.E+~
4
3r200.E+03
215
100
3--6QQ4,E+03
6-r00000.E+
1-~l
E+03
3r6
E+03
3,~6000.E+G
3-r600.E-#03
4
105
4-~-0QQ4,E+03 6-,-80000.E+
1-~-2QQ.~E+034-r000.E+03
4,~-0000.~+~
4-r000.E+03
04
4
110
4,-6E+03
7-r80000.B+ l~400.E+03 4r600.Ef03
4-~-6000.~+G
4-r600.E~03
05
4
115
5-.-4QQ4,E+03
8,-60000.E~+ l-1-6QQ~E+03 5-~-4
E-I-03
5,,-4000.&+4
5-~-400.E+03
0-4
4
120
6--OQQ4,E-l-03
1,-000000.~ l--8QQ~E-I-03 6--0~Q~E-F036,-0000.~-+G 6-r000.C1-03
+G6
4
I-B
Tier
I and Tier
II Feed Rate and Emissions Screening Limits
for
Noncarcinogenic Metals for Facilities
in Noncomplex Terrain
(Values for rural areas
TESH
(m)
Antimony
Barium
Lead
Mercury
Silver
Thallium
(g/hr)
(g/hr)
(g/hr)
(g/hr)
(g/hr)
(g/hr)
4
3-,-14,E+Ol
5-~-2QQ~E+039.4E+0O
3-,-1.g+01
3,-1E+02
3-,-1.E+01
6
3-r6.E+Ol
6-r000.E+03
1,rl.E~0l
3,-6.E+01
3-~-60.E+02
3-~-6.E*0l
8
4r0.E+Ol
&r800.E+03
1’r2.E10l
4-z-O.~+O1
4-z-00.E+02
4-,rO.EfOl
10
4-1-64,E+Ol
7~-89Q~E+031-~-4.E+01
4-~-6,~E+0l
4-~-60.E-*-02
4-~-64,E+01
12
5~8.E+0l
9r600.E+03
l-r7.g+01
5-~-8.E+01
5--80.E+02
5-r8.E+0l
14
6v84,E+0l
l-,-l000.~44 2-~-l.E+0l
6-~-8.E+01
6--80.E+02
6-~-8.E+0l
4
16
8-r6.E+01
l,-4000.E-+0
2-,r6.E+Ol
8-6.E+01
8-1-60.E+02
8-.-6.E+01
4
18
1rlE+02
l,-8000.E+G
3-~-2.E1~0l
lrlO.E+02
1-~-100.E+03 1-~-10.E+02
4
20
1-r3~E+02
2,-2000.&40
4-,-0.E+0l
1~-3E+02
1’T-300.E+03
1-~-30.E+02
4
22
lr7O.E+02
2r8000.~+G5-~0.E+01
l~70.E+02
l~-700.E+03 1-r70.EF02
4
24
2--2Q~E+02
3-,~-6000.E-44 6-~-4.~+0l
2~-2Q~E+02 2-~-2QQ~E+032-1-2Q~E+02
4
26
2r8E+02
4,-6000.~+G8,-2.E+Ol
2-r80.E±02
2’-r800.Ef03
2-,-80.E102
4
28
3,-5E-I-02
5-,-8000.E-44
1-.-00.E+02
3-~-50.E+02
3~-5QQ~E+033-~-5Q~E+02
4
30
4-r3E+02
7-r6000.~#01~30.E+02
4r30.E+02
4r300.E+03
4r30.E+02
4
35
7-~-2E+02
l~,-20000.E+2-~-1E+02
7-,-2E+02
7r2
E+03
7~20.E+02
04
40
1-ri
E+03
l-~-80000.B+3r20.E+02
l-riOO.E+03
1iri000.~+G l-~-100.Ef03
0?-
4
45
lr500.E+03
2r50000.E+ 4r60.E+02
1-,-500.E+03
l-,-5000.&44
1-rSOO.E+03
04
4
50
2rOE+03
3r30000.E+ 6r00.E+02
2r000.E+03
2r0000.~44 2r000.E+03
0-4
4
55
2-~-6QQ~E+034-~-40000.E+ 7-r80.E-i-02
2-T-600.E+03
2r6000.~+0 2-r600.E+03
0-4
4
60
3-r4~Q~E+03
5,r80000.~+1r000.E+03
3-r400.E+03
3r4O00.E+~ 3-r400.Et03
05
4
65
4-~-6QQ~E+037-,-60000.E*
l,-4
E+03
4-,-600.E+03
4-T-6000.&1-0
4-~-600.E+03
04
4
70
5,-4E+03
9’r00000.~+
1r600.E+03
5r400.E+03
5r4000.E+G 5r400.E+03
04
4
75
6r4E+03
l-~-i0O000.E
1-~-900.E+03
6-r400.E+03
&r4000.E44
6400.E+03
+46
4
80
7r600.E-F03
1-~-30O000.~2-r300.E103
7-~-600.E+03 7r6000.B+G
7r600.E103
+0-6
4
216
85
9-r400.E+03
1-r500000.~2r800.E+03
9r400.E+03 9400O.~+G 9r400.E+03
+0-6
4
90
1ri000.E+0
1,r800000.~
3r300.E+03
1.ri000.E+Q
i-,-10000.E+
1-rl000.E+0-
4
+46
4
04
4
95
1~-3000.~+02-r200000.g
3-r900.E+03
1-r3000.B+0-
130000.~+ 1-r3000.~+G
4
+0-6
4
94
4
100
1~5000.&ê4 2~-600000.~4-~~-600.E+0315000.&40- 150000.E+ 1-~50OO.E+G
4
+46
4
94
4
105
1-T-8000.~+G 3r000000.~5~400.E+03 lr8000.E+9
1r80000.B+ 1r8000.B+0-
4
+05
4
44
4
110
2-r2000.&44
3r600000.g 6-r600.E+03
21-2000.E+0 2,-2000O.~+2-~~-2OOO,B+G
4
+06
4
0-4
4
115
2~600O.&44 4r400000.~
7r800.E+03
2-r6000.~+G2r60000.B+ 2-r6000.E+G
4
+0-6
4
0-5
4
120
3v4000.~+0 5r000000.~ 9r200.E+03
3r1000.E+O 3r10000.E+
3-~-1O00.E+0-
4
.446
4
0-4
4
I-C
Tier
I and Tier
II Feed Rate and Emissions Screening Limits
for
Noncarcinogenic Metals
for Facilities
in Complex Terrain
Values for urban and rural areas
TESH
(m)
Antimony
Barium
Lead
Mercury
Silver
Thallium
(g/hr)
(g/hr)
(g/hr)
(g/hr)
(g/hr)
(g/hr)
4
1-v-4.E+0i
2r400.E+03
4.3E+00
1r4.E+01
1r40.E+02
lir4.E+Ol
6
2rl.E+01
3r500.E+03
6.2E+00
2rl.E+01
2r10.E+02
2-rl.E+0i
8
3r0.E+0i
5r000.E+03
9.2E+00
3r0.E+0l
3-~-00.E+02
3-rO.E+0l
10
4,r3.E+0i
7-r600.Ef03
1r3.E+01
4r3.E+01
4r30.E+02
4r3.EfOl
12
5r44,E+0i
9000.E+03
1r7.E+01
5,4.E+Ol
5~40.E+02
5r4.E+0l
14
6-,r8.E+0l
1-,-1000.E+0
2-~-O.E+01
6-r8.E+0i
&r80.E+02
6r8.E+Ol
4
16
7r8.E+0i
13000.~+0-2r4.E+01
7r8.EFO1
7r80.E+02
7-r8.E+01
4
18
8r64,E+0i
14000.&44 2r6.E+01
8r6.E+01
8r60.E+02
8-,-6.E+01
4
20
9r64,E+01
1r6000.E+G
2-r9.E+0l
9r6.E+0i
9r60.E+02
9r6.E1~01
4
22
l00.E+02
18000.E+0
3r2.E+0i
1r00.E+02
l’r000.E+03
l-rOO.E+02
4
24
1-r20.E+02
1r9000.S+0-
3r5.E+0i
1r20.E+02
1-~2O0.E+03
1-r20.E+02
4
26
130.E+02
2r2000.B+9
3r6.E+0i
1r30.E+02
l-,-300.E+03
1-~-3O.E+02
4
28
lr4Q4,E+02
2r4000.E+G 4r3.E+01
1-r40.E+02
1-~-400.E+03 1r4O.E1~O2
4
30
i-r60.E+02
2,r7000.E+0
4-1-6.E+0l
lrGO.E+02
1,-600.E+03
i,,-60.E+02
4
35
2--00.E+02
3r3000.E+G
5r8.E+Ol
2r00.E+02
2r000.Et03
2~r00.I~+02
4
40
2-r40.E+02
4r0000.E+9
7-,-2.E+Ol
2r40.E+02
2r400.E+03
240.E+02
4
45
3r00.E~02
5r0000.B+0 9rO.E+Ol
3r00.E+02
3r000.Et03
3r00.ET02
4
50
3-,r60.E+02
6-,~-0000.~+91-1-10.E+02
3-~-60.E+02
3-,-600.E+03
3-1-60.E+02
4
55
4-,-60.E+02
7~-6000.E44
1r40.E+02
4r60.E+02
4r600.E±03
4r60.E+02
4
60
5-,r80.E+02
9w4000.E+0
1-r70.E+02
5r80.E+02
5r800.E+03
5r80.E+02
4
65
6r8Q4,E+02
1~10000.B+2-riO.Ef02
6r80.E+02
&r800.Ef03
6-r80.E+02
217
0-5
70
7-r80.E~02
1—r3OO0Q.~+
2-r40.E+02
7r80.E+02
7r800.E±03
7r80.E+02
0-4
75
8-,-60.E+02
l-r40000.E+
2-,-60.E+02
8~60.E+02
8600.E+03
&~60.E+02
0-4
80
9-~-60.E+02
i-r60000.E+
2,-90.E+02
9r60.E+02
9r600.Ef03
9-rGO.E102
04
85
1100.E+03
lr80000.E+
3-~-30.E+02
1-~-i00.E+03 1,rl000.E+4
i-~-10O.E+03
0-5
4
90
1200.Ef
03
2~r00000.B+ 3r60.Ef02
1200.E+03
12000.E+4
i-r200.Ef03
0-5
4
95
1-~-400.E+03 2,,-30000.E+
4-rOO.E+02
1,-400.E+03
l-.r4000.E44
1-r400.E+03
05
4
100
1-r500.E+03
2-r60000.B+
4-r60.E+02
l-r500.E+03
1-~-5000.E+G 1-r500.E+03
0-4
4
105
1r700.E+03
2r80000.&4~
5r00.E+02
l-r-700.E+03
l-,-7000.~+9
1-1-700.E+03
0-5
4
110
1-r900.E+03
3r20000.E+
5-r80.E+02
i-T-900.E+03
l-~-9000.~+4
1-r900.E+03
0-4
4
115
2~400.E+03360000.S+
6-r40.E+02
2rlOO.E+03
2,-1000.E+O
2-,-100.E+03
0-5
4
120
2r4QQ~E±034r00000.B+
7,20.Et02
2r400.E103
2-r4000.E+G
2-s-400.E+03
04
4
I—D
Tier
I and Tier II Feed Rate and Emissions Screening Limits
for
Carcinogenic Metals for Facilities
in Noncomplex Terrain
Values for use in urban areas
Values for use in rural areas
TESH
Arsenic
Cadmium
Chromiu
Berylli
Arsenic
Cadmium
Chromiu
Berylli
(m)
(g/hr)
(g/hr)
m
urn
(g/hr)
(g/hr)
m
urn
(g/hr)
(g/hr)
(g/hr)
(g/hr)
4
0.4-r6E
1.
1E+00
0.1,-7E
0.8-,-2E
O.2r4E
0.5r8E
0.08,-6
0.4-~-3E
04
04
04
04
04
-04
04
6
0.5r4E
1. 3E+00
0.lr9E
0.9r4~
O.2r8E
0.6v6?-
0.lrOE
0.5,~0E
04
04
04
04
04
04
8
0.6r0~
1. 4E+00
0.2-~-2E
1. 1E+00
0.3-~-2E
O.7,6E
0.lrlE
0.5-r6E
04
04
04
94
04
04
10
0.6r8~
1.
6E+00
0.2r4E
1.
2E1 00
O.3r6~
0.865
O.l-r3?-
0.6,-4~
04
04
94
04
04
04
12
0.7r6~
1. 8E+00
O.2r7&
1. 4E+00
0.4-r3~
1. lE+00
O.l-,-6&-~
O.7~,-8g
04
0-4
04
04
94
14
0.8r6B
2.1E+00
O.3r1B
1.5E+00
0.5-r4E
l.3E+00
0.2r05
0.9r6E
04
04
94
04
94
16
0.9r6E
2.3E+00
0.3r5E
1.7E+Q0
0.6-r8E-
1.6E+00
0.2-,-4~
1.2E+00
94
94
04
94
18
1.1E-4-00
2.6E+00
O.4-rOE.
2.OE+00
0.8r2?-
2.OE+00
0.3rOE
1.5E+00
0-4
04
04
20
1.2E+00
3.OE+00
0.4r4E
2.2E+00
l.OE+00
2.5E+00
O.3r7E
1.9E±OO
94
04
22
1.4E+00
3.4E+00
0.5r0?
2.5E+00
l.3E+00
3.2E+00
0.4i-8E
2.4EfOO
04
04
24
1.6E+00
3.9E+0O
0.5r8B
2.8E+00
1.7E+00
4.OE+00
O.6-,-0~ 3.OE+00
04
04
26
1.8E+00
4.3E~00 0.64&
3.2E+00
2.1E100
5.OE+00
O.7r6E
3.9EF0O
04
94
28
2.OE+00
4.8E+00 0.72~
3.6E+00
2.7E+00
6.4E+00
0.9r8E
5.OE+00
04
04
30
2.3E+00
5.4E+00
0.8r2E
4.OE+O0
3.5E+00
8.2E+00
1.2E+00
6.2E~00
218
04
35
3.OE+00
6.8E+00
1.0E400
5.4E+00
5.4E100
l~3.~+Gl.9E+00
9.6E+00
4-
40
3.6E+00
9.0E+00
1.3E+00
6.8E+00
8.2E+00
2-v-0.&44
3.OE+pO
15.E+0
4-
4-
45
4.6E+00
l,-l.~+G l.7E+00
8,6E+00
1-rl.E+G
2-r84,E+9
4.2E+00
2rl4,~+0-
4-
4-
-1-
4.
50
6.OE+O0
l-r4~+G 2.2E+00
1-ri4,E+Q
1-r54,E+0
3r7,~+9
5.4E+00
2r8~E+4
4.
4-.
4-
4-
4.
55
7.6E+O0
i’r8.E+G
2.7E+00
1-r4.~+G
2-1-0.E+9
5rO.B44
7.2E+00
3-r6.~+G
4-
4-
4-
4-
4-
60
9.4E+00
2r2+4
3.4E+00
1r7+4
2,-7.E+0
6~4~E+0
9.6E+00
4~,r8.&44
.4
-4
4-
.4
4.
65
1-,r1.B+G
2~-8.B+G 4.2E+00
2,-i.E+0-
3-,-6.B+9
8-v6.~+9
ir3.~+0-
6’r4.E+G
-1-
4.
.4
.4
.4
.4
.4
70
1-r3.E44
3~-1.E+0 4.6E+00
2v4.E+0
4-r3.~E+0 ir0Q,~E+ 1r5,~,E+0 764,E+0
4-
4.
4-
4-
04
4-
4.
75
i-r5.B+G
3r6.B+G
5.4E+00
2r7.~+9-
5r0.E+9
1,20.E+
1r8.~+G
9r0.~+G
.4
4.
.4
4.
0-a
4-
4.
80
i-r7.&44
4ir0.E+0
6.OE+00
3rO.E+0
6r0.E+O
l,40.E+
2-~-2.~+9 i~-l0.~+
.4
4.
.4.
4-
9--a
4-
04
85
i-r9.B+0-
4r6.~+G
6.8Et00
3r4.~+0
7r2.5+9
i,-70.B+
2r6.E+9
1r30.B+
&
-4
4-
4-
0-2-
4.
02-
90
22.E+0
5r0.E+0
7.8E+00
3-,-9.E+0
8-,-6.E+0
2-rOO.E+
3-,-0.E+0
i-.-50.E+
.4
.4.
-4.
-4
9-2-
4.
04
95
2ir5.B+G
5r8.B40
9.OEFOp
4-r4.E+0
1r00.E+
2r40.E4
3r6.E+0
i-r80.B+
4
4-
4-
0-a
02-
-4
04
100
2r8.B+O
6-r8.&44
1~r0.E+0 5,0.~+9 120.E+
2r90.E+
4-r3.E+0
2r20.E4
4-
4.
-4.
4.
04
0-2-
4-
04
105
3-r2.B+G
7~-6.B+G 1-,-i.E.44
5-s-6.E+G
1-r40.B+
3-r40.E+
5,-0.E+9
2-r60.B+
4
4-
-4
4-
02-
02-
4-
04
110
3-,r6.E+G
8r6.E+G
l’r3.E+0
6-r4.E+0
1r70.E+
400.E+
6rO.+0
300.E+
4-
.4.
-4
04
92-
4-
92-
115
4-rO.B+G
9r6.B+G
1-r5.B+G
7r2.B+0-
2r00.B+
4-r80.E+
7r2.~44
360.E+
4
-4
4-
4.
0-2-
02-
4.
04
120
4-,r6.E40
1riO.E+
l,-7.E+0
8~,-2.E+0
2r40.E+
5,80.E+
8~r6.+0
430.E4
4-
02-
-4
4.
92-
02-
-4
92-
I—E
Tier
I
and Tier II Feed Rate and Emissions Screening Limits for
Carcinogenic Metals for Facilities
in Complex Terrain
Values
for use in urban and rural areas
TESH
(m)
Arsenic
(g/hr)
Cadmium (g/hr)
Chromium
Beryllium
(g/hr)
(g/hr)
4
0.i-rlEOi
0.2-,-6E—0i
0.04r0E~02
0.2~-0E-01
6
0.1,-6E-0i
0.3,-9E—01
005-r8E~02
0.2-~-9E—0l
8
0.2r4E0l
0.5r8E0i
0.08r6E
02
0.4r3E01
10
0.3-r5E
01
O.8-1-2E-0l
0.1~3E
01
0.6-~-2E 01
12
0.4,r-3E01
1.OE+OO
0.15E01
0.7-r6E01
14
0.50E—0i
i.3E+00
0.1-,-9E—0i
0.9-~-4E—01
16
0.6rOE
01
l.4E+00
0.2,-2E-0i
1.1E+00
18
0.6-r8E0i
1.6E1-00
0.2--4E
01
1.2E+00
20
0.7r6E—01
1.8E+00
0.2-~-7E—0l
1.3E+00
22
0.8r2E01
i.9E+00
0.3-,-OE—01
1.5E+00
24
0.9rOE
01
2.1E+00
0.3r3E
01
l.6E+00
26
1.OE+00
2.4E+00
0.3,-6E
01
1.8E+00
28
l.1E+00
2.7E+00
0.4r0E01
2.OE+00
30
l.2E+00
3.OE+00
0.4-~-4E0i
2.2E+00
35
l.5E+00
3.7E+00
0.5-r4E
01
2.7E+00
40
1.9E+00
4.6E+O0
0.6r8E 01
3.4EfOO
219
45
2.4E+00
5.4E+00
0.&r4E 01
4.2E+00
50
2.9E-l-00
6.8E+OG
l.OE+00
5.OE-t-00
55
3.5E+00
8.4E+00
1.3E1-00
6.4E+00
60
4.3E+00
lrO.E+01
1.5E+00
7.8E+00
65
5.4E+00
lr3.E~01
1.9E+00
9.6EiOO
70
6.OE+00
1~4.E+01
2.2E+00
l-r1.E101
75
6.8E+00
1-,-6,E+01
2.4E+0O
l-r2.E+Ol
80
7.6E+00
1-~-8.E+01
2.7E+00
1-r3.E+Ol
85
8.2E+00
2r0.E+01
3.OE+00
l-r5.E+01
90
9.4Et00
2r3.gF01
3.4E+00
1-r7.E+01
95
1’r0.E+01
2r5.E+01
4.OE+00
1r9.E+Ol
100
1r2.E+01
2-r-8.E+O1
4.3E+00
2-~-1.E+0.
105
1-r3.E+01
3-r2.E~0l
4.8EfOO
2,-4.E101
110
1r5.E±01
3r5.E+01
5.4E+00
2r7.E101
115
1-r7,E+01
40.E+Ol
6.OE+00
3-~-0.E+01
120
1r94,E+01
4,-4.E+Oi
6.4E+00
3-,-3.E+01
(Source:
Amended at
19
Ill.
Reg.
________,
effective
__________________
Section 726.Appendix B
Tier
I Feed Rate Screening Limits for Total Chlorine
Tier
I Feed Rate Screening Limits for Total Chlorine
TESH
(m)
Noncomplex
Noncomplex
Complex Terrain
Terrain
Terrain
(g/hr)
Urban (g/hr)
Rural
(g/hr)
4
8r2.E+0l
4~2.E+01
19.E+01
6
9-~-1.E1~01
4-r8.E+0i
2r8.E+01
8
l-rOO.E102
5-r3.E+0i
4-r1.Ef01
10
l-r20.E+02
6w2.E+01
5,r8.E+01
12
1r3E+02
77.E+01
7r2.E+01
14
1r50.E+02
9,-l.E+01
9,-1.E+01
16
1v70.E+02
1r20.E 102
1-rlO.Et02
18
1r90.E+02
1r40.E+02
lr20.E+02
20
2-rl0.E+02
1~-80.E+02
l-r-30.E+02
22
2r40.E+02
2r30.E+02
1-r40,E+0~
24
2-r70.E102
2-r90.E+02
i-,-60.E+02
26
3r10.E+02
3r70.E+02
1r70.E+02
28
3r50.E+02
4r70.E+02
1r90.E+02
30
3r90.E+02
5-~-8C,E+02
2,-10.E+02
35
5-r30.E+02
9r60.E+02
2r60.E+02
40
6-,r20.E+02
1r400,E+03
3r30.E+02
45
8r20.E+02
2r000.E+03
4r00.E+02
50
l-rlOO.E+03
2-r600.gF03
4r80.E+02
55
l-r300.E403
3-~-50O.E+O3
&r20.E+02
60
l-r600.E+03
4~60O.E+O3
7r70.E+02
65
2000.E+03
6-~-200.E+03
9,-10.E+02
70
2r300.EF03
7-~-200.E+03
1-rlOO.E103
75
2-r500.E103
8-r600.E+03
1r200.E±03
80
2-r900.E~03
1-,r0000.E+04
1-r-300.E+03
85
3-r300.E+03
1-~-2000.E+04
1r400,E+03
90
3r700.E+03
l-r4000.E+04
1,-600.E+03
95
4200.E+03
1-r7000.Et04
1-r800.E+03
100
4r800.E+03
2-~-l000.E+04
2~-000.E+03
105
5r300.E+03
2-~-4000.E+04
2,-300.E+03
110
6r200.~+03
2r9000.E+04
2r500.E±03
115
7v200.E1~03
3r5000.E+04
2r800.E+03
120
8r200.E+03
4.rl000.Ef04
3r200.E+03
(Source:
Amended at
19
Ill.
Reg.
________,
effective
________________
220
Section 726.Appendix C
Tier
II Emission Rate Screening Limits for Free
Chlorine and Hydrogen Chloride
Noncomplex Terrain
Noncomplex Terrain
Complex Terrain
Urban areas
Rural areas
Urban and
rural areas
TESH
(m)
Chlorine
HC.
Chlorine
HC1
Chlorine
HC1
Gas
(g/hr)
Gas
(g/hr)
gas
(g/hr)
(g/hr)
(g/hr)
(g/hr)
4
8-~-2.E+0l
l-r400.&44
4-~-2.E+01
7r30.E+02
1r9.E+01
3r30.E+02
2-
6
9iri.E+01
1-r600.E+9
4-r8.E+Ol
8-~-30.E+02
2r8.EfOl
4r90.E+02
-a
8
lrOO.E+02
1-~-800.~+0
5-r3.E+Ol
9-r20.E+02
4~1.E+01
7-rlO.E+02
3
10
1r20.Et02
2-r000.E+9
6r2.E±O1
lrlOO.E+G
5r8.E+01
1r000.E+0-
2-
3
•2-
12
lr3O.E+02
2-~~-300.E+9
7r7.E+01
l-~-300.~+0
7r2.E+01
1-1-300.E+0
2-
2-
2-
14
150.E+02
2-r600.E+9
9rl.E+01
l-r600.~+0-
9r1.E+01
1-r600.B+9-
-a
a
2-
16
1r70.E+02
2,-900.~+0
1-~-20.E+02
2-,-000.E+9
1-rlO.E+02
1-,-800.E+0-
2-
2-
3
18
lr90.Et02
3-~-300.~+9-
l-~-40.E+02
2-r500.~+0-
1-r20.Et02
2r000.~+9-
-2-
.3
2-
20
2w40.E+02
3-,-700.E+Q
1.-80.E+02
3-r100.E+0
130.E+02
2w300.~+9
3
2-
-3-
22
2r40.E+02
4r200.~+9
2r30.E+02
3-~-900.~+0
lr4O.E+02
2r400.B+G
.3-
2-
3
24
2r70.E+02
4-,-800.~+0
2-~-90.E+02
5-~-000,E+0
l-v-60.E+02
2-r800.B+0
-3-
2-
3
26
3riO.E+02
5-r4O0,~+G
3r70.E+02
6-r500.~+G
1r70.E+02
3r000.B+G
-a
-a
28
3,50.E+02
6OOO.~+0
4r70.E+02
8-v-100.E+0
lr90.E+02
3-.-400.&+0
3
3-
2-
30
3-~-90.E+02
6-r900.E+9
5-r80.Ef02
1-r0000.~+
2-r10.E+02
3r700.Wf9
‘a
94
3
35
5-r30.E+02
9-,r200.E+0
9r60.E+02
L~7000.E+
2r60.E+02
4’~r600.E+0
.3.
04
3
40
6~-20.ET02
1-ri000.E+
l~-400.~+G
2-r5000.E+
3-r30.E102
5’r700.+9
04
3
04
45
8r20.E+02
1-,r4000.E+
2000.F,+Q
3~r5000.E+
4’rOO.E+02
7ir000.B+0
04
~a
04
3
50
1r100.~+0
1,-8000.~+
2-r600.B+G
4~-6000.E+
4-r80.E+02
8-r400.B+0
3
94
3
04
.3
55
lr300.~+9
2-~3000.E+
3-~~-500.E+4
6-~-1000.E+
6-~-20.E+02
l1000.~+
2-
04
3
04
94
60
1-r600.B+G
2-~-9000.E+
4-~-600.?-+0-
8-~--1000.B+
7-r70.E+02
1r3000.~+
3
94
2-
04
04
65
2000.E+0
3-r4000.E+
6r200.E+Q
1-T-10000.~
910.E+02
1r6000.E+
2-
04
2-
+05
04
70
2-r300.E+G
3-r9000.B+
7,-200.E+9
1’r30000.~
1-rlOO.B-+9
1~-8000.B+
2-
94
2-
+05
3
94
75
2500.E+9-
4-r5000.E+
8-,-600.E+0
1-~-5O0OO.~
1-r200.E+0
2-~,-0000.E+
‘3.
04
-3-
+05
3
04
80
2’r900.E’+0-
5-r0000.B+
l-r0000.~+
1-x-80000.?-
lr300.E44
2-i-3000.B+
-3-
04
04
+0-5
2-
94
85
3-r300.E+0
58000.E+
lr2000.E+
2-r20OQO.~
1-,-400.E+9
2-,-5000..E+
2-
04
04
.4-05
3
04
90
3-r700.E+G
6,-6000.E4
1r4000.E+
2-r50000.?-
lrGOO.544
2r9000.E+
-3
04
04
-4-04
3
94
221
(Source:
Amended at
19
Ill. Reg.
effective
Section 726.Appendix E
Risk Specific Doses
BOARD
NOTE:
These are risk specific doses
(RSD5) based on
a risk of
1E 05th
10,000
(1X105).
Unit risk
(et*
RSD
(‘aj~g/ew-m3)
m~/t~g)
Acrylamide
Acrylonitrile
Aidrin
Aniline
Arsenic
Benz (a)anthracene
Benzene
Benz idine
Benzo (a)pyrene
Beryllium
BiB (2—chloro-
ethyl) ether
Bis (chloromethyl)
-
ether
Bis (2—ethylhexyl)
—
phthalate
1,3—But
adiene
Cadmium
Carbon
Tetra-
chloride
Chlordane
Chloroform
chloromethane
Chromium
VI
DDT
Dibenz(a,h)anthra—
cene
1, 2-Dibromo—3—
chloropropane
.1, 2—Dibromoethane
1, 1—Dichloroethane
1, 2-Dichioroethane
1, 1-Dichioro—
ethylene
1, 3—Dichloro-
propene
D ieldr in
DiethylstilbestrOl
D imethyl riitros-
79—06—1
107—13—1
309—00—2
62—53—3
7440—38—2
5 6—55—3
71—43—2
92—87—5
50—32—8
7440—41—7
111—44—4
542—88—1
117—81—7
106—99—0
7440—43—9
56—23—5
57—74—9
67—66—3
74—87—3
7440—47—3
50—29—3
53—70—3
96—12—8
106—93—4
75—34—3
107—06—2
75—35—4
542 —7 5—6
60—57—1
56—53—i
62—75—9
0.001-r3E 03
0.00006-r8E~0S
0.0049E03
0.000007r4E
06
0.004r3E
03
0. 0008’r9E04
0.O00008~-3EO6
0.06r7E02
0.003r3E
03
0.002r4E03
0.000
3-r3E04
0.06-r2E
02
0.0000002r4E07
0.0002r8E
04
0. 001-r8E03
0.00001r5~O5
0.0003-nE 04
0.00002r3E05
0.000003r6EO6
0.01-r2E 02
0,000097E05
0.01r4E02
0.006-r3E 03
0. 0002-r2E04
0. 00002-~-6E05
0.00002-v6E 05
0.00005r0E
05
0.35E01
0.004’n6E
03
0.1r4E01
0.0lr4E~02
0.007-r7E03
0.l5E0
1
0.0020E—03
1. 4E-I-00
0.002r3E
03
0. 01nlE02
1,.2E-4-00
0. 000lr5E04
O.003r0E
03
0.004-~-2E—03
0.03-~-0E02
0.0001-r6E 04
4-ir2.E+01
0.03’nGE
02
0. 005r6E’03
6-,-7E—01
0. 027E02
0.4r3E01
2.8E+00
0.000&n3E 04
0.1r0E 01
0. 0007rlE04
0.OOl-r6E
03
0. 04-~-5E—02
0.3’r8E01
0.3r8E0l
0.2-rOE 01
0.00002,-9E05
0.002-r2E
03
0. 00007-~-lE05
0.00071E—04
95
4r200.~+0
7-r4000.&+-
1-,--7000.E+
3-r00000.~
1-~800.~+G
3r2000.~+
.3
94
04
+0-4
2-
04
100
4-r800.E+0-
8,4000.B+
2-,-1000.E+
3-,-60000.~
2-~000.~+9 3r5000.~+
.3-
04
04
+04
-3.
04
105
5-r-3+9-
9-r2000.~+
2-r400O.~+
4-n30000.~
2-r300.B+0
3r9000.~+
3
04
04
+0-5
3
0-4
110
6-,--200.E+0
1r10000.4
2-1-9000.E+
5-ri0000.E
2-~-50O.&+4
4r5000.~+
.3
+45
04
+44
.3
04
115
7r200.~+9-
1-r30000.4
3s-5000.~+
6-rl0000.B
2--800.B+0-
5-r0000.~+
.3
+0-4
04
+04
-3-
04
120
8r2+0
140000.4
41000.E+
7r20000.~
3-r200.E+0
5r6000.E+
3
+0-5
94
+45
3
04
Constituent
CAS
No.
222
amine
2,4—Dinitrotoluene
121—14—2
0.00008,-8E—05
O.1-1-1E
01
l,2—Diphenyl—
122—66—7
0.0002r2E~04
0.04r5E02
hydrazine
1,4—Dioxane
123—91—1
0.000001-r4E-06
7.1E+00
Epichiorohydrin
106—89—8
0.00000i-T-2E-06
8.3E+0O
Ethylene Oxide
75—21-8
0.O001-r0E~~O~1
Q~1-i-0E0l
Ethylene Dibromide
106-93-4
0.0002-r2E-04
O.04-r5EO2
Formaldehyde
50—00-0
O.00001-s-3E-05
0.7~-7E01
Heptachlor
76—44—8
0.O01-~-3E03
0.007-r7E 03
Heptachlor Epoxide
1024—57—3
0.002-T-6E—03
O.003’r8EO3
Hexachlorobenzene
118—74-1
0.0004-r9E—04
002~-OE02
Hexachlorobuta—
87—68—3
0.00002,0E
05
0.5r0E0l
diene
Alpha—hexachloro—
319—84—6
0.OOl-r8E-03
0.005-,-6E03
cyclohexane
Beta—hexachloro-
319—85-7
0.0005-n3E 04
0.01r9E 02
cyclohexane
Gaxnma—hexachloro—
58—89-9
0.0003-r8E—04
0.O2r6EO2
cyclohexane
Hexachlorocyclo-
0.0005-nE
04
0O2-~-0E
02
hexane, Technical
Hexachlorodibenzo-
1.34+0
0. 000007-.-7E—06
p—dioxin(1,2
Mixture)
Hexachloroethane
67—72—1
0.000004’-nOE-06
2.5E+OO
Hydrazine
302—01—2
0.002-r9E—03
0.O03r4E03
Hydrazine Sulfate
302—01—2
0.002-1-9E—03
0.O03’r4E03
3—Methylchol—
56495
0.002-n7E
03
O.003-n7E
03
anthrene
Methyl Hydrazine
60—34—4
0.0003-1-1E-04
0.03’r2EO2
Methylene Chloride
75—09—2
0.000004-,-1E—06
2.4E+OO
4,4’—Methylene—
101—14—4
0.0O0O4-~-7E
05
0.2~-lE01
bis—2—chloro—
aniline
Nickel
7440—02—0
0.0002-r4E—04
0.04-r2E02
Nickel Refinery
7440—02—0
0.0002-r4E—04
0.O4ir2C 02
Dust
Nickel Subsulfide
12035—72—2
0.0004-1-8E-04
0.02-r1E02
2—Nitropropane
79—46—9
Q,~2-r7E—02
0.0003r7E04
N—Nitroso—n—butyl—
924—16—3
0.OOl-r6E-03
0. 006,-3E03
amine
N—Nitroso—n—
684—93—5
0.086E-02
0.0001-r2E04
methylurea
N—Nitrosodiethyl—
55185
0.04-n3E 02
O.O002-~-3E04
amine
N—Nitroso—
930—55—2
0.0006-,-1E—04
0.O1,-6E02
pyrrolidine
Pentachloronitro—
82—68-8
0.00007--3E
05
benzene
PCB5
1336—36—3
0.00lr2E03
0.O08~3E03
Pronamide
23950—58—5
0.000004-T-6E—06
2.2E+OO
Reserpine
50—55—5
0.003-rOE
03
0.003-s--3E
03
2,3,7,8—Tetra—
1746—01—6
4-r5.E-4-O1
0.0000002n2E07
chlorodibenzo—p—
dioxin
l,l,2,2—Tetra-
79—34—5
O.00005--8E 05
0.17E
01
chioroetharie
Tetrachioro-
127—18-4
O.0000004-,-8E-07
2-~.14,E-l-Oi
ethylene
Thiourea
62—56—6
0.0005-n5E
04
0.01r8E 02
1,l,2
79—00—5
O.00001’r6E 05
Q4,6r3E 01
223
Trichloroethane
Trichioroethylene
79—01-6
O.O00OOl-~-3E06
7.7E+00
2,4,6—Trichloro—
88—06—2
O.000005-r7E—06
1.8E+00
phenol
Toxaphene
8001—35—2
0.0003-r2E 04
0.03-nE
02
Vinyl Chloride
75—01—4
O.000007’-rlE-OG
1.4E+OO
(Source:
Amended at 19
Ill. Reg.’
,
effective
_____________________
Section 726.Appendix M
Mercury-Bearing Wastes That MaY Be Processed
in Exempt
Mercury Recovery Units
The following materials are exempt mercury—bearing materials containing less
than 500 ppm of 35
Ill.
Adm. Code 721.Appendix H organic constituents, when
generated by manufacturers or users of mercury or mercury products:
Activated
carbon
Decomposer graphite
Wood
Paper
Protective
clothing
Sweepings
Respiratory cartridge filters
Cleanup articles
Plastic bags and other contaminated containers
Laboratory and process control samples
K106 and other wastewater treatment plant
sludge and filter cake
Mercury cell Bump and tank sludge
Mercury cell process solids
Recoverable levels of mercury contained
in soil
(Source:
Added at
19
Ill.
Reg.
,
effective
______________________
TITLE
35:
ENVIRONMENTAL PROTECTION
SUBTITLE G:
WASTE DISPOSAL
CHAPTER
I:
POLLUTION CONTROL BOARD
SUBCHAPTER
c:
HAZARDOUS
WASTE
OPERATING
REQUIREMENTS
PART
728
LAND
DISPOSAL
RESTRICTIONS
SUBPART
A:
GENERAL
Section
728.101
Purpose,
Scope
and
Applicability
728.
102
Definitions
728.103
Dilution Prohibited as
a Substitute for Treatment
728.104
Treatment
Surface
Impoundment
Exemption
728.105
Procedures for case—by—case Extensions to an Effective Date
728.106
Petitions
to
Allow
Land
Disposal
of
a
Waste
Prohibited
under
Subpart
C
728.107
Waste
Analysis
and
Recordkeeping
728. 108
Landfill
and Surface
Impoundment
Disposal
Restrictions
(Repealed)
728.109
Special
Rules
for Characteristic Wastes
SUBPART
B: SCHEDULE FOR LAND DISPOSAL PROHIBITION
AND
ESTABLISHMENT OF TREATMENT STANDARDS
Section
728.110
First Third
728.111
Second Third
728.112
Third Third
728.113
Newly Listed Wastes
224
728. 114
Surface
Impoundment
exemptions
SUBPART
C:
PROHIBITION
ON
LAND
DISPOSAL
Section
728.130
728. 131
728.132
728. 133
728.134
728. 135
728.136
728.137
728.138
728.139
Section
728. 140
728. 141
728.142
728. 143
728.144
728. 145
728. 146
728. 148
Section
728. 150
728.Appendix
A
728.Appendix
B
728.Appendix
C
728.Appendix
D
728.Appendix
E
728.Appendix
F
728.Appendix
G
728.Appendix
H
728.Appendix
I
728.Appendix
J
Waste
Waste
Waste
Waste
Waste
Waste
Waste
Waste
Specific
Specific
Specific
Specific
Specific
Specific
Specific
Specific
Prohibitions
on Storage of Restricted Wastes
Toxicity
Characteristic
Leaching
Procedure
(TCLP)
Treatment
Standards
(As
concentrations
in the Treatment
Residual
Extract)
List
of
Halogenated
Organic
Compounds
Organomctallic
Lab
Pack~Wastes
Excluded from Lab Packs
Organic
Lab
Packs
(Repealed~
Technologies
to
Achieve
Deactivation
of
Characteristics
Federal Effective Dates
National Capacity LDR Variances for UIC Wastes
EP
Toxicity
Test
Method and Structural Integrity Test
Recordkeepthg, Notification,
and Certification Reguirements
728.Table
A
728.Table
B
728.Table C
728.Table
D
728.Table
B
728.Table
F
728.Table
0
728.Table
H
728.Table
T
728.Table
U
Constituent Concentrations
in Waste Extract
(CCWE)
Constituent Concentrations
in Wastes
(CCW)
Technology Codes and Description of Technology—Based
Standards
Technology—Based Standards by
RCRA
Waste Code
Standards for Radioactive
Mixed
Waste
Alternative
Treatment
Standards
for
Hazardous
Debris
Alternative
Treatment
Standards
Based
on
HMTR
Wastes Excluded from CCW Treatment Standards
Treatment
Standards for Hazardous Wastes
Universal Treatment Standards
(UTS~
AUTHORITY:
Implementing
Section
22.4 and authorized by Section 27 of the
Environmental
Protection
Act
(415 ILCS
5/22.4
and
27.
SOURCE:
Adopted
in
R87-5 at
11
Ill.
Reg.
19354,
effective
November
12,
1987;
amended in R87—39 at
12
Ill.
Reg.
13046, effective July 29,
1988;
amended
in
Prohibitions
——
Solvent
Wastes
Prohibitions
——
Dioxin-Containing Wastes
Prohibitions
——
California List Wastes
Prohibitions:
—First
Third
Wastes
Prohibitions
——
Second
Third
Wastes
Prohibitions
—-
Third
Third
Wastes
Prohibitions
—-
Newly
Listed
Wastes
Prohibitions
—-
Ignitable
and
Corrosive
Wastes Whose Treatment Standards Were Vacated
Characteristic
Waste—Specific Prohibitions:
Newly—Identified Organic Toxicity
Characteristic Wastes and Newly-Listed Coke By—Product and
Chlorotoluene Production Wastes
Statutory
Prohibitions
SUBPART D:
TREATMENT STANDARDS
Applicability of Treatment Standards
Treatment Standards Expressed as Concentrations
in Waste Extract
Treatment Standards Expressed as Specified Technologies
Treatment Standards e~xpressedas Waste Concentrations
Adjustment of Treatment Standard
Treatment Standards
for Hazardous Debris
Alternative Treatment Standards Based on HTMR
Universal Treatment
Standards
SUBPART E:
PROHIBITIONS ON STORAGE
225
R89—1
at
13
Ill.
Reg.
18403,
effective
November
13,
1989;
amended
in
R89—9
at
14
Ill.
Reg.
6232,
effective
April
16,
1990; amended
in R90—2 at
14
Ill.
Reg.
14470,
effective
August
22,
1990;
amended
in
R90-1O
at
14
Ill.
Reg.
16508,
effective
September
25,
1990;
amended
in
R90—11
at
15
Ill.
Reg.
9462,
effective
June
17,
1991;
amended
in
R92—1O
at
17
Ill.
Reg.
5727,
effective
March
26,
1993;
amended
in
R93—4
at
17
Ill.
Reg.
20692,
effective
November
22,
1993;
amended
in
R93—l6
at
18
Ill.
Reg.
6799,
effective
April
26,
1994;
amended
in
R94—7
at
18
Ill.
Reg.
12203,
effective July 29,
1994;
amended
in
R94—17
at
18
Ill.
Reg.
17563,
effective
November
23,
1994;
amended
in
R95—6 at
19
Ill.
Reg.
________,
effective
____________________
SUBPART
A:
GENERAL
Section
728.101
Purpose,
Scope
and
Applicability
a)
This
Part
identifies
hazardous
wastes
that
are
restricted
from
land disposal and defines those limited circumstances under which
an
otherwise
prohibited
waste
may
continue
to
be
land
disposed.
b)
Except
as
specifically
provided
otherwise in this Part or 35
Ill.
Adm.
Code
721,
the
requirements
of
this
Part apply to persons
w~ethat generate
or
transport hazardous waste and to owners and
operators
of
hazardous
waste
treatment,
storage4,
and disposal
facilities.
c)
Restricted wastes may continue to be land disposed as follows:
1)
Where
persons
have
been
granted
an extension to the
effective
date
of
a
prohibition
under
Subpart
C
or
pursuant
to
Section
728.105,
with
respect
to
those
wastes
covered by
the
extension;
2)
Where
persons
have
been
granted
an
exemption
from a
prohibition
pursuant
to
a
petition
under
Section
728.106,
with
respect
to
those
wastes
and
units
covered
by
the
petition;
3)
Wastes
that
are
hazardous
only
because
they
exhibit
a
hazardous
characteristic-,-
and
whiohthat are otherwise
prohibited
from
land
disposal
under
this
Part-,
are
not
prohibited
from
land
disposal
if the wastes:
A)
Are
disposed
into
a
nonhazardous
or
hazardous
waste
injection
well4,
as
defined
in
35
Ill.
Adm.
Code
704.106(a);
and
B)
Do
not
exhibit
any prohibited characteristic of
hazardous
waste
at
the point of injection-n;
and
çj
If,
at
the
point
of
generation, the inlected wastes
include
DOOl
High
TOC
subcategory
wastes
or
D012—D017
pesticide wastes that are prohibited
under
Section
728.117(c), those wastes have been treated to meet the
treatment
standards of Section 728.140 prior to
injection.
d)
This Part does not affect the availability of
a waiver under
Section 121(d) (4)
of the Comprehensive Environmental Response,
Compensation,
and Liability Act of 1980
(CERCLA)
(42 U.S.C.
,S19601
et
seq~).
226
e)
The
following
hazardous
wastes
are not subject to any provision of
this
Part:
1)
Wastes generated by small quantity generators of less than
100
kg
of
non—acute
hazardous
waste
or
less
than
1
kg
of
acute hazardous waste per month,
as defined in
35
Ill.
Adm.
Code
721.105;
2)
Waste pesticides that
a farmer disposes of pursuant to 35
Ill. Adm.
Code
722.170;
3)
Wastes
identified
or
listed
as
hazardous
after
November
8,
1984,
for
which
U4,S~EPA has
not
promulgated
land
disposal
prohibitions
or
treatment standards.
4)
De
minimis
losses
to wastewater treatment systems of
commercial
chemical
product
or
chemical
intermediates
that
are
ignitable
(DOOl)-,- or corrosive
(D002)-, or that are
organic constituents that exhibit the characteristic of
toxicity
(D0l2-D043’)
and that contain underlying hazardous
constituents4, as defined in Section 728.102 of this Part,
are not considered to be prohibited wastes.
~De minimis~is
defined as losses
from normal material handling operations
(e.g.4, spills from the unloading or transfer of materials
from bins or other containers-,~leaks from pipes, valves4,
or other devices used to transfer materials);
minor leaks of
process equipment, storage tanks4, or containers;
leaks from
well—maintained pump packings and seals;
sample purging; a~4
relief device discharges;
discharges from safety showers and
rinsing and cleaning of personal safety equipment;
and
rinsate from empty containers or from containers that are
rendered empty by that rinsing.
5)
Land disposal prohibitions for hazardous characteristic
wastes do not apply to laboratory wastes displaying the
characteristic of ignitab4eilitv
(D001’j,
and corrosivej~
(D002), or organic toxicity
(D012 through D043
laboratory
wastec containing underlying ha~ardouaconstituanto from
laboratory opcrationc, that are mixed with other plant
wastewaters at facilities whose ultimate discharge is
subject to regulatione under the CWA (including wastewaters
at facilities whichthat have eliminated the discharge of
wastewater), provided that the annualized flow of laboratory
wastewater into the facility’s headwork does not exceed one
percent-,- or provided that the laboratory wastes’ combined
annualized average concentration does not exceed one part
per million in the facility’s headwork~.
f)
This Part
is cumulative with the land disposal restrictions
of 35
Ill.
Adni.
Code
729.
The
Environmental
Protection Agency
(Agency)
shall
not
issue
a
wastestream
authorization
pursuant
to
35
Ill.
Adxn.
Code
709
or Sections
22.6
or
39(h)
of
the
Environmental
Protection Act
(Ill.
flay.
Stat.
1987,
oh. 11l~,pars.
1022.6 or
1039(h))1415 ILCS 5/22.6 or 39.61
unless the waste meets the
requirements of this Part
as
well as
35
Ill. Adm.
Code 729.
(Source:
Amended at
19
Ill. Reg.
________,
effective
_____________________
Section 728.102
Definitions
When used in this Part4, the following terms have the meanings given below.
All other terms have the meanings given under 35
Ill. Adm. Code 702.110,
227
720.1024,
or
721.103.
“Agency” means the Illinois Environmental Protection Agency.
“Board” means the Illinois Pollution Control Board.
“CERCLA” means the
Comprehensive
Environmental
Response,
Compensation,
and
Liability Act
of 1980
(42 U.S.C.
9601
et
seq.)
“Debris” means solid material exceeding a 60 mm particle size that
is intended for disposal and that is:
A~,manufactured object; e~
plant or animal matter; or natural geologic material.
However,
the following materials are not debris:
A~nymaterial
for which a
specific treatment
standard is provided in 728.Subpart D,
namely
lead acid batteries,
cadmium batteries,
and radioactive lead
solids ~rocess
residuals4, such as smelter slag and residues from
the treatment of waste, wastewater,
sludges,
or air emission
residues; and intact containers of hazardous waste that are not
ruptured and that retain at least
75
of their original volume.
A
mixture of debris that has not been treated to the standards
provided by Section 728.145
of this Part and other material
is
subject to regulation as debris
if the mixture
is comprised
primarily of debris,
by volume, based on visual inspection.
“Halogenated organic
compounds”
or
“HOCs”
means
those
compounds
having a carbon—halogen bond whichthat are listed under Section
728.Appendix C.
“Hazardous constituent or constituents” means those constituents
listed in 35
Ill. Mm.
Code 721.Appendix H.
“Hazardous debris” means debris that contains
a hazardous waste
listed in 35
Ill. Adm.
Code 721.Subpart
D-,- or that exhibits a
characteristic of hazardous waste identified in
35 Ill. Adm. Code
721.Subpart
C.
Inorganic Solid Debris
are nonfriable
inorganic solids that are
incapable of passing through
a 9.5 mm standard
sieve-p and that
require cutting-, or crushing and grinding-,- in mechanical sizing
equipment prior to stabilization,
limited to the following
inorganic or metal materials:
Metal slags
(either dross or scoria).
Glassified slag.
Glass.
Concrete
(excluding cementitious or pozzolanic stabilized
hazardous wastes).
Masonry and refractory bricks.
Metal cane,
containers,
drums4, or tanks.
Metal nuts, bolts,
pipes, pumps,
valves,
appliances4, or
industrial equipment.
Scrap metal4, as defined
in
35 Ill.
Adm. Code 721.1O1(c)(6),
“Land disposal” means placement
in or on the land,
except in a
corrective action management
unit,
and includes,
but
is not
228
limited to,
placement
in a landfill,
surface impoundment, waste
pile,
injection well,
land treatment facility,
salt dome
formation,
salt bed formation, underground mine4, or
cave-,- or
placement
in
a
concrete
vault
or
bunker
intended
for
disposal
purposes.
“Nonwastewaters” are wastes that do not meet the criteria for
“wastewaters”
in
this
Section.
“Polychlorinated
biphenyls”
or
“PCBs”
are
halogenated
organic
compounds defined
in accordance with 40 CFR 761.3,
incorporated by
reference
in
35
Ill.
Adm.
Code
720.111.
“ppm”
means
parts
per
million.
“RCRA
corrective
action”
means
corrective
action
taken
under
35
Ill. Adm.
Code
724.200
or
725.193,
40
CFR
264.100
or
265.93
(1992-4),
or
similar
regulations
in
other
States
with
RCRA
programs
authorized
by
U.S.
EPA
pursuant
to
40
CFR
271
(1992-i).
“Underlying
hazardous
constituent”
means
any
regulated
constituent
listed
in Section 728.Table
U,
“Universal Treatment Standards
(UTS)”,
except vanadium and zinc,
that can reasonably be expected
to be present,
at the point of generation of the hazardous waste,
at lcvcloa concentration above the F039 constituent—specific ~
treatment standard
at the point of gcricration of
the ha~ardouo
~aatc.
“U.S.
EPA”
or
“USEPA”
means
the
United
States
Environmental
Protection
Agency.
“Wastewaters”
are
wastes
that
contain
less
than
1
by
weight
total
organic carbon
(TOC)
and less than
1
by
weight
total
suspended
solids
(TSS),
with
the following exceptions:
FOOl,
F002,
F003,
P004,
and P005 solvent-water mixtures that
contain less than 1
by
weight
TOC
or
less
than
1
by
weight
total FOOl,
FOO2, F003,
F004, and FOO5 solvent constituents
listed
in
Table
A.
KOll,
K013,
and
K014
wastewaters
(as
generated)
that
contain
less than 5
by weight TOC and less than
1
by
weight
TSS.
K103
and K104 wastewaters that contain less than 4
by
weight
TOC
and
less
than
1
by
weight
TSS.
(Source:
Amended
at
19
Ill.
Reg.
________,
effective
_____________________
Section
728.107
Waste Analysis and Recordkeeping
a)
Except
as specified in Section 728.132, where a generator’s waste
is
listed
in
35
Ill. Adm.
Code 721.Subpart D or
if the waste
exhibits
one
or
more
of
the
characteristics
set
out
at
35
Ill.
Adm. Code 721.Subpart
C,
the
generator
shall
test
its
waste,
or
test an extract using the Toxicity Characteristic Leaching
Procedure, Method
1311,
in
“Test Methods
for Evaluating Solid
Waste,
Physical/Chemical Methods”,
U.S. EPA Publication SW-846,
incorporated by reference in 35
Ill.
Adm. Code 720.111, or use
knowledge of the
waste-,- to determine
if the waste
is restricted
from land disposal under this Part.
Except ac opooified in
Section 728.132,
if a generator’s waste axhibito one or more of
the
oharactcrioticc
set
out
at
35 Ill. Mm.
Code 721.Cubpart C,
as
229
the
generator
shall
toot
an
extract
using
the
EP
Toxicity
Test,
~fethod1310,
in “met Ziethods
for Evaluating Solid Waste,
Physical/Chemical Methods”, U.S.
EPZi Publication SW—8~16, as
incorporated by reference in 35
Ill. Adm. Code 720.111,
or use
knowledge of the waste, to determine if the waste
is restricted
from land disposal under this Part.
If the generator determines
that its waste displays the characteristic of ignitability
(DOOl)
(and is not in the High TOC Ignitable Liquids Subcategory or
is
not treated by INCIN,
FSUBS,CMBST or RORGS of Section 728.Table C
of this Part), er—the waste displays the characteristic orf
corrosivity
(D002)-, and is prohibited under Section 728.137,
or
the waste displays the characteristic of organic toxicity
(D012-
D043)
and is prohibited under Section 728.138, the generator shall
determine
what
underlying
hazardous
constituents
(as
defined
in
Section 728.102 of thip Part),
are reasonably expected to be
present
in the DOOl4, er—DOO2,
or DO12 throuah DO43 waste.
1)
If
a generator determines that the gencratorj~is managing a
restricted waste under this Part and determines that the
waste does not meet the applicable treatment standards set
forth
in
728.Subpart
D
of
this
Part
or exceeds the
applicable prohibition levels set forth in Section 728.132
or 728.139,
with each shipment
of waste the generator shall
notify the treatment or storage facility in writing of the
appropriate treatment standard set forth in Subpart
D of
any applicable prohibition levels
set forth in
Section 728.132
or 728.139 with each shipment
of waste.
The
notice must include the following information:
A)
U.S.
EPA hazardous waste number;
B)
The
corresponding
treatment
otandardowaste
constituents that the treater will monitor,
if
monitoring will not include all regulated
constituents,
for
wastes
FOOl
through
FOO5,
F039,
DOO1,
0002,
DO12 through DO43,
and wastes prohibited
pursuant to Section 728.132 or Section 3004(d)
of the
Resource Conservation and Recovery Act, referenced in
Section 728.139.
Treatment standards for all other
restricted wastes must either be
included,
or be
referenced by including on the notification thc
applicable waotewatcr
(as defined in Section
728.102(f))
or nonwactewator
(as defined in Section
728.102(d))
category,
the
applicable
oubcatogory
made
within a waste code based on waste—specific criteria
(such
as D003 reactive cyanides), and the Sections and
subsections
whore
the
applicable
treatment
standard
appears.
Where
the
applicable
treatment
standards
are
expressed as specified technologies in Section
728.142,
the applicable five letter treatment code
found
in
Section
728.Table
C
(e.g.,
INCIN, WETOX)
also
must be listed on the notification.
The generator
must also include whether the waste is
a nonwastewater
or_wastewater
(as
defined
in
Section 728.102
(d) and
(f H
and
indicate
the
subcategory
of
the
waste
(such
as “DOO3
reactive cyanide”)
if applicab1e~
C)
The manifest number associated with the shipment of
waste;
and
D)
For hazardous debris, the contaminants subject to
treatment4, as provided by Section 728.145(b)4, and the
230
following statement:
“This hazardous debris is
subject to the alternative treatment standards of
35
Ill.
Adxn.
Code
728.145;
and
E)
Waste analysis data,
where available-i-;
and
fi
The
date
on
which
the
waste
is sublect to the
prohibitions.
2)
If
a generator determines that the gcncratorj~is managing a
restricted waste under this
Part-,- and determines that the
waste can be land disposed without further treatment,
with
each shipment of waste the generator shall submit,
to the
treatment,
storage4, or
land disposal facility,
a notice and
a certification to the treatment.
storage, or land disposal
facility stating that the waste meets the applicable
treatment standards set forth in 728.Subpart D of this Part
and setting forth the applicable prohibition levels set
forth in Section 728.132
or RCRA Section 3004(d), referenced
in Section 728.139.
~gGeneratore
of hazardous debris that
is excluded
from the definition of hazardous waste under 35
Ill.
Adm.
Code 72l.1O3(e~)j2j, 35
Ill.
Adm. Code
728.103(f)(2)4, a*44~35
Ill. Adm. Code 720.122
(i.e. debris
that is delisted),
however4, e*eJ~not subject to these
notification and certififcation requirements.
A)
The notice must
include the following information:
i)
U.S. EPA hazardous waste number;
ii)
The corresponding treatment standardowaste
constituents that the treater will monitor,
if
monitoring will not include all regulated
constituents,
for wastes FOOl through P005,
FO39,
1DOO1, D002,
D012 throuah 0043,
and
wastes
prohibited pursuant to Section 728.132 or
Section 3004(d) of the Resource Conservation and
Recovery Act, referenced in Section 728.139.
Treatment
standards
for
all
other
restricted
wastes
on tnc notlrLoatlon tne appiicaoieme
generator must also include whether the waste
is
a waatewater or nonwastewater
(as defined
in
Section 728.102(d)
and
(f))
category,
and
indicate the subcategory of the wasteapplicable
subdivisions made within
a waste code based on
waste-specific criteria
(such as DOO3, reactive
cyanides),
and the Section and subsection where
the applicable treatment standard appearsj~
applicable.
Where the applicable treatment
e~andardsare expressed as
specified
technologies
in Section 728.142, the applicable
five letter treatment code found in Section
728.Table C (e.g.,
INCIN,
WETOX)
also must be
~4sted on the notification.
iii)
The
manifest
number
associated
with
the
shipment
of waste;
and
iv)
Waste analysis data,
where available4,
B)
The
certification
must
be
signed
by
an
authorized
231
representative and must state the following:
I certify under penalty of law that
I personally have
examined and am familiar with the waste through
analysis and testing or through knowledge of the waste
to
support this certification that the waste complies
with
the
treatment
standards
specified
in
35
Ill.
Adm.
Code
728.Subpart
D
and
all
applicable
prohibitions
set
forth
in
35
Ill.
Adm.
Code
728.132,
728.1394,
or
Section
3004(d)
of
the
Resource
Conservation
and
Recovery
Act.
I
believe
that
the
information
I
submitted
is
true,
accurate4,
and
complete.
I
am
aware
that
there
are
significant
penalties
for
submitting
a
false certification,
including the possibility
of
a
fine
and
imprisonment.
3)
If
a generator’s waste is subject to an exemption
from a
prohibition on the type of
land disposal method utilized for
the waste (such as,
but not limited to,
a case—by—case
extension under Section 728.105,
an exemption under Section
728.106,
an
extension under Section 728.1O1(c)(3)4, or a
nationwide
capacity variance under 40 CFR 268.Subpart
C
(199~)j, with each shipment of waste,
the generator shall
submit
a notice with each shipment of the waste to the
facility receiving the generator’s waste-, stating that the
waste is not prohibited from land disposal.
The notice must
include the following information:
A)
U.S. EPA hazardous waste number-t-~
B)
The corresponding treatment standardewaste
constituents that the treater will monitor,
if
monitoring will not include all regulated
constituents,
for
wastes
FOOl through F005,
DOOl,
D002, and DO12 through_DC~---~
-
waotc..~
pLUILLiJ~.~.LU
pursuant
i.v
~uu~J.uz1
~
or
beoLiOfl
3004(d)
of
the
Resource
Conservation
and
Recovery
Act,
referenced
in
Section 728.139.
Treatment standards for all other
restricted
wastes
must
either
be
included
or
be
referenced
by
including
on
the
notification
the
,
and
the
Section
and
subsection
where
the
applicable
treatment standard appears.
Where
the
applicable
treatment
standards
are
expreoaed
as
specified
technologies
in
Section
728.142,
the
applicable
five—
letter treatment code found in Section 728.Tablc C
(e.g.,
INCIN,
WETOX)
also
must
be
listed
on
the
notification.
The generator must also include whether
the
waste
is
a
nonwastewater
or
wastewater
(as
defined
in
Section
728.102(d)
and
(f)),
and
indicate
the
subcategory of the waste
(such as “D003 reactive
cyanide”),
if applicable
C)
The
manifest
number
associated
with
the
shipment
of waste;
D)
Waste analysis data,
where available;
E)
For hazardous debris, ~when using the alternative
treatment technologies provided by Section 728.145:
jj
Ihe
contamine~nets
subject
to
treatment4,
as
provided
by
Section 728.145(b)1
232
JJJ
An indication that these contaminants are being
treated to comply with Section 728.145 and the
following
statement:
“This
hazardous
debris
is
subjoct
to
the
alternative
treatment
standards
of
35
Ill.
Adm.
Codc
728.l45~t;
and
fi
For
hazardous
debris
when
using
the
treatment
standards for the contaminating waste(s)
in Section
728.140:
the requirements described in subsections
(a’,(3)(A)
through
(a)(3)(D)
above
and
subsection
(a)(3)(G)
below; and,
F~)
The date
on
which the waste is subject to the
prohibitions.
4)
If
a generator
is managing
a prohibited waste in
tanks4, eE
containers, or containment buildings regulated under
35
Ill.
Adm.
Code
722.134-,-
and
is
treating
such waste in such tanks,
containers4, or containment buildings to meet applicable
treatment
standards
under
728.Subpart
D
of
this
Part,
the
generator shall develop and follow
a written waste analysis
plan that describes the procedures the generator will carry
out
to
comply
with
the treatment standards.
(A generator
treating hazardous debris under the alternative treatment
standards of Section 72a.Table
F,
however,
is not subject to
these
waste
analysis
requirements.)
The
plan
must
be
kept
on—site
in
the generator’s records,
and the following
requirements must be met:
A)
The waste analysis plan must
be based on a detailed
chemical and physical analysis of
a representative
sample of the prohibited wastes being treated,
and j~
must
contain
all
information
necessary
to
treat
the
wastes
in
accordance
with
the
requirements
of
this
Part,
including the selected testing frequency.
B)
Such plan must be filed with the Agency
a minimum of
30
days
prior
to
the
treatment
activity,
with
delivery
verified.
C)
Wastes shipped off—site pursuant to this subsection
must
comply
with
the
notification
requirements
of
Section 728.107(a)(2).
5)
If
a generator determines whether the waste is restricted
based solely on the generator’s knowledge of the waste,
the
generator shall retain all supporting data used to make this
determination
on—site
in
the
generator’s
files.
If
a
generator determines whether the waste is restricted based
on testing the waste or an extract developed using the test
method described
in Section 728.Appendix
A, the generator
shall retain
all waste analysis data on site
in t-he
gcncrator’aj~
files.
6)
If a generator determines,
subsequent to the time of
generation, that the generatorit is managing a restricted
waste that
is excluded from the definition of hazardous or
solid waste or exempt from regulation as a RCRA hazardous
waste under
35 Ill. Adm.
Code
721.102
through 721.106, the
generator shall place,
in the facility’s file,
a one—time
notice stating such generation, the subsequent exclusion
from the definition of hazardous or solid waste or exemption
233
from
regulation
as
a RCRA hazardous waste,
and the
disposition
of
the
waste.
7)
~gGeneratore
shall retain on—site
a copy of all notices,
certifications, demonstrations, waste analysis data4, and
other documentation produced pursuant to this Section for
at
least five years from the date that the waste that
is the
subject of such documentation was last sent to on—site or
off—site treatment4, storage4, or disposal.
The five year
record retention period
is automatically extended during the
course
of
any
unresolved
enforcement
action
regarding
the
regulated
activity4,
or
as
requested
by
the
Agency.
The
requirements
of
this
subsection apply to solid wastes even
when
the
hazardous
characteristic
is
removed
prior
to
disposal,
er—when the waste
is excluded from the definition
of hazardous or solid waste under
35 Ill.
Adm.
Code
721.102
through
721.106,
or
when
the
waste
is exempted from
regulation
as
a
RCRA
hazardous
waste
subsequent
to
the
point
of generation.
8)
If
a generator
is managing
a lab
pack
that
contains
wastes
identified
in
Section
728.Appendix
D
and
wishes
to
use
the
alternative treatment standard under Section 728.l42jgj,
with each shipment of waste the generator shall
submit
a
notice to the treatment facility
in accordance with
subsection
(a)(l)
above,
except that underlying hazardous
constituents need not be determined.
The generator shall
also comply with the requirements in subsections
(a)(5) and
(a) (6) above and shall submit the following certification,
which must be signed by an authorized representative:
I certify under penalty of
law that
I personally have
examined and am familiar with the waste and that the lab
pack does not containe onlyanv of the wastes
apocifiodidentified
in
35
Ill.
Adm.
Code
728.Appendix
D—e*
solid
wastes
not
subject
to
regulation
under
35
Ill.
Adiu.
Code
721.
1 am aware that there are significant penalties
for submitting a false certification,
including the
possibility of fine or imprisonment.
9)
If
a generator
is managing
a lab pack that containo organic
wastes
specified
in
Section
728.Appcndix
E
and
wishes
to
use
the alternate treatment st.andardc under SectIon 728.142,
with
each
shipment
of
waste
the
generator
shall
submit
a
notice to the treatment facility
In accordance with
subsection
(a)(l)
above.
The generator also shall comply
with
the
requirements
in
subsections
(a)(5)
and
(a)(6)
above
and
shall
submit
the
following
certification
that must be
signed
by
an
authorized
reprcccntative~This
subsection
corresponds with 40 CFR 268.7(a)(9), marked “reserved” by
U.S.
EPA
at
59
Fed.
Req.
48045
(Sept.
19,
1994).
This
statement maintains structural consistency with federal
regulations.
I certify under penalty of
law that
I
personally
have
eMamined
and
am
familiar
with
the
waste
through
analysis
and
testing
or
through
knowledge
o~ the
waste
and
that
the
lab
pack contains only organic waste
specified
in
35
Ill.
Mm.
Code
728.Appendix B or solid
wastes
not
sub~cct to
regulation
under
35
Ill.
Mm.
Code
721.
I am aware that there are
significant
penalties for submitting a false certificati-on,
234
poe
10)
Small
quantity
generators with tolling agreements pursuant
to 35
Ill. Adm.
Code
722.120(e)
shall comply with the
applicable notification and certification requirements of
subsection
(a)
above for the initial shipment of the waste
subject
to
the
agreement.
Such generators shall retain on—
site
a
copy
of
the
notification
and
certification,
together
with
the
tolling
agreement,
for
at
least
three years after
termination
or
expiration
of
the
agreement.
The
three—year
record retention period is automatically extended following
notification pursuant to Section 31(d)
of
the
Environmental
Protection
Act-7-
until
either
any subsequent
enforcement
action
is
resolved-,
or
until
the
Agency
notifies
the
generator
documents
need
nor,
be
retained.
b)
Treatment
facilities
shall
test
their
wastes
according
to
the
frequency
specified
in
their
waste analysis
plane4, as required by
35
Ill.
Adm.
Code
724.113
or
725.113.
Such testing must be
performed
as
provided
in
subsections
(b)(l),
(b)(2)4,
and
(b)(3)
below.
1)
For wastes with treatment standards expressed as
concentrations in the waste extract (Section 728.141), the
owner
or
operator
of
the
treatment
facility
shall
test
the
treatment
residues
or
an extract of such residues developed
using the test method described
in Section 728.Appendix A to
assure that the treatment residues or extract meet the
applicable treatment
standards.
2)
For
wastes
prohibited
under
Section
728.132
or
728.139
that
are not subject to any treatment standards under 728.Subpart
D
of
this
Part,
the
owner
or operator of the treatment
facility shall test the treatment residues according to the
generator
testing
requirements
specified
in
Section
728.132
to
assure
that
the treatment residues comply with the
applicable prohibitions.
3)
For wastes with treatment standards expressed as
concentrations in the waste
(Section 728.143), the owner or
operator of the treatment facility shall test the treatment
residues
(not
an
extract
of
such
residues) to assure that
the treatment residues meet the applicable treatment
standards.
4)
A notice must be sent with each waste shipment to the land
disposal facility that includes the following information,
except that debris excluded from the definition of the
hazardous waste under Ccction35
Ill. Adm.
Code
72~.1O3(~)-f-Q-)-(i.e., debris treated by
an
extraction
or
destruction technology provided by Section 728.Table
F,
and
debris that is delisted)
is subject to the notififcation and
certification
requirments
of
subsection
(d)
below rather
than
these
notification
requirments:
A)
U.S.
EPA
hazardous
waste
number;
B)
The corresponding treatment atandardowaste
constituents
to
be
monitored,
if
monitoring
will
not
include
all
regulated
constituents,
for
wastes
FOOl
through F005,
FO39, DOOl,
0002, D012 through D043,
and
wastes
prohibited pursuant to Section 728.132 or
235
Section
3004(d)
of the Resource Conservation and
Recovery
Act,
referenced
in
Section
728.139,
and
for
underlying hazardous constituents
(as defined in
Section 728.102 of this Part),
in DOOl and D002 wastes
if
those
wastes
arc
prohibited
under
Section
72-8.137
of
thip
Part.
Treatment
standards
for
all
other
restricted
wastes
must
either
be
included,
or
be
referenced
by
including
on
the
notification
the
applicableThe
generator
must also include whether the
waste is
a nonwastewater or wastewater
(as defined in
Section
728.102(d)
or
(f)), and indicate the
subcateqory
of
the
waste
or
nonwactowator
(as
defined
in
Section
728.102(d))
category,
the
applicable
subdivisions
made
within
a
waste
code
based
on
waste-
specific
criteria
(such
as
DOO3
reactive
cyanides),
and the Sections and subsections where the applicable
treatment
standard appcarsif applicable;.
Where the
applicable treatment standards arc expressed as
specified technologies
in Section 728.142,
the
applicable
five-letter
treatment
code
found
in
Section
728.Table
C
(e.g.,
INCIN, WETOX)
also must be listed
on the notification.
C)
The manifest number associated with the shipment of
waste;
and
D)
Waste analysis data,
where available.
5)
The treatment facility owner or operator shall submit
a
certification with each shipment of waste or treatment
residue
of
a
restricted
waste to the land disposal
facility
stating that the waste or treatment residue has been treated
in compliance with the treatment standards specified in
728.Subpart
D
of
this
Part
and
the
applicable
prohibitions
set
forth
in
Section
728.132
or
728.139.
Debris
excluded
from the definiton of hazardous waste under Scotion35
Ill.
Adm. Code 72&L.l03(-~Q)-(-~-)-(i.e.,
debris treated by an
extraction or destruction technology provided by Section
728.Table
F,
and debris that is delisted),
however,
is
subject
to
the
notififcation
and
certication requirements of
subsection
(d)
below
rather
than
the
certification
requirements
of
this
subsection
(b)(5).
A)
For wastes with treatment standards expressed as
concentrations
in
the
waste
extract
or
in
the
waste
(Sections 728.141 or
728.143),
or
for
wastes
prohibited under Section 728.132 or 728.139 that are
not
subject
to
any
treatment
standards
under
728.Subpart
B
of
this
Part,
the
certification
must
be
signed
by
an
authorized
representative
and
must
state
the following:
I
certify
under
penalty
of
law
that
I
have
personally examined and am familiar with the
treatment
technology
and
operation
of
the
treatment process
used
to
support
this
certification and that,
based on my inquiry of
those individuals immediately responsible
for
obtaining this information,
I believe
that
the
treatment process
has been operated and
maintained properly4, so as to comply with the
performance
levels
specified
in
35
Ill.
Adm.
236
Code 728.Subpart B and
all applicable
prohibitions set forth in 35
Ill.
Adm. Code
728.132
or
728.139
or
Section
3004(d)
of
the
Resource Conservation and Recovery Act without
impermissible dilution of the prohibited waste.
I am aware that there are significant penalties
for
submitting
a
false
certification,
including
the
possibility
of
fine
and
imprisonment.
B)
For wastes with treatment standards expressed as
technologies
(Section 728.142), the certification must
be
signed
by
an authorized representative and must
state
the
following:
I
certify
under
penalty
of
law
that
the
waste
has been treated in accordance with the
requirements of 35 Ill. Adm. Code 728.142.
I am
aware that there are significant penalties for
submitting
a false certification,
including the
possibility
of
fine
and
imprisonment.
C)
For wastes with treatment standards expressed
as
concentrations
in the waste pursuant to Section
728.143,
if compliance with the treatment standards
in
728.Subpart
B
of
this
Part
is based
in part or in
whole on the analytical detection limit alternative
specified
in
Section
728.143(c),
the
certification
also must state the following:
I
certify
under
penalty
of
law
that
I
have
personally examined and am familiar with the
treatment technology and operation of the
treatment process used to support this
certification and that, based
on
my
inquiry
of
those individuals immediately responsible
for
obtaining this
information,
I believe that the
nonwastewater organic constituents have been
treated
by incineration
in units operated in
accordance with 35
Ill. Mm.
Code 724.Subpart 0
or
35
Ill.
Mm.
Code
725.Subpart
0,
or
by
combustion
in fuel substitution units operating
in accordance with applicable technical
requirements,
and
I
have
been
unable
to
detect
the noriwastewater organic constituents despite
having used best good faith efforts to analyze
for
such constituents.
I am aware that there
are significant penalties for submitting a false
certification, including the possibility of fine
and imprisonment.
QI
For characteristic wastes DOO1,
D002,
and D012 through
D043 that are subiect to the treatment standards
in
Section
728.140
(other
than
those
expressed
as
a
required
method
of
treatment),
that
are
reasonably
expected
to
contain
underlying
hazardous
constituents
as
defined
in
Section
728.102(i),
that
are
treated
on-
site to remove the hazardous characteristic,
and that
are
then
sent
off—site
for
treatment
of
underlying
hazardous constituents,
the certification must state
the following:
I certify under penalty of
law that the waste
237
has been treated
in accordance with the
requirements of
35
Ill. Adm.
Code
728.140
to
remove the hazardous characteristic.
This
decharacterized waste contains underlying
hazardous
constituents
that
require
further
treatment to meet universal treatment standards.
I am aware that there are significant penalties
for submitting
a false certification,
including
the possibility of fine and imprisonment.
6)
If the waste or treatment residue will be further managed at
a
different
treatment
or
storage
facility,
the
treatment,
storage4, or disposal facility sending the waste or treatment
residue
off—site
must
comply with the notice and
certification
requirements
applicable
to
generators
under
this Section.
7)
Where the wastes are recyclable materials used in
a manner
constituting disposal subject to the provisions of 35
Ill.
Adm. Code 726.120(b), regarding treatment standards and
prohibition
levels,
the
owner
or
operator
of
a
treatment
facility (i.e. the recycler)
is not required to notify the
receiving facility pursuant to subsection
(b)(4)
above.
With each shipment of such wastes the owner or operator of
the recycling facility shall submit
a certification
described in subsection
(b)(5)
above and a notice that
includes the information listed in subsection
(b)(4) above
(except
the
manifest
number)
to
the
Agency.
The
recycling
facility also shall keep records of the name and location of
each entity receiving the hazardous waste—derived product.
C)
Except where the owner or operator
is disposing of any waste that
is a recyclable material used in a manner constituting disposal
pursuant to 35
Ill.
Adm.
Code 726.120(b),
the owner or operator of
any land disposal facility disposing any waste subject to
restrictions under this Part shall:
1)
Have copies of the notice and certification specified in
subsection
(a) or
(b)
above and the certification specified
in
Section
728.1084,
if
applicable.
2)
Test the waste,
or an extract of the waste or treatment
residue developed using the test method described
in Section
728.Appendix A or using any methods required by generators
under Section 728.132,
to assure that the wastee or
treatment residuee a-reis in compliance with the applicable
treatment
standards
set
forth
in
728.Subpart
B
of
thic
Part
and all applicable prohibitions set
forth in Sections
728.132
or
728.139.
Such
testing
must
be
performed
according to the frequency specified in the facility’s waste
analysis plan as required by 35
Ill.
Adm. Code 724.113 or
725.113.
3)
Where the owner or operator
is disposing of any waste that
is subject to the prohibitions under Section 728.133(f) but
not subject to the prohibitions set forth in Section
728.132,
the owner or operator shall ensure that such waste
is the subject of
a certification according to the
requirements
of
Section
728.108
prior
to
disposal
in
a
landfill
or
surface
impoundment
unit,
and that such disposal
is
in accordance with the requirements of Section
728.105(h)(2).
The same requirement applies to any waste
238
that is
subject to the prohibitions under Section 728.133(f)
and also is subject to the statutory prohibitions in the
codified prohibitions in Section 728.139 or Section 728.132.
4)
Where the owner or operator is disposing of any waste that
is
a recyclable material used in
a manner constituting
disposal subject to the provisions of
35
Ill.
Adm.
Code
726.120(b), the owner or operator
is not subject to
subsections
(c)(1)
through
(c)(3)
above with respect to such
waste
-
d)
~gGeneratore
or treaters that first claim~that hazardous debris
is excluded from the definition of hazardous waste under 35
Ill.
Adm. Code 72~-i.103(~)-(-~+
(i.e.,
debris treated by an extraction
or destruction technology provided by Section 728.Table F,
and
debris that has been delisted)
a*ej~.subject to the following
notification and certification requirements:
1)
A one—time notification must be submitted to the Agency
including the following information:
A)
The name and address of the
RCRA
Subtitle B
(municipal
solid waste landfill)
facility receiving the treated
debris;
B)
A description
of the hazardous debris as initially
generated, including the applicable U.S. EPA hazardous
waste numbers; and
C)
For debris excluded under 35
Ill. Adm. Code
728.l03(f)(2),
the technology from Section 728.Table
F-,- used to treat the debris.
2)
The notification must be updated
if the debris
is shipped to
a different
facility-,- and,
for debris excluded 35
Ill.
Adm.
Code 721.2(d)(l),
if
a different type of debris
is treated
or
if
a
different
technology
is
used
to
treat
the
debris.
3)
For debris excluded under 35
Ill.
Adm.
Code
728.l03(f)(2),
the owner or operator of the treatment facility shall
document and certify compliance with the treatment standards
of Section 728.Table
F,
as follows:
A)
Records
must
be
kept
of
all
inspections,
evaluations,
and analyses of treated debris that are made to
determine compliance with the treatment standards;
B)
Records
must
be
kept
of any data or information the
treater
obtains
during
treatment
of
the
debris
that
identifies
key
operating
parameters
of
the
treatment
unit; and
C)
For
each
shipment
of
treated
debris,
a
certification
of compliance with the treatment standards must be
signed by an authorized representative and placed in
the facility’s files.
The certification must state
the following:
“I certify under penalty of law that
the debris has been treated
in accordance with the
requirements of 35
Ill. Adm.
Code
728.145.
I
am
aware
that there are significant penalties for making a
false certification,
including the possibility of fine
and imprisonment.”
239
(Source:
Amended at 19
Ill. Reg.
________,
effective
_____________________
Section 728.109
Special Rules for Characteristic Wastes
a)
The initial generator of a solid waste shall determine each U.S.
EPA hazardous waste number
(waste code)
applicable to the waste in
order to determine the applicable treatment
standards under
728.Subpart 0 of this Part.
For purposes of this Part,
the waste
must
carry
the
waste
code for any applicable listing under
35
Ill.
Adxn.
Code 721.Subpart D.
In addition, the waste must carry one or
more of the waste codes under 35
111.
Adm. Code 72l.Subpart C
where the waste exhibits the relevant a characteristic, except in
the case when the treatment standard for the waste code listed in
35
Ill.
Adm.
Code 721.Subpart D operates in lieu of the
standard
for the waste code under 35
Ill. Adm.
Code 721.Subpart
C,
as
specified
in
subsection
(b)
below.
If
the
generator
determines
that its waste displays the characteristic of ignitability
(DOO1)
(and is not in the High TOC Ignitable Liquids Subcategory or is
not treated by INCIN,
FSUBS,CMBST or RORGS of Section 728.Table C
of this Part)4,
er—that
its waste displays the characteristic of
corrosivity
(D002)
and
is prohibited under Section
728.137, Q~
that
its waste displays the characteristic of toxicity
(DO12
through DO43) and
is prohibited under Section 728.138, the
generator shall determine what underlying hazardous constituents
(as defined in Section 728.102)
are reasonably expected to be
present in the D0014, ef—D002,
or D012 through D043 waste.
b)
Where a prohibited waste
is both listed under 35 Ill.
Adm.
Code
72l.Subpart D and exhibits
a characteristic under
35
Ill. Mm.
Code
721.Subpart
C, the treatment standard for the waste code
listed in 35
Ill. Adm. Code 72l.Subpart
D will operate in lieu of
the standard for the waste code under
35
Ill.
Adm.
Code
721.Subpart
C,
provided that the treatment standard for the listed
waste includes a treatment standard
for the constituent that
causes the waste to exhibit the characteristic.
Otherwise,
the
waste must meet the treatment
standards for all
applicable listed
and
characteristic
waste
codes.
c)
In addition to any applicable standards determined from the
initial point of generation,
no prohibited waste whiohthat
exhibits a characteristic under 35
Ill. Adm.
Code 72l.Subpart C
shall be land disposed unless the waste complies with the
treatment standards under 728.Subpart D of this Part.
d)
AwWastes that exhibits
a characteristic ere~also subject to
Section 728.107 requirements, except that once the waste
is no
longer hazardous,
a one time notification and certification must
be placed in the generator~sor treaterLs files and sent to the
Agency.
The notification and certification that
is placed in the
generator’s or treater’s4, files must be updated if the process or
operation generating the waste changes or if the subtitle D
facility receiving the waste changes.
However, the generator or
treater need only notify the Agency on an annual basis
if such
changes occur.
Such notification and certification should be sent
to the Agency by the end of the year4, but no
later than December
31.
1)
The
notification
must
include
the
following
information:
A)
The
name
and
address
of
the
non—RCRA
Subtitle D
hazardous waste (municipal
solid waste landfill)
facility receiving the waste shipment;
and
240
B)
A description of the waste as initially generated,
including the applicable U.S. EPA
hazardous waste
numbers,
the applicable wastowater
or
nonwastcwatcrtreatability group(s),
and the underlying
hazardous constituents
(as defined in Section
728.lo2jjj)
category,
and the subdivisions made within
a waste code basod on waste—specific criteria
(such as
D003,
reactive oyanides)~inDOOl and D002 wastes
prohibited under Section 728.137 or D012 through D043
wastes prohibited under Section 728.138.
treatment standards anilicable to the waste at the
initial point of gencra~ion.
2)
The certification must be signed by an authorized
representative and must state the language found in Section
728.lO7(b)(5)(A).
If treatment removes the characteristic
but does not treat underlying hazardous constituents, then
the certification found
in Section 728.l07(b)(5)(D) applies.
(Source:
Amended at
19 Ill.
Reg.
________,
effective
______________________
SUBPART
C:
PROHIBITION ON LAND DISPOSAL
Section 728.130
Waste Specific Prohibitions——Solvent Wastes
a)
The spent solvent wastes specified in
35 Ill.
Adm.
Code 721.131 as
U4,S~EPAHazardous Waste Numbers FOOl,
F002,
F003,
FOO44, and FOO5
are prohibited under this Part from land disposal
(except
in an
injection well)
unless one or more of the following conditions
apply:
1)
The generator of the solvent waste is
a small quantity
generator of 100 to 1000 kilograms of hazardous waste per
month;—e*
2)
The solvent waste is generated from any
response action
taken under CERCLA or from RCRA corrective action_-,- except
where the waste is contaminated soil or debris;—er-
3)
The initial generator’s solvent waste is a solvent—water
mixture, solvent—containing sludge or solid,
or solvent—
contaminated
soil
(non—CERCLA
or
non—RCRA
corrective
action)
containing lees than
1 percent total FOOl through F005
solvent
constituents
listed
in
Table
AT-n;
or
4)
The solvent waste is a residue from treating
a waste
described in subsections (a)(1),
(a)(2)4, or
(a)(3)_above’t-4,
or the solvent waste
is a residue
from treating a waste not
described in subsections
(a)(l),
(a)(2)4, or (a)(3), provided
such residue belongs to a different treatability group than
the waste
as
initially generated and wastes belonging to
such treatability group are described in subsection
(a)(3).
b)
The FOOl through F005 solvent wastes listed in subsections (a)(1),
(a)(2),
(a)(3)4, or
(a)(4)
above are prohibited from land disposal.
c)
Effoptivo flovombor
8,
1990, tlhe FOOl through F005
solvent wastes
whichthat are contaminated soil and debris resulting from a CERCLA
response or RCRA corrective action or the residue from treatment
of these wastes are prohibited from land disposal.
Until November
241
~s,.i~-.t~iu,triesc wactos may cc
ctisposecl in a ianariii or ourrace
impoundment only if such unit
is in compliance with the
requirements specified
in
40 aPR 268.5(h)(2),
incorporated by
reference in Section 728.105.
d)
The requirements of subsections
(a),
(b)4, and
(c) above do not
apply
if:
1)
The wastes meet the standards of 728.Subpart D; or
2)
Persons have been granted a~nexemption
(adjusted standard)
was granted from
a prohibition pursuant to a petition under
Section 728.106-,. with respect to those wastes and units ~
the activity is covered by the petition; or
3)
Persons
have
been
granted
an
extension
to
the
effective
date
of
a
prohibition
by
U.S.
EPA
pursuant
to
Section
728.105-7-
with
respect
to
those
wastes
and
units
and
the
activity
is
covered
by
the
extension.
(Source:
Amended
at
19
Ill.
Reg.
,
effective
_____________________
Section 728.133
Waste Specific Prohibitionsj—First
Third Wastes
a)
The wastes specified in
35
Ill.
Adm. Code 721.132 as
tJ4,S.
EPA
hazardous wastes numbers listed below are prohibited from land
disposal
(except
in an injection well).
FOO6
(nonwastewater)
KOOl
K004
wastes
specified
in
Section~
728.l43-Q-(-a-)-
and
728.Table
KOO8
wastes
specified
in
Section~
728.14-3-Q-~-aj-and
728.Table
KO 15
KO 16
KO 18
KO 19
KO2 0
KO21
wastes
specified
in
Section
Section~
728.l4~Q-~-a-~-
and
728.Table BT
K022
(nonwastewater)
KO2 4
KO25
nonwastewaters
specified
in
Section~
728.14~3-Q-(-a-~-
and
728.Table BT
KO3O
KO36
(nonwastewater)
KO3 7
KO44
KO45
(nonexplosive)
K046
(nonwastewater)
KO47
K060
(nonwastewater)
K06l
(nonwastewaters containing
less than 15
zinc)
KO62
(non
CaSO4)
KO69
(nonwastewater)
K086
(solvent washes),
K08 7
K09 9
K100
nonwastewaters specified
in Section~728.143Q-(-a-)- and
728.Table
~T
KlOl
(wastewater)
242
1(101
(nonwastewater,
low arsenic subcategory
——
less than
1
total arsenicj
1(102
(wastewater)
1(102
(nonwastewater,
low arsenic subcategory
——
less than
1
total arsenic!
1(103
1(104
b)
The waste specified
in 35
Ill.
Adm. Code 721.132 as U4,S~EPA
Hazardous Waste
No.
1(071
is prohibited from land disposal.
c)
The wastes specified in Section 728.110 having a treatment
standard in 728.Subpart D based on incineration and which are
contaminated
soil
and
debris
are prohibited from land disposal.
e)
The requirements of subsection
(a),
(b)4, and
(c)-,- above-, do not
apply
if:
1)
The wastes meet~the applicable standards specified in
728.Subpart D;—er-
2)
Parsons have been granted a~nadjusted standard was granted
pursuant to Section
728.106-,- with respect to those wastes
and units,
and the activity is covered by the
pctitionadlusted standard or
3)
Persons have been granted an extension to the effective date
of a prohibition by U.S. EPA pursuant to Section 728.105-,-
with respect to those wastes and units and the activity
is
covered by the extension.
~j
This subsection corresponds with 40 CFR 268.33(f),
a provision
whose effectiveness has expired.
This statement maintains
structural consistency with U.S. EPA regulations.
g)
To determine whether a hazardous waste listed in Section 728.110
exceeds the applicable treatment standards specified in Sections
728.1314,
and 728.1430,
and 728.Table
T,
the initial generator
shall 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
the generator may use knowledge of the waste.
If the waste
contains constituents
in excess of the applicable
728.Subpart B
levels, the waste
is prohibited from land disposal and all
requirements
of this Part are applicable except as otherwise
specified.
(Source:
Amended at
19
Ill. Reg.
,
effective
_____________________
Section
728.138
Waste—Specific Prohibitions:
Newly—Identified Organic
Toxicity Characteristic Wastes and Newly-Listed Coke By-
Product and Chlorotoluene Production Wastes
~j
The wastes specified
in
35
Ill. Adm. Code 721.132 as U.S. EPA
hazardous waste numbers 1(141,
1(142, K143,
Kl44,
1(145,
1(147,
1(148,
1(149,
1(150,
and
1(151 are prohibited from land disposal.
In
addition,_debris contaminated with U.S. EPA hazardous waste
numbers FO37,
FO38,
1(107 through 1(112,
1(117,
K118,
1(123 through
1(126,
1(131, K132,
1(136, U328,
U353, U359 and soil and debris
contaminated with B012 through D043.
1(141 through 1(145,
and
1(147
through K151 are prohibited from land disposal.
The following
wastes that are specified
in the table at 35
Ill. Adm. Code
243
721.124(b)
as U.S. EPA hazardous waste numbers DO12,
8013, 8014,
0015,
0016, 0017,
D018,
8019,
D020,
D021,
8022, 0023,
DO24,
D025,
DO26,
D027,
0028,
D029,
8030,
8031,
8032,
DO33, D034,
8035,
8036,
8037,
0038,
D039,
D040,
8041,
8042,
and 8043 that are not
radioactive,
that are managed
in systems other than those whose
discharge
is regulated under the federal Clean Water Act
(CWA;
33
U.S.C.
çç 1251
et seq.).
that are zero dischargers that do not
engage in CWA—eguivalent treatment before ultimate land disposal,
or that are injected
in Class
I deep wells regulated under the
Safe Drinking Water Act
(SDWAI
are prohibited from land disposal.
“CWA—equivalent treatment”,
as used
in this Section, means
biological treatment
for organics,
alkaline chlorination or
ferrous sulfate precipitation for cyanide, precipitation and
sedimentation for metals,
reduction for hexavalent chromium, or
another treatment technology that can be demonstrated to perform
equally to or better than these technologies.
~j
On September
19,
1996,
radioactive wastes that are mixed with any
of U.S. EPA hazardous waste number 8018 through 0043 waste that
are managed
in systems other than those whose discharge is
regulated under the Clean Water Act
(CWA),
in systems that iniect
in Class
I deep wells regulated under the Safe Drinking Water Act
(SDWA),
or
in systems that are zero dischargers that engage
in
CWA—equivalent treatment,
as defined in subsection
(a) above,
before ultimate land disposal are prohibited from land disposal.
Radioactive wastes mixed with any of U.S. EPA hazardous waste
number K141 through 1(145 and
1(147 through
1(151 are also prohibited
from land disposal.
In addition,
soil and debris contaminated
with these radioactive mixed wastes are prohibited from land
disposal.
~j
Between December 19,
1994 and September 19,
1996,
the wastes
included
in subsection
(b)
above may be disposed in a landfill or
surface impoundment only if such unit is
in compliance with the
requirements specified in Section 728.105(h) (2).
~j
The requirements of subsections
(a),
(b),
and
(c)
above do not
apply
if:
-
fl
The wastes meet the applicable treatment standards
specified
in 728.Subpart B
~J
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
~j.
The wastes meet the applicable alternate treatment standards
established pursuant to
a petition granted under Section
728.144
4j
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
To
determine
whether
a
hazardous
waste
identified
in
this
section
exceeds the applicable treatment standards specified
in Sections
728.140 and 728.Table
T,
the initial generator must test
a sample
of the waste extract or the entire waste,
depending on whether the
treatment standards are expressed as concentrations in the waste
extract or the waste,
or the generator may use knowledge of the
waste.
If the waste contains constituents
in excess of the
applicable 728.Subpart D levels,
the waste
is prohibited from land
244
disposal and all requirements of this Part are applicable, except
as otherwise specified.
(Source:
Added at
19
Ill. Reg.
________,
effective
_____________________
SUBPART
0:
TREATMENT STANDARDS
Section 728.140
Applicability of Treatment Standards
A
restricted
waste
identified
disposed only if an extract
of
in
Section
the waste
728.141
may
be
land
or of the treatment
-esiduc of the waste dcvcloDcd using 11etho~1311,
the “~icity
-
~lue
-‘-
Characteristic Leaching Proccdurc, uo~c
no~
~xc~a
~
vn
in Section 728.Tablo A for any hazardous constituent iiutcu
in
Scotion 728.Table A for that waste, with the
following exceptional
D004,
8008,
1(031,
1(084,
1(101,
1(102,
POlO,
POll,
P012, P036,
P038
and U136.
These wastes may be land disposed only
if an extract of
the waste or of the treatment residue of the waste developed using
either Hotbed 1310,
the Extraotion Procedure Toiricity Toot,
or
Method 1311,
the Toxicity Characteristic Leaching Procedure, or
the test method in Ccction 728.Appendix A does not exceed the
concentration shown in Section 728.Tablc
B
for any hazardous
constituent listed in Section 728.Table A for that waste.
Methods
lllfl
r~-,-i
1g11
~
b-.i-h
found in “Test Methods for Evaluating Solid
W”~, Physical/Chemical
do”,
U.S. EPA Publicati.~.,SW 846,
incorporated by reference in 35
Ill. Adm. Code 720.l11.A waste
identified in Section 728.Table T,
“Treatment Standards for
Hazardous Wastes”, may be land disposed only
if
it meets the
requirements found in that Section.
For each waste, Section
728.Table T identifies one
of three types of treatment standard
requirements:
-~~-
Mo
he
-~
LiflOWn
jj~
All hazardous constituents
in the waste or in the treatment
residue must be at or below the values found in that Section
for that waste
(“total waste standards”)
2.).
The hazardous constituents
in the extract of the waste or in
the extract of the treatment residue must be at or below the
values found in that Section
(“waste extract standards”);
or
~
The waste must be treated using the technology specified in
that Section (“technology standard”Y, which
is described in
detail
in
Section 728.Table C, “Technology Codes and
Description of Technology-Based Standards”.
b)
A restrLoted waste
for which a treatment technology is specified
t*~dorSection 728.142(a)
or hazardous debris for which a treatment
technology
is specified under
Section 728.145 may be land disposed
after it
is treated using that specified technology or
an
equivalent treatment method approved by the Agency under the
procedures sot forth in
Section 728.142(b).
For wasto displaying
the characteristic of ignitability
(8001)
and reactivity
(8003),
that arc diluted to meet the deactivation treatment standard in
Section 728.Tablos C and 8
(DEACT),
tho treater shall comply with
the precautionary measures specified in
35
Ill. Adm. Code
724.117(b) and
35
Ill. Mm.
Code 725.1l7(b).For wastewaters,
compliance with concentration level standards
is based on maximums
for any one day,
except for D004 through 8011 wastes for which the
previously promulgated treatment standards based on grab samples
remain
in effect.
For all nonwastewaters, compliance with
concentration level standards
is based on grab sampling.
For
a)
c)
d)
245
wastes
covered
by
the
waste
extract
standards,
the
test
Method
1311,
the Toxicity Characteristic Leaching Procedure,
found in
“Test Methods for Evaluating Solid Waste, Physical/Chemical
Methods”, U.S. EPA Publication SW—846,
incorporated by reference
in Section 720.111, must be used to measure compliance.
An
exception
is
made
for
D004
and
0008,
for
which
either
of
two
test
methods may be used:
Method 1311 or Method 1310,
the Extraction
Procedure
Toxicity
Test,
found
in
“Test
Methods
for
Evaluating
Solid Waste,
Physical/Chemical Methods”,
U.S. EPA Publication SW—
846, incorporated by reference
in Section 720.111.
For wastes
covered
by
a
technology
standard,
the
wastes
may
be
land
disposed
after being treated using that specified technology or an
equivalent treatment technology approved by the Agency pursuant to
Section 728.142(b).
Ex-cept
as
othorwico
specified
in
Section
728.143(c),
a
restricted
waste identified in Section 728.143 may be land disposed only
if
the constituent concentrations in the waste or treatment residue
of
the
waste
do
not
exceed
the
value
shown
in Section 728.Table B
~er any hasardous constituent listed in Section 728.Table
B for
that wpstp.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.
If
a
treatment
standard
has
been
established
in
Sections
728.141
through
728.1’13
for
a
hacardous
waste
that
is
itsel-f
subject
t~o
those standards- rather than the standards for hazardous debris
under
Section
728.145.Notwithstanding
the
prohibitions
specified
in
subsection
(a)
above,
treatment
and
disposal
facilities
may
demonstrate
(and certify pursuant to
35
Ill. Adm.
Code
728.1O7(b)(5))
compliance with the treatment
standards for organic
constituents specified by a footnote
in Section 728.Table T,
provided the following conditions are satisfied:
fl.
The treatment
standards for the organic constituents were
established based on incineration in units operated in
accordance with the technical requirements
of 35 Ill.
Adm.
Code
724.Subpart
0,
or
based
on
combustion
in
fuel
substitution units operating in accordance with applicable
technical requirements;
21
The treatment or disposal facility has used the methods
referenced
in
subsection
(d)(1)
above
to
treat
the
organic
constituents; and
~j
The treatment or disposal
facility may demonstrate
compliance with organic constituents
if good—faith
analytical efforts achieve detection limits
for the
regulated organic constituents that do not exceed the
treatment standards specified
in this Section and Section
728.Table
T
by
an
order
of
magnitude.
For characteristic wastes
(U.S. EPA hazardous waste numbers DOO1,
D002,_and_D012
through
D043
that
are
subject
to
treatment
standards in Section 728.Table T,
“Treatment Standards
for
Hazardous Wastes’,
all underlying hazardous
constituents (as
defined in Section 728.102(i)) must meet universal treatment
standards,
found in Sections 728.148 and 728.Table U prior to land
disposal.
fi
The treatment standards for U.S. EPA hazardous waste numbers FOOl
246
through F005 nonwastewater constituents carbon disulfide,
çyçlohexanone, or methanol apply to
wastes
that
contain
only
one,
two,
or three of these constituents.
Compliance
is measured for
these constituents
in the waste extract from test Method 1311, the
Toxicity Characteristic Leaching Procedure found in “Test Methods
for Evaluating Solid Waste, Physical/Chemical Methods”,
U.S. EPA
Publication SW-846,
incorporated by reference
in Section 720.111.
If the waste contains any of these three constituents along with
any of the other 25 constituents found in U.S. EPA hazardous waste
numbers FOOl through FOO5, then compliance with treatment
standards for carbon disulfide, cyclohexanone,
or methanol
are not
required.
(Source:
Amended at
19
Ill.
Reg.
________,
effective
Section 728.141
Treatment
Standards
Expressed
as
Concentrations
in
Waste
Extract
)
For the requirements previously found
in this Section and for treatment
standards
in Section 728.Table
A,
“Table CCWE-Constituent Concentrations in
Waste Extracts”.
refer to Section 728.140 and 728.Table T,
“Treatment
Standards for Hazardous Wastes”.
U.S. EPA
Publication
CW—84~
once
in
35
Ill.
Mm.
Code
720.111
b)
When wastes with differing treatment standards for
a
constituent
of concern arc 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
noriwastewater 1(061 arc subject to the treatment standard for high
zinc
1(061.
c~
The treatment standards for the constituents
in Fool through P005
that arc listed
in Section 728.Table A only apply to wastop which
contain one,
two, or all three of these constituents.
If the
waste contains any of these three constituents along with any of
the other
26 constituents found
in FOOl through FOO5,
then only
the treatments standards
in Section 728.Tablc A are required.
(Source:
Amended at
19
Ill.
Reg.
________,
effective
__________________
Section 728.142
Treatment Standards Expressed as Specified Technologies
a)
The
following
wastes
in
subsections
(a)(1)
and
(b)(2)
below
and
Sections
728.Table
BT,
“Treatment
Standards
for
Hazardous
Wastes”,
for which standards are expressed as a treatment method rather
than
a
concentration
level,
and
728.Tablc
E
must
be
treated
using
the technology or technologies specified in subsections
(a)(1)
and
(a)(2)
below
and
Section
728.Table
~.
1)
Liquid hazardous wastes containing PCBs at concentrations
greater than or equal to
50 ppm but less than 500 ppm must
be incinerated in accordance with the technical requirements
‘-~~1
.-,—..~
n,_t__t
—
Z
~
£1
—~-—-~
---.-.~----—
-—-i
~_l___
____.,
J,.-.t_____.____
—
—
that may not bL
excccaca
sy
tne
extracted
using
extract
ci
a
waste
or
waste
treatment
rssiguai
Method
1311,
the
Toxicity
Characteristic
Leaching
Procedure,
for
the
allowable
land
disposal
of
such
wastes.
Compliance with these concentrations is required
based
upon
grab
-samples,
unless otherwise noted in Section 728.Table A.
Method
1q11
to
found
in
“Toot )4oth~do
for
~valuating
Solid
W~nto.
247
of
40
CFR
761.70,
incorporated
by
reference
in
35
Ill.
Adm.
Code
720.111,
or
burned
in
high
efficiency
boilers
in
accordance
with
the
technical
requirements
of
40
CFR
761.60.
Liquid
hazardous
wastes
containing
PCBs
at
concentrations
greater
than
or
equal
to
500
ppm
must
be
incinerated
in
accordance with the technical requirements of 40 CFR 761.70.
Thermal
treatment
in
accordance
with
this
Section
must
be
in
compliance with applicable regulations in
35
Ill. Adm.
Code
724,
725,
and
726.
2)
Nonliquid hazardous wastes containing halogenated organic
compounds (HOC5)
in total concentrations greater than or
equal to 1000 mg/kg and liquid HOC-containing wastes that
are
prohibited
under
Section
728.132(e)(1)
must
be
incinerated
in
accordance
with
the
requirements
of
35
Ill.
Adm.
Code
724.Subpart
0
or
35
Ill.
Adm.
Code
725.Subpart
0.
These
treatment
standards
do
not
apply
where
the
waste
is
subject to a treatment standard codified in 728.Subpart
C—ef-
this Part for a specific HOC
(such
as
a hazardous waste
chlorinated solvent for which
a treatment standard
is
established under Section 728.141(a)).
3)
A mixture consisting
of wastewater,
the
discharge
of
which
is
subject
to
regulation
under
35
Ill.
Mm.
Code
309
or
310,
and de minimis losses of materials
from manufacturing
operations
in which these materials are used as raw
materials or are produced as products in the manufacturing
processT
and that meets the criteria of the DOO1 ignitable
liquids containing greater than 10
total
organic
constituents
(TOC)
subcategory—,- 4e~g subject to the DEACT
treatment standard described in Section 728.Table C.
For
purposes
of
this
subsection,
“de minimis losses” include:
A)
Those
from
normal
material
handling
operations
(e.g.,
spills
from
the
unloading
or
transfer
of
materials
from bins or other containers,
or leaks from pipes,
valves, or other devices used to transfer materials);
B)
Minor leaks from process equipment,
storage tanks,
or
containers;
C)
Leaks from well—maintained pump packings and seals;
8)
Sample purgings;
and
E)
Relief device discharges.
b)
Any person may submit
an application to the Agency demonstrating
that an alternative treatment method can achieve a level of
performance equivalent to that achievable by methods specified in
subsections
(a)
above and
(c) and
(d) below for wastes or
specififed
in Section 728.Table F for hazardous debris.
The
applicant
shall
submit
information
demonstrating
that
the
applicant’s
treatment
method
is
in
compliance
with
federal
and
state
requirements,
including
this
Part-7-~ 35
Ill.
Adm.
Code
709,
724,
725,
726,
and
729j.
and
Sections
22.6
and
39(h)
of
the
Environmental Protection Act
(415 ILCS 5/22.6 and
39(h)),- and that
~the
treatment
method
is
protective
of
human
health
~
the
environment.
On the basis of such information and any other
available
information,
the
Agency
shall
approve
the
use
of
the
alternative
treatment
method
if
the
Agency
finds
that
the
alternative
treatment
method
provides
a
measure
of
performance
248
equivalent
to
that
achieved
by
methods
specified
in
subsections
(a)
above
and
(c)
and
(d)
below
and
in
Section
728.Table
F,
for
hazardous
debris.
Any
approval
must
be
stated
in
writing
and
may
contain
such
provisions
and
conditions
as
the
Agency
determines
to
be
appropriate.
The
person
to
whom
such
approval
is
issued
shall
comply
with
all
limitations
contained
in
such
determination.
C)
As
an
alternative
to
the
otherwise
applicable
treatment
standards
of 728.Subpart D of this Part,
lab packs are eligible for land
disposal
provided
the
following
requirements
are
met:
1)
The lab packs
comply with the applicable provisions of
35
Ill.
Adm.
Code
724.416
and
725.416;
BOARD
NOTE:
35
Ill.
Adm.
Code
729.301
and
729.312
include
additional
restrictions
on
the
use
of
lab
packs.
2)
All
haEardous
wastes
contained
in
such
lab
packs
are
speci~.~on
-
.......ppend~.
or
Section
728.Appendix
EThe lab pack does not contain any of the wastes listed in
Section 728.Appendix D;
3)
The
lab
packs
are
incinerated
in
accordance
with
the
requirements of
35 Ill.
Adm. Code 724.Subpart 0 or 35
Ill.
Adm. Code 725.Subpart 0;
and
4)
Any
incinerator
residues
from
lab
packs
containing
8004,
DOO5,
D006,
0007,
D008,
DO1O,
and
DOll
are
treated
in
compliance
with
the
applicable
treatment
standards
specified
for
such
wastes
in
728.Subpart
8.
d)
Radioactive hazardous mixed wastes with treatment standards
specified
in
Section
728.Table
E
arc
not
aubjcct
to
any
treatment
standards
spccified
in
Section
728.141,
723.143,
or
728.Tablc
0.
Radioactive hazardous mixed wastes not subject to treatment
standards
in
Section
728.Table
E
remain
subject
to
all
applicable
~-r~eatment
standards
specified
in
Cectiona
7~~1~1
-
~
1A)
...~
728.Tablc D.—are subject to the treatment standards in Sections
728.140 and 728.Table
T.
Where treatment
standards are specified
for radioactive mixed wastes
in Section 728.Table T,
“Table of
Treatment Standards”, those treatment standards will govern.
Where there
is no specific treatment standard for radioactive
mixed
waste.
the
treatment
standard
for
the
hazardous
waste
(as
designated by EPA waste code)
applies.
Hazardous debris
containing
radioactive
waste
is
not
subject
to
the
treatment
standards
specified
in
Section
728.Tablc
F
but
is
subject
to
the
treatment standards specified
in Section 728.145.
(Source:
Amended at
19
Ill.
Reg.
________,
effective
_____________________
Section 728.143
Treatment Standards eExpressed as Waste Concentrations
For
the
requirements
previously
found
in
this
Section
and
for
treatment
standards in Section 728.Table
A,
“CCW—Constituent Concentrations in Wastes”,
refer to Section 728.140 and 728.Table
T.
“Treatment
Standards
for
Hazardous
mkl..
,-,
~.3__s.1
CI
..-.
st..
~
_L.~i
their
associated
hazardous
constituents
which
must
not
bc
exceodga
by
the
waste
or
treatment
residual
(not
an
extract
of
ouch
waste
or
treatment
r~-r~
ic~un1~
for
tho
n11,-ntr~h1r~
lond disposal
of
nii,~h
Wastes”.
£_t._
~.—.-_
249
b
When wastes with different treatment standards for a constituent
of concern are combined for purposes of treatment, the treatment
residue must moot the lowost treatment standard for the
constituent
of concern.
Notwithstanding the prohibitions specified in subsection
(a)
and
C)
Table
B, treatment and disposal facilities may demonstrate
(and
certify pursuant to Section 728.l07(b)(5)) compliance with the
treatment standards
for organic constituents specified by a
footnote in Table B, by satisfying the following conditions:
1)
The treatment standards for the organic constituents were
established based on incineration in units operated in
accordance with the technical requirements of 35
Ill. Mm.
Code 724.Subpart 0 or 35
Ill. Mm.
Code 725.Cubpart 0,
or
based on combustion in fuel substitution units operating
in
accordance with applicable technical requirement-a;
2)
The treatment or disposal facility has used the methods
referenced in subsection
(c)(1)
to treat the organic
—
3)
The treatment or disposal
facility has boon unable to detect
the organic constituents despite using its best good—faith
efforts as defined by applicable standards.
Until such
standards
are
developed,
the
treatment
or disposal facility
may demonstrate such good faith efforts by achieving
detection limits
for the regulated for the regulated organic
constituents which are less than ten times the treatment
standard specified in this Section.
(Source:
Amended
at
19
Ill.
Reg.
,
effective
_____________________
Section
728.145
Treatment
Standards
for
Hazardous
Debris
a)
Treatment standards.
Hazardous debris must be treated prior to
land disposal as follows unless the Board has determined,
under 35
Ill.
Adm.
Code
721.103(d)
(2),
that
the
debris
is no longer
contaminated
with
hazardous
waste
or
the
debris
is
treated
to
the
waste-specific treatment standard provided
in this Subpart for the
waste contaminating the debris:
1)
General.
Hazardous
debris
must
be
treated
for
each
“contaminant subject to treatment”~defined by subsection
(b) of thip Soctionbelow,
using the technology or
technologies
identified
in
Section 728.Table F.
2)
Characteristic debris.
Hazardous debris that exhibits the
characteristic of ignitability,
corrosivity,
or reactivity
identified under
35
Ill.
Adm. Code 721.121,
721.122,
afidor
721.123,
respectively, must be deactivated by treatment
using one of the technologies identified in Section
728.Table
F.
3)
Mixtures of debris types.
The treatment standards of
Section 728.Table F must be achieved for each type of debris
contained
in
a mixture of debris types.
If an
immobilization technology is used
in
a treatment train,
it
must be the last treatment technology used.
250
4)
Mixtures of contaminant types.
Debris that is contaminated
with two or more contaminants subject to
treatment
identified under subsection
(b)
of this Seotionbelow must be
treated for each contaminant using one or more treatment
technologies identified in Section 728.Table
F.
If an
immobilization technology
is used in a treatment train,
it
must be the last treatment technology used.
5)
Waste PCB5.
Hazardous debris that
is also
a waste PCB under
40 CFR 761
is subject to the requirements of either 40 CFR
761 or
the
requirements
of this Section, whichever are more
stringent.
b)
Contaminants subject to treatment.
Hazardous debris must be
treated for each “contaminant subject to treatment”.
The
contaminants
subject to treatment must be determined as follows:
1)
Toxicity
characteristic debris.
The contaminants subject to
treatment
for
debris
that
exhibits
the
Toxicity
Characteristic
(TC) by 35
Ill. Mm.
Code 721.124 are those
EP constituents for which the debris exhibits the TC
toxicity characteristic.
2)
Debris contaminated with listed waste.
The contaminants
subject to treatment
for debris that
is contaminated with
a
prohibited listed hazardous waste are those constituents ~
wastes for which BDATtreatment standards are established for
the waste under Sections 728.1440 and
728.44-STable_T.
3)
Cyanide reactive debris.
Hazardous debris that is reactive
because
of
cyanide
must
be
treated
for
cyanide.
c)
Conditioned exclusion of treated debris.
Hazardous debris that
has been treated using one of the specified extraction or
destruction technologies in Section 728.Table F and that does not
exhibit
a characteristic of hazardous waste identified under
35
Ill.
Adrn. Code 721.Subpart C after treatment
is not a hazardous
waste and need not be managed in a subtitle C facility.
Hazardous
debris contaminated with a listed waste that
is treated by an
immobilization technology specified in Section 728.Table F
is
a
hazardous waste and must be managed in a RCRA Seubtitle C
treatment,
storage,
or disposal facility.
d)
Treatment residuals
1)
General requirements.
Except as provided by subsections
(d)(2) and
(d)(4)
below:
A)
Residue from the treatment of hazardous debris must be
separated from the treated debris using simple
physical or mechanical means;
and
B)
Residue from the treatment of hazardous debris
is
subject to the waste—specific treatment standards
provided by 728.Subpart
0 of this Part for the waste
contaminating the debris.
2)
Nontoxic debris.
Residue from the deactivation of
ignitable,
corrosive, or reactive characteristic hazardous
debris
(other than cyanide-reactive)
that
is not
contaminated with a contaminant subject to treatment defined
by subsection
(b)
above, must be deactivated prior to land
251
disposal and is not subject to the waste—specific treatment
standards of 728.Subpart D of this Part.
3)
Cyanide—reactive debris.
Residue from the treatment of
debris
that
is
reactive
because
of
cyanide
must
meet
the
standards for U.S. EPA hazardous waste number DOO3 under
Section 728.143.
4)
Ignitable nonwastewater residue.
Ignitable nonwastewater
residue
containing
equal
to
or
greater
than
10
total
organic carbon is subject to the technology—based standards
for U.S. EPA hazardous waste number DOOl:
“Ignitable Liquids
based on 35
Ill.
Adm.
Code
721.121(a)(l)”~
under
Section
728.142.
5)
Residue from spalling.
Layers of debris removed by spalling
are hazardous debris that remain subject to the treatment
standards of this Section.
(Source:
Amended at 19
Ill.
Reg.
________,
effective
______________________
Section 728.146
Alternative Treatment Standards Based on HTMR
Section 728.Table C identifies alternative
trc....~...... standardo
1(062 ncnwacitewatera.For the treatment standards previously found
in Section
728.Table G,
as
formerly referenced
in this Section. refer to Sections 728.140
and 72$.Table T,
“Treatment Standards for Hazardous Wastes”.
(Source:
Amended at
19
Ill.
Reg.
________,
effective
_____________________
Section 728.148
Universal Treatment Standards
Section 728.Table U,
“Universal Treatment Standards
(UTSP’, identifies the
hazardous constituents,
along with the nonwastewater and wastewater treatment
standard levels,
that are used to regulate most prohibited hazardous wastes
with numerical, limits.
For determining compliance with treatment
standards
for underlying hazardous constituents,
as defined in Section 728.102(i),
these
treatment standards may not be exceeded.
Compliance with these treatment
standards is measured by an analysis of grab samples, unless otherwise noted
in Section 728.Table
U.
(Source:
Added
at
19
Ill.
Reg.
________,
effective
_____________________)
Section 728.Appendix D
Organometallic Lab PackoWastes Excluded from Lab Packs
Hazardous waste with the following U.S. EPA hazardous waste codes may not be
placed in lab Packs under the alternative lab pack treatment standards of
Section 728.142(c):
DOO9,
F0l9,
1(003.
1(004,
1(005,
1(006.
1(062,
1(071,
1(100,
1(106,
POlO.
POll, P012,
P076, P078,
U134,
and U15l.
Hazardous
waste
with
the
following
hazardous
waste
code
numbers
may
be
placed
in
an
“organomctallic”
or
“Appendix
D
lab
pack:11
POOl,
P002,
P003,
P004,
P005,
P006,
P007,
P008,
P009,
P013,
P014,
P016,
P016,
P017,
P018,
P020,
P021,
P022,
P023.
P024.
P026.
P027.
P028.
P029.
P030.
P031.
i’U.~’Ig
~tJ.3V,
iU.~/,
iU35~
1~U~tJ,
L’U~.L,
L’LI~JJ,
iU~,
P046,
P047,
P048,
P049,
P050,
P051,
P064,
P056,
P057,
P058,
P059,
P060,
P062,
P063,
p064, P066, P066,
P067,
P068,
P069,
P070,
P071, P072,
P073, P074, P075,
P073,
P0-81,
P082,
P084,
P086,
P087,
P088, P089,
P092, P093,
P094,
P095,
P096,
P097,
P098, P099,
P101, P102,
P103,
P104, P105,
P106, P108,
P109,
P110,
P111,
P112,
P113,
P114,
P116, P116,
P118,
P119,
P120,
P121,
P122,
P123
252
U0O1,
U002,
U003, U004,
U0OS, 0006,
UOO7,
0008,
U009, 0010,
0011,
0012, U014,
U015,
U0l6,
U017, 0018,
0019, U020,
0021,
0022,
0023, 0024,
0025,
0026,
0027,
U028,
0029,
U030, U031,
U032, U033,
0034,
0035,
0036, U037,
0038,
0039, U041,
U042,
U043,
0044,
U045,
U04?,
U047,
0048,
U049,
0050,
0061,
0062,
0063,
U055,
UO56,
U057,
U058,
UOS9,
U060,
U061,
U062, 0063,
U064, U066,
U067,
0068, 0069,
U070,
U071,
UO72, 0073,
U074, 0075,
0076, 0077, U078,
0079,
UO80,
0081,
0082,
0083,
U081,
U085,
0086,
0087,
U088,
0089, U090r 0091,
UO92,
U093,
U094, 0095,
U096,
U097,
0098, 0099,
0101,
(3102,
U103, UlOS, U106,
0107,
U108,
0109, 0110,
U111,
0112,
U113,
0114,
U1l5,
0116,
U117,
Ul18,
0119,
0120,
U12l,
U122,
0123,
U124,
Ul25,
Ul26,
0127,
Ul28,
0129,
Ul30, U131,
Ul32,
0133, 0136,
U137, 0138,
U1~10, 0141,
U142,
UiA3,
U144,
U145, 0146,
0147,
U148,
Ul49, UlSO,
0162, U153,
0154,
0155,
0156,
0157,
0158,
0159,
0160,
0161,
U162,
0163,
0164,
U165,
(3166,
Ul67, U1?8, 0169, 0170,
U171,
Ul72, 0173,
0174,
0176,
U177, U178,
U179,
0180,
U18l,
Ul82,
U183,
0184,
UlBS,
0186, 0187,
0188,
U189,
UlOO, 0191,
0192,
0193,
Ul94,
Ul96,
0197,
U200,
U201,
U202,
0203,
0204,
0205,
0206,
U207,
U208,
0209,
0210,
U211,
U213, 0214,
U216, 0216,
U217,
0218, 0219,
0220,
U221,
U222,
0223,
U225,
U226,
0227,
0228,
0234,
0235,
U236,
0237,
U238,
0239,
0240,
U243,
0244,
U246,
0247,
U248, 0249
FOOl,
F002,
F003,
F004,
FOpS,
F006, FOb,
F020,
F021,
F022,
F023,
F024,
F025
F026,
F027,
F028,
FO3~
1(001,
1(002,
1(008,
1(009,
1(010,
1(011,
1(013,
1(014,
1(016,
1(016,
1(017,
1(019,
1(019,
1(020,
1(021,
1(022,
1(023,
1(024,
1(026,
1(026,
1(027,
1(028,
1(029,
1(030,
1(031,
1(032,
F03~.. V.034.
T-C035. K03~. K037.
KO3A.
K039.
K040.
V041.
V,042. R04~. VOU.
V04S
1(046,
1(047,
K048,
1(049,
1(050,
1(051,
1(052,
1(060,
1(061,
1(069,
1(071,
1(073,
1(083,
1(084,
1(085,
1(086,
1(087,
1(093,
1(094,
1(095,
1(096,
1(097,
1(093,
K099,
1(101,
1(102,
1(103,
1(104,
1(106,
1(113,
1(114,
1(116,
1(116
DOOl,
D002,
D003,
D004,
D005, DOO6,
D007,
D008,
D010, Doll,
DO12,
D013,
D014,
D015,
D016, D017
BOARD
NOTE:
35
Ill.
Adm. Code 729.301 and 729.312 include additional
limitations
on
the
use
of
lab
packs.
(Source:
Amended
at
19
Ill.
Reg.
effective
Section 728.Appendix E
Organic Lab Packs
(Repealed)
Hazardous
wastoc
with
the
following
Hazardous
Waste
Code
No.
may
be
placed
in
an “organic” or “Appendix C”
lab pack:
P001,
P002,
P003,
P004,
P005,
P007,
P008, P009,
P014, P016,
P017,
P018,
P020,
P021,
P022,
P023,
P024,
P026, P027,
P029, P030,
P031, P033,
P034,
P037,
P039,
P040,
P041,
P042,
P043,
P044,
P045,
P046,
P047,
P048,
P049, P050,
P061,
P064,
P0-57,
P058,
P059,
P060,
P062,
P063,
P064,
P066,
P067,
P068,
P069,
P070,
P071,
P072,
P075,
P077,
P081,
P082,
P084,
P085,
P088,
P089,
P093,
P094,
P095, P097,
P098,
P101,
P102,
P105,
P106, P108,
P109,
P111,
P112, P116,
P118,
P123
0001, 0002,
0003, 0004,
0005, UOO6,
(3007,
U008,
0009, 0010,
0011,
0012, 0014,
UO1S, U016, Ugh,
0018,
0019, UO20,
0021,
U022, 0023,
0024,
0025,
0026, U027,
0028, 0029,
0030,
0031,
0033,
0031,
0036,
0036,
0037, 0038,
0039,
0041, 0042,
UO43,
0044, 0045,
U046,
U047,
U048,
0049,
UO50,
0062, 0063,
U065, UOS6,
U057,
U058,
U059,
0060,
0061,
13062,
0063,
0064,
0066,
U067, 0068,
U069,
UO7O,
0071,
0072, U073,
U074,
U075,
U071, U077,
0079,
U079,
0080,
0081,
0092, 0083,
U084,
U086, U086,
U097,
0088, 0089,
U090,
0091,
13092, 0093,
0094,
0095,
U096,
0097,
0098,
0099,
0101,
Ul02,
0103,
Ul05,
0106,
0107,
0108,
0109,
0110,
Ulhi,
0112,
U113,
U114,
0116,
0116,
U1l7,
0118, 0119,
U120,
U121, 0122,
0123,
U124,
U125,
0126,
U127,
0128,
Ul29,
U130,
0131,
0132,
U133,
Ul35,
0137,
(3139,
0140,
0141,
0142,
0143, -0147,
0148, U149,
UlSO,
0162,
Ul63,
0164, 0165,
0166, 0157,
0158,
0159,
(3160, 0161,
0162, U163,
0164,
U165,
0166,
Ul67, Ul68,
0169, U170,
0171,
0172,
U173,
0174,
0176, U177,
0178,
0179,
0180,
0181, 0182,
0183, 0184,
0185,
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254
‘Constituents of
concern.
•Treatability
group.
‘Manifest number.
‘Waste analysis
data
(where
available).
Certification
statement required
under Section
728.107(a)(2) (B)
that waste complies
with treatment
standards and
prohibitions.
C. Waste
is
sub—
Each shipment
Receiving
Notice must
lect to exemption
facility
include:
from a prohibition
on the type of
•Statement that
land disposal
waste
is not
utilized for the
prohibited from
waste.
such as
a
land disposal.
case—by-case
extension under
•U.S.
EPA hazardous
Section 728.105,
waste number.
an exemption under
Section 728.106,
•Constituents of
or
a nationwide
concern.
caPacity variance
(see Section
‘Treatability
728.107(a(3)).
group.
‘Manifest number.
•Waste analysis
data
(where avail-
able).
‘Date the waste
is
subject to the pro-
hibitions.
D. Waste
is being
Minimum of 30 days
Agency.
Deliv—
Generator must
accumulated
in
prior to treatment
ery must be
develop,
keep on—
tanks or
activity,
verified,
site,
and follow a
containers
written waste
regulated under 35
analysis plan
Ill. Adm. Code
describing
722.134 and
is
procedures used to
being treated
in
comply with the
such tanks or con—
treatment
tainers to meet
standards.
applicable treat-
ment standards
If waste
is shipped
(see Section
off—site,
generator
728.107
(a)(4LL~
also must comply
255
with notification
reguirement of See--
tion 728.107(a) (2).
E. Generator
is
managing
a
lab
pack containing
certain
wastes
and
wishes
to
use
an
alternative
treat-
ment standard
(see
Section
728.107
(a)
(8)).
Each shipment
Treatment
facility
tsXr~f~i~
in
~r~t~r~r—
dance with Section
728.107(a) (1).
,
and
(a)(6),
(a)(5)
where applicable.
Certification
in
accordance
with
(a) (8).
728.107
F.
Small quantity
2~fl r’ators with
tolling agreements
(pursuant to
35
Ill. Adm. Code
722.l20(e~)
(see
Section 728.107
(a) (9)).
Initial shi~nent
Treatment
facility
Must r”~.vwith
applicable notifi-
cation
and
certfication
requirements
in
Section 728.107(a).
Generator also must
retain copy of the
nntific~tir~n ~nd
certification to-
gether with tolling
agreement on—site
for at least
3
after
t~rmi
—
nation or expira-
tion of agreement.
G.
Generator has
determined waste
is restricted
based solely on
his know1ed~eof
the waste
(see
Section 728.107
(a) (5)).
Generator’ s
file
All supporting data
must be retained
on—site
in gener-
ator’s files.
H. Generator has
determined waste
is restricted
based on testing
waste or an ex-
tract
(see Section
728.107(a) (5)).
Generator’ s
file
All waste analysis
data must be re-
tained on—site in
generator’s files.
I. Generator has
determined that
waste is excluded
from the
definition of
hazardous or solid
waste or exempt
from
RCRA
Subtitle
C
(hazardous
waste) regulation
One-time
Generator’ s
file
Notice of
generation and sub-
sequent exclusion
from the definition
of hazardous or
solid waste,
or
exemption from
RCRA
Subtitle C
(hazardous waste)
regulation,
and
information
regarding the
(see Section
728.107(a) (6)).
256
disposition of the
waste.
3. Generator
(or
treater) claims
that hazardous
debris
is excluded
from the
definition of
hazardous waste
under 35 Ill.
Adxn.
Code 721.l03(f)(1)
(see Section
728.107(d)).
Agency.
Notification
must be undated
as necessary
under Section
728.107(d) (2).
Notice must
include:
‘Name and address
of
RCRA
Subtitle D
(municipal solid
waste landfill)
facility receiving
treated debris.
•U.S.
EPA hazardous
waste number and
description of
debris
as initially
generated
‘Technology used to
treat the debris
(Table
1 of Section
728.145).
Certification and
recordkeeping
in
accordance with
Section 728.107
(d) (3).
K. Generator
(or
treater)
claims
that
characteristic
wastes are no
longer hazardous
(see Section
728.109
(d)).
One-time
Generator’s
(or
treater
•
s)
files and
Agency.
Noti-
fication must
be updated as
necessary under
Section
728. 109 (dt±
Notice must
include:
‘Name and address
of
RCRA
Subtitle D
(municipal
solid
waste landfill)
facility receiving
the waste.
•U.S. EPA hazardous
waste number and
description
of
waste
as
initially
generated.
‘Treatability
group.
‘Underlying
hazardous
constituents.
Certification
in
accordance with
Section 728.109
(d) (2).
One-time
L.
Other
recordkeeping
requjrements
(see
Section 728.107
Ia) (7)).
257
Generator’ s
file
Generator must
retain a copy of
all notices,
certifications,
demonstrations,
waste analysis
data, and other
documentation
produced pursuant
to Section 728.107
on—site
for at
least
5 years from
the date that the
waste was last sent
to on—site or off—
site treatment,
storage, or
disposal.
This
period
is
automatically
extended during
enforcement actions
or as requested by
the
Agency.
II. Treatment Facility
A. Waste shipped
from treatment
facility to land
disposal
facility
(see Sections
728.l07(b)(4)
and
(b) (5)).
Each shipment
Land disposal
facility
Notice must
include:
.U.S.
EPA hazardous
waste number.
‘Constituents of
concern.
‘Treatabilitv
group.
‘Manifest number.
‘Waste analysis
data (where
available).
Application
certification,
in
accordance with
Section 728.107
(b) (5) (AL,
(b)(5)(B)
or
(b)(5)(C), stating
that the waste or
treatment residue
has been treated in
compliance with
applicable
treatment standards
and prohibitions.
B. Waste treatment
Each shi~ti-~ent
residue from a
Receiving
facility
Treatment,
storage,
or disposal.
treatment or
storaae facility
will be further
manaaed at a
different
treatment or
storaae facility
(see Section
728.107(b) (6)).
258
facility must
com~lvwith all
notice and
certification
requirements
applicable to
generators.
C. Where wastes
are recyclable
materials used in
a manner
constituting
disposal subject
to Section 726.120
(b)
(see Section
728.107(b) (7)).
Each shi~nent
Agency.
No notification
to
receiving facility
required Pursuant
to Section
728.107(b) (4).
Certification as
described in Sec-
tion 728.lO7(b)(5)
and notice with
information listed
in Section 728.107
lb)(4),
except
manifest number.
III. Land Disposal Facility.
Recycling facility
must keep records
of the name and
location of each
entity receiving
hazardous
waste—derived
products.
A. Wastes accepted
~
by land disposal
facility
(see
Section
728.3.07
(C)).
Maintain copies of
notice and
certifications
specified in
~Section728.107(a)
and
(b).
Certification Statements
A.
I
certify under penalty of law that
I personally have examined and pm
familiar with the waste through analysis and testing or through knowledge
of the waste to support this certification that the waste complies with
the treatment standards
specified in 35
Ill.
Adm.
Code 728.Subpart D and
all applicable prohibitions set
forth
in
35
Ill.
Adm. Code 728.132 or
RCRA
section 3004(d).
I believe that the information
I submitted is true,
accurate and complete.
I am aware that there are significant penalties
for submitting a false certification,
including the possibility of fine
~n~imprisonment.
(Section 728.107(a)(2)(B))
B.
I certify under penalty of law that
I personally have examined and am
familiar
with
the
waste
and
that
the
lab
rack
does
not
contain
any
wastes
identified
at
Section
728.Appendix
D.
I
am
aware
that
there
are
gignificant penalties for submitting a false certification,
including
possibility of fine or imprisonment.
(Section 728.107(p) (8))
C.
I certify under penalty of law that
I have personally examined and am
259
familiar with the treatment technology and operation of the treatment
process used to support this certification
and that, based on my inquiry
of
those
individuals
immediately
responsible
for
obtaining
this
information,
I
believe
that
the
treatment
process
has
been
operated
and
maintained properly so as to comply with the performance levels specified
in 35 Ill.
Adm. Code 728.Subpart
D, and all applicable prohibitions set
forth in 35 Ill.
Adm.
Code
728.132
or
RCRA
section 3004(d) without
impermissible dilution of the prohibited waste.
I am aware that there are
significant
penalties
for
submitting
a
false
certification,
including
the
~g~sibilitv of fine and imprisonment.
(Section 728.107(b)(5)(A))
D.
I certify under penalty of law that the waste has been treated
in
accordance with the requirements of 35
Ill. Adm.
Code
728.142.
I
am
aware
that
there
are
sianificant
penalties
for
submitting
a
false
certification,
including the possibility of fine and imprisonment.
(Section 728.107
(b) (5)
(BIl
E.
I
certify
under
penalty
of
law
that
I
have
personally
examined
and
am
familiar with the treatment technology and operation of the treatment
process used to support this certification and that, based on my inquiry
of
those
individuals
immediately
responsible
for
obtaining
this
information,
I believe that the nonwastewater organic constituents have
been
treated
by
incineration
in
units
operated
in
accordance
with
35
Ill.
Adm. Code 724.Subpart 0 or 35
Ill. Adm. Code 725.Subpart 0 or by
combustion in fuel
substitution units operating
in accordance with
applicable technical requirements, and
I have been unable to detect the
nonwastewater organic constituents,
despite having used best good faith
efforts to analyze for such constituents.
I
am aware that there are
significant
penalties
for
submitting
a
false
certification,
including
the
p~ssibilitvof fine and imprisonment.
(Section 728.107(b)(5)(C))
F.
I
certify
under
penalty-
of
law
that
the
waste
has
been
treated
in
accordance with the requirements of
35
Ill.
Adm.
Code
728.140
to
remove
the hazardous characteristic.
This decharacterized waste contains
underlying hazardous constituents that require further treatment to meet
universal
treatment
standards.
I
am
aware
that
there
are
significant
penalties for submitting a false certification,
including
the
possibility
of fine and imprisonment.
(Section 728.107 (b) (5)(D))
G.
I
certify
under
~enaltv
of
law
that
the
debris
have
been
treated
in
accordance with the requirements of
35
Ill.
Adm.
Code 728.145.
I am aware
that there are significant penalties for making a false certification,
including the possibility of fine and imprisonment.
(Section 728.107
(d)
(3) (C))
(Source:
Added at
19
Ill. Reg.
________,
effective
______________________
Section 728.Table A
Constituent Concentrations in Waste Extract
(CCWE)
For the requirements previously found in this Section and Section 728.141,
refer
to
Section
728.140
and
728.Table
T,
“Treatment
Standards
for
Hazardous
Wastes”.
D,
F
anu
r,. i.~iotoaWastes
CAl
No.
for
Conccntra—
Regulated
Conoontra—
tion
(mg/-L-)-
Waste See
Rcgui.atca Haz~iraouo
Hac~ardous
tion
(mg/L)
Nonw3stcwat—
Code
Also
Constituent
Conotitucnb Waetewatcrs
e-~-e
260
D004
Table
B
Arsenic
7440
38—2-
NA
~.p
fI’~
DOGS
Table B
Barium
7440-39-i
NA
100-.
D006
Thblc
B
Cadmium
7-440-43
9
NA
DOO-7
Tabl-e--B
Chromium
(Total)
7440-47—3k
NA
7439 921
NA
-S-~-0
5.0 IA
0.20
D-008
Table—B Lead
D009
(Low
Mercury
Subcatcgory-—lcsc
Tables
Mercury
D~D
than
260
mg/kg
Mercury)
7439 97—6
NA
D-O-10
Table—B
Selenium
7792-19—2
NA
.S-r~7.
DOll
Tabl-e---R
Cilvcr
7440 22—4
NA
75-15-0
NA
108
94-1
NA
67-56—i
NA
.S--G
4-~.&
0.75
0.75
F001-F005 spent solvents
Tabl-e---B
Carbon dioulfide
Cyclohcxanonc
Methanol
F-O-0-6
Table--B Cadmium
7440-43—9
NA
3440
47
32
NA
7439
92-1
NA
7440-02—0
NA
7440-22—1
NA
0-~.-0-6-6
5-~.4
0.51
0.32
0.0Th
Chromium
(Total)
Load
Niokcl
Silver
FO0-7
Table—B
Cadmium
7440
4-3—9
NA
7440-47—32
NA
3439—92—1
NA
7440-02—0
NA
7440-22—4
NA
0.066
6-,4
Q-.-6-1
O-.32
0.0-7-2
Chromium (Total)
Lead
N-ickel
Silver
FOOS
Table—B
Cadmium
7440-43—9
NA
3440 47
32
NA
7439
92
1
NA
7440-02—0
NA
7440-22—4
NA
0.066
~-r2
0.51
0.3a
0.072
Chromium (Total)
Lead
N-iekcl
Si-1-vcr
F-009
Table
0
Cadmium
Chromium (Total)
7440-43-9
NA
3-440-47—32
NA
7439—92—1
NA
7440
02
0
NA
7440
22
4
NA
0-.066
S-~-2~
0.51
0.32
0.072
Lead
Nickcl
Silver
FOil
Tabl-e---B
Cadmium
7440-43—9
NA
7440
47
32
NA
7439 92—1
NA
7410-02—0
NA
7440—22—4
NA
0.066
-4
0.51
0.32
0.072
Chromium
(Total)
Lead
Nickel
Silver
F012
‘~-ab1c--B Cadmium
Chror~.
-—
-
7440
43
9
NA
-7-4-4-0-47
32
NA
3439—92—1
NA
7440 02 0
NA
7440-22---4
NA
0.066
&~-2-
0.51
0.32
0.072
Lead
N-ickcl
&ilver
F019
Table-B
3-440-47-32
NA
nium
(Total)
Clwomium (Tot3~1)-
Chromium
Lead
Nickel
(Total)
Chromium
Nickel
(Total)
Chromium (Total)
K006
(anhydrouc)
Table B
Chror
Lead
7440—47—32
7439—92—1
7440—02—0
7440—47
32
7440—02—0
7440
47
32
7440
02
0
NA
0.073
NA
Reserved
NA
0.088
Chromium
(Total)
Chromium
(Total)
7440—4 7—32
NA
261
HxCDD All Hcuaohlorodi
benso
p
diox ins
UxCDF—All
Hcxaohlorodi—
boncofurano
PoCDD All t’entaahloro-
dibcnLo p dioxins
PoCDF-All
Pontaohlorodi—
bonsofurans
TCDD
All
Totrachioro
dibcnso—p dioxina
TCDF—All Totraohloro-
dibcnzofurano
2,4,
5
Trichiorophcnol
2, 4, 6 Trichlorophenol
2,3,
4, 6—Totrachiorophonol
E’cntachlorophcnol
1.
ppb
1.
ppb
1.
ppb
1.
ppb
1.
ppb
1.
ppb
1.
ppb
1.
ppb
1.
ppb
1.
ppb
1.
ppb
1.
ppb
95
95
4
88-06-2
58-90—2
87—86—5
0.05
ppm
0.05
ppm
0.05
ppm
0.01
ppm
(0.05 ppm
0.05
ppm
0.05
ppm
0.01
ppm
F024
Table
B
F037
Table
B
F038
Table
B
Nickel
Antimony
Arsenic
Barium
Cadmium
Tables
B~D
K001
Table B
K002
Table
B
K003
Table B
K004
Table B
K005
Table B
cnrom~....
Lead
Mercury
Nickel
Selenium
Silver
Lead
Chromium
(Total)
(Total)
Lead
Chromium
Lead
(Total)
Chromium
Lead
(Total)
Chromium
(Total)
NA
NA
NA
NA
Section 728.137
7440360
NA
7440—38—2
NA
7440—39—3
NA
7440—43—9
NA
7440
47
32
NA
7439—92—1
NA
7439—97—6
NA
7440—02
0
NA
7782—49
2
NA
7440—22—4
NA
7439
92—1
NA
7440—47—32
NA
7439—92—1
NA
7440—47
32
NA
7439—92—i
NA
7440 47—32
NA
7439921
NA
7440—47—32
N-A
7439 92—1
NA
7440—47—32
N-A
7439—92
1
NA
1.7
0.20
1.7
0.20
0.23
0.066
p.51
0.025
0.32
5.7
0.072
0.51
0.094
0,37
0.094
0.37
0.094
0.37
0.094
0.37
0.094
0.37
Lead
I-, t~
Table
B
K007
Table B
7440
47
32
NA
0.094
Chromium
Lead
Chromium
(Total)
(Total)
Nickel
Antimony
Chromium (Total)
Nickel
Chromium
(Tot-al)-
Lead
Nickel
Arsenic
Lead
,,1.........-.,~
,..-..
Nickel
Chromium
Nickel
Chromium
~Total)
(Total-)-
Nickel
Chromium (Total)
Nickel
Chromium (Total)
Nickel
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (Total)
Lead
Mercury
Nickel
Selenium
Silver
Thallium
Zinc
Chromium ~Total)
7439 92—1
7440—47—32
7439—92—1
7440—47
32
7440—02—0
7440 36—0
7440—47—32
7440—02—0
7440
47
32
3439—92
—
7440—02—0
7440
38
2
7439—92—1
7440—47
32
7440—02—0
7440—47—32
7440 02
0
7440—47—32
7440-02
0
7440—47—32
7440-02—0
-3-440
47
32
7440-02—0
74 4 0—3 6—0
7440 38
2
7440—39—3
7440—41—7
7440
43
9
3440
47
32
7439—92—1
3439—97—6
7440
02
0
7782
49
2
7440—22—4
7440
66
6
7440—47—32
7 439—92—1
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
N-A
NA
NA
NA
NA
NA
NA
NA
NA
NA
0.37
0.094
0.37
1.7
0.23 #A
0.32
0,073
0.021
0.088
5.6 #A
0.18
1.7
0.2-0
1.7
0.20
0.20
1.7
0.20
1.7
0.20
0.055
0.014
0.33
0-.-3 7
0.00-9
0.16
0.078
0.094
0.37
Lead
262
1(008
Table B
1(015
Table
B
1(021
1(022
Table
B
Table B
1(028
Table B
1(031
~O46
1(048
Table
B
Tablc B
Table B
1(049
Table
B
1(050
Table
B
1(051
Table
B
1(052
Table B
1(061
Table
B
1(062
Table B
Lead
1(069
(Calcium Sulfate
Tables
Cadmium
B&D
Load
1(071
Table
B Mercury
1(083
Table
B
Nicke~i
-1,
7440—-13—9
-7-4-39
92—1
3439—97—6
3440
02
0
NA
NA
N-A
NA
0.14
0.24
0.025
0.088
263
1(064
Table--B
Arsenic
3440 38-2
NA
5.6 #A
1(08-6
Table--B
Chromium
(Total-)
3440-17-32
NA
0.094
Lead
3439-92—1
NA
0.37
1(087-
Table-B
Load
7439
92
1
NA
0.51
1(10-0
Table
B
Cadmium
3440—13—9
NA
0.066
Chromium
(Potii’i
3440-47-32
NA
Load
7439
92
1
NA
0.5i
fl~01
T-able--&
Arsenic
7440-38—2
NA
5.6
IA
1(102
Table B
Arsenic
3-4-40 38 2
NA
-5.6 IA
1(106 ~Low Mercury Suboatogory--loao than 260 mg/kg Mercury—-residues from
RulEItC)
Table-s
Mercury
7439-97-6
NA
0.020
B—&- 0
r~iuo
(Low Mercury Cubcatcaorv
less than 260 mg/kg Mercury
that arc
not
residues
from
flIIEflC)
Tables
Mercury
7439—97—6
NA
0.025
1(115
Table
B Nickol
7440 02 0
N-A
0.32
P
and
U
Listed
Wastes
CAS
No.
for
Consontra—
Commercial
Regulated
Regulated
Conoontra—
tion
(mg/L)
Waste See
Chemical
Hazardous
Hazardous
tion
(mg/L)-
Nonwactc
Code
Also
Name
Constituent
Constituent
Wagtel.Jatero
watcro
POlO
Table
B
Arsenic
acid
Arsenic
7440—38-2
NA
5.6
IA
P011
Table
B Arsenic
Arsenic
7440
38
2-
NA
5.6
IA
pontox ida
PGI-2-
Table
B
Arsenic tn
Arsenic
7440-38 2
NA
5.6
#21
exide
P013
Table B
Barium
Barium
7440—39—3
NA
5-2-,-
cyanide
I’03-6
Tab-ic
B
Dichioro—
Arsenic
7440—38-2
NA
phenylarcinc
P038
Table
B
Dicthyl—
Arsenic
7440
38—2-
NA
5-.6 #A
arcinc
P065
(Low Mercury Cuboategory
ices than 260 mg/kg Mercury
residues
from
IU4ERC)
Tablos
Mercury
Moroury
7439-97—6
NA
O-.20
B
C.
0
fulminate
r065
~Low
Mercury &ubcatcgory -loss than 260 mg/kg Mercury
incinerator
residues
(and arc not restduoo from
RMEFtC))
Tables
Meroury
Mercury
7439—97—6
NA
0.025
B
C. B
?ulminatc
Nickel
carbonyl
Nickel
eyanidc
P073
Table-B
P074
Table-B
Nickel
Nickel
RMERC-
Tables
NA
NA
0-. 32
0.32
from
0.20
264
7440
02
0
7440—02—0
o
than
260 mg/kg
3-4-39—97—6
than
260
mg/kg
N
JUfERC)
)-
7439—97-6
7440
22
4
778~49
2
7440—22—4
7439—92—1
7782—49
2-
-3-440—47—32
7439—92—1
7440
38
2
7439—92—1-
7439 92
1
7439 92—1
2-60-
~7L3~
7439 97—6
Phenyl
mor
Mercury
cury
acetate
ury
Suboatcgory——lcai
are
not residues
frog
Phenyl mer-
Mcrcury
oury
acetate
Potassium
Silver
silver
cyanide
Selonourca
Selenium
Silver
Silver
cyanide
Totrasthyl
Load
lead
Thallium
Cclcnium
galenite
Calcium
Chromium
chromatc
(Total)
Creosote
Lead
Cacodylic
Arsenic
acid
Lead
acetate
Lead
Lead
Lead
phosphate
Lead sub
Lead
acetate
Mercury
Table-e
B-C.
t)
P099
Table B
P103
Table B
P104
Table B
P110
Table B
P114
Table B
U032
Table—B
U05l
Table-B
U136
Table B
U144
Table B
(1145
Table
B
fl46
Table—B
U151 .(-1~:
--
IUIERC)
Table-s
NA
-1——i~
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
0.025
0.072
0.072
0.51
-r.7
0.094
0.51
0.51
0.51
0.51
from
0.20
Horcu..
8ubcatcaory——lc~
Mercury
-~-‘-cury-—rco1duca
B—C.
D
UlSi
(Low Herour-- Suboategor”-
‘—~
than
~“
mci/ks
Mercury
~
NA
resiouco trom RHERO)
Tables
Mercury
B
&D
U204
Table-B
Selenium
dioxide
(1205
Table—B
Selenium
sulfide
Mercury
Selenium
Selenium
7439-97—6
NA
0.025
7782 49
2
NA
5~~l.
7782
49
2
NA
Waste See
Code
Also
BGC2
~Reacti
NA
Cyanide
e
(Total-)-
0004
Table A
0005
Table -A
D-006
Table A
0007
Table A
0008
Table A
0009
Table A
DOlO
Tab-ic--A
DOll
Table
A
00-12
Table
B
001-3
Table -D
0014
Table—B
0015
Table—B
D016
Table B
0017
Table B
F001-FO05
spar
Acetone
~1
~
Arsenic
Barium
Cadmium
Chromiunl
ITM
Lead
Mercury
Selenium
Silver
Endrin
Lindanc
Mcthoxycxhlor
Toxaphcnc
2, 4—D
57
12
5
7440—38—2
7440
39
3
74 40—43—9
7440
47
32
7439 92—1
7439
97—6
7782—49—2
7440 22—4
720—20
8
58-89
9
72—43—5
8001
35—1
94—75—7
03 76
5
0.28
71 43
2
71 36
3
0.86
100.
0.20
NA
NA
NA
NA
NA
NA
160.
0.07-0
NA
NA
NA
NA
NA
NA
NA
NA
0.13
A
0.066 A
0.18 A
1.3 A
10.0 A
7.9 A
3.7
A
265
IA
Those treatment
standards
have
been
based
on
EP
Leachate
analysis
but
this
does
not -preclude
the
usa
of
TCLP
analyoio-
~B-—Thooe-
waste
codes
arc
not
suboategorised
into
wastewatero
and
nenwas—
tewatero.
NA-
Not
Applicable.
(Source:
Amended
at
19
Ill.
Reg.
effective
Section 728.Table B
Constituent Concentrations
in Wastes
(CCW)
For the reauirements previously found in this Section and for treatment
standards in Section 728.143,
“Constituent Concentrations
in Wastes
(CCW)”,
refer to Section 728.140 and 728.Table
T,
“Treatment Standards
for Hazardous
Wastes”.
D,
1~ and
1(
Liotcd
Wastes
CAC
No.
f or
concentra—
Regulated
Conccntra—
tion (mg/L)
Regulated Hazardous
Liazardouc
tion
(mg/L)
Nonwaste
Constituent
Constituent Wastcwatcro
waters
v?~
ayanidcc cubcategory
based on
35
Ill.
Adm. Code 721.123(a) (5))
57
12—S
Roe.
# 590.
C
—
—
— ——
F
,t
colvori
67—64—1
flcnzcnc
n—Butyl
dl_
I
266
I
..~.t
~
o
creed
_rs~
..t.
~~...iorobcnzcne
Ethyl
Ethyl
acetate
bonseno
Ethyl other
Isc~utyl
alcohol
Methylefte
chloride
Methyl
ethyl
katono
Methyl ioobutyl ketono
Nitrobcnzene
Pyridinc
Totrachlorocthylone
Tolue-ne
56
23
5
108 90
7
95 50—1
141
7
6
100—41—4
60—29—7
~7-8831
75
9-2
3-8—93—3
-1-0-8-10—1
9-8
95
3
1-10
86 1
127—18—4
108-88—3
3-1-55—6
79 00—5
3-9-01-6
76—13—-i
0.057
0.057
0.77
0.11
0.088
0.34
0.057
0.12
-S-rS
0.089
0.28
0.14
0.068
0.014
0.056
0.08
0.054
0-~03O
0.054-
0.057
4--4
~4
3~-3-
5-~-6
4-2-
~3-3,-
~-~4
160.
170.
-~3-~-
-a-6-1-
2-3-~~-
~4-~-
441-
-,-6
2-9-~~-
~-~-6
~7-.-?~-A
-5-~-6
2-8-v
75
69
4
0.02
3~3--
0.32
57
12
5
57—12—5
7440—43—9
7440
47
32
7439
92
1
3-440-02—0
4—-2-
0.86
-i-~-6
0.32
0.040
0.44
590.
-3-0-s-
NA
NA
NA
NA
57
12
5
5712
5
3-4-4-0—47—32
7439—92—1
7440 02
0
4-1-9
9~4
0.32
0.04
0.44
500.
-3-9-,-
NA
NA
NA
-5-3-—12—5
57—12—5
3440-47
32
7439
92
1
7440—02—0
4-~-9
0.13
0.32
0.04
0.44
590.
-3-O--
NA
NA
NA
57—12—5
57
12—5
7440—47—32
3-439—92—1
7440
02
0
4--9
G---l
0.32
0.04
0.44
590.
~9-,-
NA
NA
NA
5~7-12-5
57
12—5
4-1-9
0-~4
4~-5-
NA
57125
57—12—5
7440—47—32-
7439 92—1
3440 02
0
4-,-9
0-T-l
0.32
0.04
0.44
110.
9—~-l
NA
NA
NA
57-12—S
5-7125
7440—47
32
4-~4
0-1-1
0.32
110.
~-l
NA
i,
i,
1,1,2 Trichloroethane
T-Eiahloroethylene
1, 1,2—Triohloro—1,
2,2—
trifluoromethane
Trichloromono fluoromc
thano
Xylericc
(total)
Cyanides (Total)
Cyanideo
(Amenable)
Cadmium
Chromium
Lead
Nickel
Cyanidco (Total)
Cyanidco
(Amenable)
Chromium (Total)
Lead
Nickel
Cyanidoo (Total)
Cyanidoo
(Amenable)
Chromium
Load
Nickel
Cyanides (Total)-
Cyanides
(Amonable)
Chromium
Lead
Nickel
Cyanidco
(Tot-a-i-)-
Cyanidec
(Amenable)
Cyanidee
(Total)
Cyanidoo
(Amenable)
Chromium (Total)
Lead
Nickc1
Cyanidco
(Total)
Cyanides
(Amenable)
Chromium (Total)
1006
Table A
P007
Table A
P008
Tab-b
A
P009
Table A
POlO
NA
P011
Table
A
F012
Table—A
267
Cyani-d-co
(Total)
Cyanidea
(Amcnablc)
208—96—8
-1-2-O---l2
7
71
43
2
5-O---32—8
117—81—7
75
15
0
2 18—01—9
105—67
9
100
41
4
86—73—7
91—20—3
85—01—8
108
95
2
129 00—0
0.059
B
0.059
B
0.14 B
0.059 B
0.061
B
0.28 -B
0.059 B
0.057
8
0.057
B
0.059 B
0--059
B
O-.-O-69
B
0-~
039—B
0.067
B
NA
28. A
14.
A
20. A
12.
A
7.3 A
15. A
~3-.-6 A
14.
A
NA
42. A
34.
A
3.6 A
36.
A
Load
Nickel
P019
Table A
r11IA
~
~‘fl’~A
3-439
92
1
7440 02—9
57—12—5-
5-7
12—5
7440-47—32
~
1~-~~A
—.4—
Table
2_
e- A
C.
Oè-1-oro—
4,3—
buta—
die no
0.04
0.44
0.86
0.32
NA
NA
590.
C
30. C
NA
426—99—8
3
Chloropropcne
1,2—Diahioroethanc
1,2 Dichloropropane
4e-
4~,
—
--
-
~ooroncnc
r~r~nu-l
,3—Diohloropropcn~
Lie
(
2-cthylhcxyl
)
phthalatc
0.28 A
107
05
1
75—34—3
-1-0-7
—
06—2
78 87
5
1-0061
0-1—5-
10061—02—6
117—81—7
67
72—I
3-440
47—3k
7440—02—0
0.046 B
107
06—2
75—35
4
75
9
2
56—23—5
79-00—5
79
01
6
75
01
4
Chromium (Total)
Nickel
P025
(Light ends oubcatogory)
NA
0-hboro-
67
66-3
form
.i.
,.~—uionioroctnanc
1,1 Dichlorocthylcn-e
Hcthylcne chloride
Carbon tetrao-hloridc
1,1,2—Trichloroethanc
Trichlorocthylcne
0.28 A
0.28 A
0.014 A
0.014 A
0.014 A
0.014 A
0.014
-A
0.036
A
0.036 A
0.35
0.47
6.2 A
0.21 B
0.025 B
0-.089
B
0.057 B
0.054
B
0.054
B
0.27
B
6.2 A
0.089
B
0.057
B
O-.-054
B
0.054 B
0.27 B
0.055
B
0.055
B
0.055
B
0.28 A
0-.-O-14
A
0.014 A
0.014 A
0.014—A
0.014 A
A
1.8 A
NA
NA
6.2 A
6.2 A
31. A
6.2 A
~-.--2
A
5.6 A
33.
A
3-1. A
6.2 A
6.2 A
A
33. 1~
37.
2i
28.
A
3-0.
A
F025
(Spent filters or
NA
Chboro—
67
66
3
form
ida and dcci
Z-fothybenc chloride
Carbon tetraohborido
1, 1,2 Trichioroethanc
Trichioroothylenc
Vinyl chloride
Hc~achlorobenscnc
Hcxachlorobutadienc
Hexacthloroethane
0.046-B
75—9—2
56—23—5
79 00
5
3-9---
0
1—6
75—01—4
118—74—1
3—68
3
67 72
1
antriracene
ovrcn~
inexyl)
F037
Table A
Aoonaphthcnc
Anthracono
Bcn~ene
Bcnzo(a)
is(2
ethy’
phthalatc
Chryocne
-p~1’~
Ethylbcnzenc
Fluorene
Naphthabone
Phenanthreno
Phenol
Pyrcnc
-butvl
Iti...L...L(
268
P038
Table A
F039
(and DOOl
Table
Acetone
sAC.
0
Tolucnc
Xylcno(o)
108 88-3
57—12—5
0.08 B
0.32
B
0.028 A
14.
A
22. A
1.8 A
Cyanidco (Total)
Chromium (Total)
7440—47-32
7439
92
1
Q-,4
0.037
NA
NA
Lead
Benseno
71—43—2
50—32—8
117-81
7
0.14
B
0.061 B
0.28
8
14.
A
12.
A
7.3
A
Benco(a)pyrena
Dio(2
ethylhcxyl)
phthalatc
Chrysene
318—01-9
84—74—2
0.059
0.057
B
B
15.
A
3.6 A
Di—n—butyl phthalata
Ethylbontene
100
41
4
0.057
B
14.
A
Fluorone
86-73
7
0.050
B
NA
Naphthabcno
91—20—3
0.059
B
42.
A
Phenanthronc
85—01—8
0.059
B
34.
A
Phenol
108-95—2
0.039
8
3.6
A
Pyrcnc
129 00 0
0.067
B
36. A
Tolueno
108—88—3
0.080
B
14.
A
Xylcne(s)
0.32
B
22. A
Cyanidea
(Total)
57-12
5
7440 47
32
0.028
0,4
A
1.8 A
NA
Chromium
(Total)
Lead
7439 92—1
0.037
NA
67 64—1
d
D002
wastes
prohibit
~d under
Cection
728.137)
0.28
B
160.
A
Acenaphthalenc
Accnaphthcnc
Aootonitrilc
Acetophenonc
2-Acetylaminofluorene
Acrolien
Acrylonitrilc
Aidrin
4-ArninobiDhenvi
Aniline
Anthraccnc
Aramito
Aroclor 1016
Aroolor 1221
Aroalor 1232
Z~roolor1242
Aroclor 1248
Aroclor 1254
firoclor 1260
alpha-El-IC
beta DUO
delta-BUC
gamma-BHC
Benzcnc
Berizo (a) anthraccne
fonts
(b) fluoranthene
Benzo(k) fluoranthene
Bcnso(g,h,
i)porylcna
Bcnzo(a)pyrcne
Bromodichloromctharie
Bromoform
(Tribromo—
methane)
Bromomethanc
(methyl
208
06-8
0.059
B
3.4
A
83
32
9
0.059
B
4.0 A
75—05—8
0.17
B
NA
96—86—2
0.010 B
9.7 A
53—96
3
0.059 B
140. A
107—02
8
0.29
B
NA
107—13—1
0.24
B
84.
A
309—00—2
0.021 B
0.068 A
92—67
1
0.13 B
NA
62
53
3
0.81 B
14. A
120—12—7
0.059
B
4.0
A
140—57—8
0.36
B
NA
12674
11
2
0-1--013
B
0.92 A
11104—28
2
0.014 B
0.92 A
11141—16—5
0.013
B
0.92
A
53469—21—9
0.017
B
0.92
A
12672
29—6
0.013
B
0.92
A
11097
60
1
0.014
B
1.8
A
11096—82—S
0.014
B
1.8
A
319—84—6
0.00014
B
0.066
A
319
85
7
0.00014
B
0.066
A
319
86
8
0.023
B
0.066
A
58—89—9
0.0017
B
p.066
A
71—43—2
0.14
B
36.
A
56
55
3
0.059
B
8.2
A
205
99
2
0.055
B
3.4
A
207
08—9
0.059
B
3.4
A
191—24—2
0.0056
B
1.5
A
50
32
8
0.061
B
8.2
A
75
27
4
0.35
B
15.
A
75—25—2
0.63
B
15.
A
74
63
9
0.11
B
15.
A
bromide)
269
4-Bromophenyl phenyl ether
n Butyl
alcohol
Butyl bentyl phthalatc
~—scc-Butyl—4, 6-dinitro—
phenol
Carbon
tctrachloride
Carbon dioulfide
Chbordano
p—Chloroaniline
Ohlorobenvcne
Chborobensilatc
2—Chloro-1, 3-butadione
LILU
I
.I~flJ.OL(JELfl
Chioroethanc
~
___
mcL
ri~ji~
101
55
3
71—36
3
86—68—7
88—85—7
0.055
-B
5.6 B
0.017 B
0.066 B
15. A
2.6 A
7.9 A
2.5 A
56—23
5
75—15—0
57—74—9
106 47
8
108 90—7
510—16—6
126—99—8
124
48—1
75
00—3
111—91—1
111—11—4
67 66—3
39638—32 9
0.057 B
0.014 B
0.0033
B
0.46 B
0.057
B
0.10
B
0.057
B
0.057 B
0.27
B
0.036
B
0033
B
0-.-046
B
0.055
B
5.6 A
NA
0.13 A
16. A
5.7
A
NA
NA
16. A
6.0
A
7.2
11
7.2 A
5.6 A
7.2 A
59—50—7
74-87
3
0.018
B
0.19
B
14.
A
33. A
91-8-7
95-57—8
107
05
1
218
01
9
95—48—7
108941
96
12
8
0.055
B
0.044
B
0.036
B
0.059
B
0.11
B
0.77 B
0.3GB
0.11
B
5.6
A
5~.7 A
28.
A
8.2 A
5.6
A
3.2 A
NA
15. A
106—93—4
0.028
B
15.
A
74—95—3
94—75—7
0.11
B
0.72
B
15.
A
10. A
53
19
0
72
54
8
3424—82—6
3-2-~-55—9
389
02
6
50
29
3
53—70—3
-19-2---65—4
541 73—1
9~5
50
1
106—46—7
75—71—8
3-5-343
-10-7-06
2
3-5—35—4
120 83
2
87
65
0
3-8
87
5
40061-01—6
1-0061-02—6
60
57—1
8-4—66—2
-1-05-67—9
1-31
11—3
84
74
2-
0.023 B
0.023
B
0.031 B
0.031 B
0.0039
B
0.0039
B
0.065
B
0.061
A
0.036 B
0.088 B
0.090
B
0.23
B
O.059B
0.21
B
0.025
B
0.054
B
0.044
B
0.044
B
0.85
B
0.036
B
0.036
B
0.017 B
0.20 B
0.036 B
0.047
B
0.057
B
0.087 A
0.087 A
0.087 A
0.087 A
0.087
A
0.087
A
8.2
A
NA
6.2 A
6.2 A
6.2
A
7.2
A
3.2A
7.2
A
33.
A
33.
A
14. A
14.
A
18. A
18.
A
18.
A
0.13 A
28. A
14. A
2-2..
A
28. A
DiS
(~—cnioroetnyi, otner
Chloroform
his (2 Chboroisopropyl)
other
p—Chloro—m—crecol
Chioromethanc
(Methyl
chloride)
2—Chborortaphthalenc
2-Chlorophcnol
3 Chborop~ropeno
Chryacne
o-Crecol
Crccoi
(m-
and
p
isomers)
Cyclohexanonc
1,2
Dibromo
3
chbore-
propane
1, 2-Dibromoothane
(Ethylene dibromidc)
Bibromomcthanc
2,
4-Dichlorophenoxyacotio
acid (2,4—B)
o,p’
DDD
p,p’
DDD
o,p’-DDE
p,p’—DDE
o,p’ DDT
p,p’-DDT
Diben~o(a,h) anthraceno
Diben~o(a,c)pyrone
m—Dichborobcntcrie
o—Dioh1orobcntcne
p—Dichlorobenecnc
Dichlorodifluoromethano
1, 1 Dichioroethane
1,2 Dichloroethane
1, 1-Diohioroethylene
trans-i,2-Dichborocthybeno
2,4 Dichlorophcnol
2, 6 Dichborcphcnol
1,2—Dichioropropano
cia—i, 3—Dichloropropenc
trans-i, 3 Dichboropropcne
Dicidrin
Diethyl phthalate
2, 4-Dimethyl phenol
Dimcthyl phthalate
DI.
n butyl phthalate
270
1,4 Dinitrobentene
4,6 Dinitro o cresoi
2, 4-Dinitrophonol
2,
4-Dinitrotoluone
2,6 Dinitrotoluene
Di-n octyl phthalate
Di—n-propylnitroaoaminc
Diphenylamine
1,2 Diphanyl hydratine
1 ,-4—Dio,cane
Disuifoton
Endoaulfan
I
Endociulfan II
Endosulfan sulfate
Endrin
Ethyl acctate
--
Ethyl cyanide
Ethyl bcnscnc
Ethyl
other
bia(2 Ethyihcxyl)
phthalato
Ethyl
mcthaorvlatc
Famphur
Fluoranthcne
Fluorenc
Hcptachlo-r
Heptachior opoxide
Hcxaohborobcn~eno
Hcxachborobutadienc
Hcxachlorooyclopentadiene
Hexaohborodibensofuranc
Hcxaehlorodibcnzo p-
diox ins
Hcxaohloroothano
Hcxaohboro~ro~ono
100—25
4
534—52
1
51—28—5
121—14—2
606 20 2
117 84-0
621—64—7
122—39—4
-1-22
66 7
621647
123 91—1
298—04—4
930-98-8
33213—6
5
1031—07—8
72—20—8
7421—93 4
141—78
6
107—12—0
100—41—4
60-29
7
117
81
7
0.32
B
0.28
B
0.12 B
0.32 B
0.55 B
0.017 B
0.40 B
0.52
B
0.087
B
0.4GB
0.12
B
0.017
B
0.023
B
0.029 8
0.029 B
0.0028
B
0.025
B
0.34
B
0.24 B
0.057
B
0.12
B
0.28
B
2.3 A
160.
A
160. A
14-0.
A
28. A
28.
A
i-4-.--2\
NA
NA
NA
170. A
6.2 A
0.066 A
0.13 A
0.13 A
0.13 A
0.13 A
33.
A
360. A
6.0 A
160. A
28.
A
97—63—2
75-21—8
52-85-7
206—44—0
36—73-7
75—69
4
76-44-8
1-024—57—3
118—74—1
87—68-3
7-7-47
-4
0.14 B
0.12
B
0.017
B
0.068
B
0.059
8
0.020
B
0.0012
-8
0.016
B
0.055
B
0.055
B
0.057
B
0.000063
160. A
NA
15. A
8-.2
A
4.0 A
33.
A
0.066 A
0.066 A
37.
A
28-. A
3-.6
A
0.001 A
0.00006-3
0.001
A
67—72—1
1888—71-7
193
39
5
74—88-4
78—83—1
‘165—73—6
120 58—1
143
50
3
126—98—7
67—56—1
91 80-5
72 43—5
56—49-5
101—14—4
0.065
8
0.035
B
0.0055
B
0.019
B
5.6 B
0.021
B
0.081 B
0.0011
B
0.21
B
5.6 B
0.081 B
0.25 B
0.0055
B
0.50 B
28.
A
28.
A
8.2 A
65.
A
170. A
0.066
A
2.6 A
0.13 A
84. A
NA
1.5 A
0.18 A
16.
A
35. A
75-09—2
78—93—3
108—10—i
80
62—6
66-27—3
298—00—1
91—20—3
91—59-8
0.089
B
0.28 3
0.14
B
0.14
B
0.018
B
0.014
B
0.059
B
0.52
B
33.
A
36. A
33.
A
160.
A
NA
4.6 A
-3.1
A
NA
Indeno
B
B
c,
d)pyrcne
$1
~1
~
I’-,
~
Iodomcthanc
I aobutanol
~podrin
I sosafrole
KCp?flC
Methanol
Mo-thapyrilcne
Mcthoxychlor
.~—r~nyz.urIuL~1nLrircnc
4,-4—Methylcnc—bis
(2-
eh-loroaniline-~-
Mo-thylene chloride
Mc~hvl
cth~:1kotone
Methyl
ioobuty.L
i~ctonc
Methyl
methasrylate
Methyl methansulfonate
Mc!thvl
riarathion
Naphth~lcnc
p Nitroanilinc
271
98
95
3
99
55
8
100—02—7
55—18—5
62
75
9
924
16
3
105—95—6
59—89—2
100
75
4
930
55
2
56—38—2
608-93—S
82—68
8
87
86
5
62—44—2
85-01—8
108
95
2
208-02
2
85—14—9
23960—58—6
120 00
0
110 86—1
p4-59—7
9 3—72—1
93
76
5
95 94-3
630—20—6
79—34—6
127—18 4
58 90—2
108—88—3
8001-35—1
120 82-1
71
55
6
79—00—5
79—01—6
95-
95
4
88
06
2
96—18—4
76—13—1
126
72 7
75—01—4
57—12—5
16961—48—8
8496-25—8
7440 36—0
7440
38
2
7440-39—3
7440—41—7
7440
43
9
7440—47
32
0.068 B
0.32 B
0.12 B
0.40 B
0.40
B
0.40
B
0.40 8
0.40
B
0.013
B
0.013
B
0.014
B
0.065
B
0. 000063
0.000063
0.055
8
0.089
B
0.081
B
0.059
B
0.039
B
0.021 B
0.69 B
0.093
B
0.067
a
0.014
B
0.081 B
0.72
B
0.72
B
0.055
B
0.000063
0.000063
0.057
B
0.057
B
0-.056
C
0.030 B
0.080 B
0.0095
B
0.055 B
0.054 B
0.054
B
0.054
B
0.18 B
0.035 B
0.85 B
0.057
B
0.11 B
0.27
B
0.32
B
1.2
B
35.
B
14.
B
1.9 B
1.4
B
1.2
B
0.82
B
0.20 B
0-.-3-7
B
14. A
28.
A
29.
A
28.
A
NA
17. A
2.3 A
2.3
A
35. A
35.
A
4.6 A
37. A
0.001 A
0.001 A
4.8 A
7.4 A
16. A
3.1 A
6.2 A
4.6 A
NA
1.5 A
8.2
A
16.
A
22.
A
7.9 A
7.9
it
19.
A
0.001 A
0.001 A
42. A
42.
A
5.6 A
37. A
28. A
1.3
A
19.
A
5.6 A
5.6 A
5.6
ii
37.
A
37. A
28. A
28.
It
NA
33.
It
28. A
1.6 A
NA
NA
NA
NA
NA
NA
NA
NA
Nitrobcnzenc
~
toluidi.....
-..~cro—
4-Ni-trophcnol
N—Nitrocodiethyiaminc
M
Ni-trocodimethylarninc
N Nitroso—di n-butylaminc
N—Nitrooornothylothylamine
N-Nitrocomorpholin-o
N Nitroaopipcridine
N Nitrocopyrrolidine
Parathion
Pcnt-achlorobcneono
Pcntachlorodibcnzo furana
Pcntaohlorodibcnzo-p-
dioxins
Pentachloronitrobentenc
rentachiorophonol
Phenacetin
Phenanthrene
Phenol
Phoratc
Phthalio anhydride
Pronamido
Pyrcne
Pyridinc
Saf role
Silvcx
(2,4,5—TP3
2,4,5 T
1,2
,
4,
5
Tctrachlorobonzene
TetrachiorodibonEofurano
Tetrachiorodibento p-
dioxina
1,1,1,2-Tetraohlorocthanc
1, 1,2,2—Tetrachlorocthane
Tctrachloroethylenc
2,3,4,6 Tctrachlorophcnol
Tolucne
Toxaphone
1,2,4-Trichlorobcntcne
1,1,1 Trichloroethane
1, 1,2-Triahlorocthano
Trichloroothylene
2,4,5-Trichlorophcnol
2, 4,6 Trichlorophcnol
1,2,3—Triohloropropanc
1,1,2—Trichloro—1, 2, 2—tri~—
fluorocthanc
Tri3(2, 3-dibromopropyl)—
B
B
B
B
phosphate
Vinyl
chloride
Xylcnc(e)
Cyanidea- (Total)
Fluoride
Sulfido
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium (Total)
Acrylctxnide
Bentcne
75
05
8
1-07-13—1-
79—06—1
71
43—2
57
12
5
0.06
0.02
21.
Itcetonitrila
Acryionitrilc
Acrylamide
Bencene
Cyanide
1Tht~
Acctonitrilc
Jtcjrvlpnjtrilo
75—05—8
107
13
1
79 06
1
31-43—2-
5-3—12—S
3-5--p5—8
-107-13--I
79—06—I
3-1
43
2-
57
12
S
0.06
19.
0.02
21.
0.06
0.02
21.
1.4—A
23. A
0.03 A
1.8
-A
-i-.-4--
A
23.
A
0-.-03
A
272
Copper
Lead
Mercury
Nickel
Celenium
Cilvcr
Thallium
Vanadium
Zinc
K001
Table A Naphthalone
Phcnanthrcnc
Pyrenc
Tolueno
Load
7440
50
8
7439 92—1
3439—97—6
7440—02—2-
7782—49
2
7440
22
4
3440-28—0
7440—62—2
3-4-40-66
0
~1-20—3
87-86—5
85 01—8
-1-29
00
0
1-08—88—3
7439
02—1
3440—47—32-
7439—92—1
3-440
47 32
3439 92—1
3440-47—32
3-4-3-0
92
1
-3-4-40-47—32
3-4-39
92
1
57
12—S
3440—47—32-
7439
02
1
7440—47—3-2
7439—92—1
-5-7---12
5r
3440-47-32-
34-39—92—1
67
66
3
67-66-3
1(042
Table—A
1(003
Table--A
1(004
Table A
1(445-
Table
A
1(006
T-able---A
1(00-7
Table A
1(008
Table A
oncu
(Totalj
Chromium
Lead
(Tot-al)
Chromium
Lead
(Total)
Chromium (Total)
Load
Chromium
Load
(Total)
Cyanidea
(Total)
Chromium
Lead
(Total)
Chromium (Total)
Lead
Cyanidcs
(Total)
Chromium (Total)
-1-.-3-
-B
0.2-8--B
0-. 1:5-8
0.-55
B
0.82
B
G-.-2-9-B
1.4 B
0.012
B
1.0
B
0.031 A
0.031
it
0.18 A
0.028
A
0.028
A
0.032
it
0.037
Ii
0.9 -B
3.4 -B
0.9
B
3.4
B
0.9
B
3.4 B
0.9—B
3.4 B
0.74 B
B
3.4 B
0.9
B
3.4
B
0.74
B
0.9
B
3.4
B
G~4
0~4
NA
NA
NA
NA
NA
NA
NA
NA
NA
1.5 A
1.5
—A
7.4—h
A
28.
it
33.
it
NA
NA
NA
NA
NA
NA
NA
NA
NA
-B
NA
NA
NA
N-Afl
B
NA
NA
6.0 A
4r0
Lead
K009
NA
C-hloroform
1(010
NA
~1~1-oroform
1(011
NA
Acctonitrilc
Ttcr~r1r~n
tri1r~
—J
1(01-3
NA
1(014
NA
Acrylarnido
Bentenc
273
cuin UI
~
Anthracon-c
Bcn~al Chloride
~----~
—.-~
uoran—
1(015
Table
It
1(016
Nh
1(017
NA
1(018
NA
1(019
NA
1(020
NA
tncnc gnu t1cnco(i~)Iiuoran—
thene
Phenanthrcnc
Tolucnc
Chromium
(Total)
Nickel
Hoxachiorobencone
Hoxachiorobutadiono
Hexachiorocyclopentadienc
Hexachlorocthane
Tetraohloroethone
1,2
Dichloropropane
1,2,3 Trichloropropane
B-ic (2-chloroothyl)
other
Chloroethanc
Chioromethanc
1, 1—Dichlorocthane
-1, 2—Diohlorocthanc
Hcxachlorobcnccnc
Hexachiorobutadienc
Pentaohloroethanc
1, 1, 1-Trichlorocthanc
Hcxachlorocthane
Bici(2—ohloroethyl) ether
Chiorobencene
Chloroform
p Dich1oroben~enc
1,2 Dichiorocthane
Fluorenc
Hcxachloroethanc
Naphthalcnc
Phcnanthrcne
1,2,4,5— Tctraehlor
obcnmono
Tetrachloroethenc
1,2, 4—Triohlorobcnceno
1, 1,
1
Trichlorocthanc
1,2 Dichloroethane
1,1,2,
2-Tetrachlorocthano
TetrachlGroethene
120—12—7
08
87
3
207—08—9
85—01—8
108—89—3
74 40—47—32
7440
02
0
118—74—1
87—68—3
77— 47—4
67 72—1
123—13—4
78
87
5
96 13—4
111—44—4
76
00—3
74 87—3
75—34—3
103—06—2
118
74
1
87
68
3
76—01—7
71—55—6
67—72—1
111—44—4
108 90—7
67
66
3
106
46
7
107—06—2
86—73—7
67—72—1
91
20
3
85—01—3
95 94—3
127
18
4
120—82—1
71—55—6
106—93
4
79—34—6
127—19—4
67
66—3
58
23—5
7-440—36—0
108
88
3
96
86—2
22—39—4
8-6
30 6
108—95
—2
7-440
47—32
3440 02—0
0.059
0.28
0.055
0.059
0.08
0.32
0.44
0.055
0.055
0.057
0.055
0.056
0.85 A B
0.85 A B
0.033 A B
0.27
0.19
0.059
0.21
0.05-5
0.055
NA
0-.-054
0.055
0.03-3
0.057
0.046
0.09
0.21
0.059
0.055
0.059
0.-05-9
0.-p5-5
0.056
0.-U5-6
0.054
0.21
0.057
0.05-6
0.046 B
0.057 B
0.60 B
0.08-0
-8
0.010
0-~52
B
0.40 B
NA
0.039
0.35
0.47
3.4
A
6.2 A
3.4
A
6.0
11
NA
NA
28.
A
5.6
A
5.6 A
28. A
6.0 A
18.
A
28.
A
7.2
it
6.0 A
NA
6.0
It
6.0 A
28. A
5.6 A
28.
It
5.6 A
6.0
it
6.0
A
NA
6.0
A
NA
23.
A
5.6 A
5.6 A
NA
6.0 A
19.
ii
6.0
2t
6.0 A
5.6
A
6.0 A
6.2
A
6.2
It
6.2 A
0.034
A
19.
A
NA
NA
13. A
12. -A
NA
NA
1(021
Table
it
Chloroform
Antimony
1(022
Table
A
Tolucne
Itoctophononc
Diphenylamino
Curn
of Diphcnylamine and
D-iphenylnitrocamine
Phenol
Chromium
(Total)
Nickel
274
(measured as Phthalic
paid)
Phthal
ic
anhydridc
Imca~ured
ai~
i’hthalia
acid)-
1(023
NA
1(024
NA
1(028
Table—h
1(029
NA
1(030
Nh
1(031
Table A
K03~
NA
1(033
NA
1(034
NA
1(035
NA
85
44
9
85 44
9
35 34
3
-8-3—68—3
67
72—1
76 01
7
6-30—20—6
79—34—6
71
55
6
70
00—5
127—18—4
7440—43—9-
3440
47
32
7439 92—1
3440—02—0
6-3
66
3
1-07
06—2
3-5—35—4
31—55—6
3-5- 01
4
95-50—1
106—46—7
87 68
3
67 72—1
1-888-7 l—-7
6-08-93-5
76 01—7
9-5—94
3
-1-2-3--
18—4
1-2-0-82—1
7-440
38—2
77—47—4
57
74 9
76
44
8
1024—57—3
-3-7 47—4
77—47—4
8-3-32
9
1:20
12—?-
5-6—55—3
5-0—32—S
2-18-
01—9
53 70—3
206—44—0
86—73—7
193
39
5
1,1 Dichloroethanc trans
1,2
Diohloroothano
Hcxachlorobut adione
Hcxachloro-cthane
?cntachlorocthanc
1, 1, 1, 2—Tetraohloroethano
1,1,2, 2-Totraohlorocthano
1,1, 1, -Trichlorocthanc
1,1,2-Trichioroethanc
Tctraahloroethylene
Cadmium
Chromium
(Total)
Load
Nickel
Chloroform
1,2
Dichlorocthanc
1, 1—Dichlorocthylcno
1,1,1—Triohlorocthanc
Vinyl chloride
o—Dichlorobcnzono
p—Dichlorobcnccnc
Hexachiorobutadiene
Hexachioroethano
Hcxaohloropropenc
Pontaohlorobonzcno
Pentachioroothanc
1,2,4,
5
-Tctrachlorobcn~cnc
Totrashloroethone
l,-2
,
4—Triohlorohonconc
Arsenic
Hcxaohlorocyolopentadione
Chlordanc
L~eptachlor
Hcptaohlor cpoxidc
Hcxachlorocyclopcntadiene
Hcxachlorocyclopcntadlenc
Accnaphthcne
Anthracone
Bona(a)anthraoono
Benco(a)pyrcnc
Chryscno
Dibcnc(a, h)anthracene
Fluoranthonc
~-1uororte
Indcno(1,2,3 cd)pyrcne
Orcoola
(rn— and p isomers)
0.069
0.069
0-.
05-9
0.054
0.055
0.055
NA
0.05-7
0.-U
57
0.054
0.054
0.0-5-6
0.35
0-.~037
0.47
0.46
0.21
0.025
0.054
0.27
0-.-088
0.09
0-.p55
0.0-5
5r
NA
NA
NA
0.055
0.056
0.055
0.79
0.057
B
0.0033 B
0.0012
B
0.016
B
0.057
B
0.057
B
NA
NA
0.59
B
NA
0.059
B
NA
0.068 B
NA
NA
0.77 B
a. ~
2-8-.-
it
6.0 A
It
5.6 A
23. A
it
5.6 A
5.6
it
6.0 A
6.0
It
6.0 -It
NA
NA
NA
NA
6.0 A
6.0
it
6.0 A
6.0 A
6.0
it
NA
NA
5.6
A
28.
A
19.
A
23.
It
5.6
it
14.
it
19.
It
NA
24. A
0.26
it
0.066
it
0.066 A
2.4 A
2.4 A
3.4 -A
3.4
-A
3.4 A
3.4 A
3.4-h
3-.4
It
3-.~4 it
3.4—A
3-. 4—A
NA
1(037
NA
DiDulfoton
Tolucne
1(040
NA
Phoratc
1(041
NA
Touaphcrio
275
Naphthaleflo
a Crcao1-
Phenanthrenc
Phenol
PyrCne
1(036
NA
fliaulfoton
1(038
NA
Phorate
1(042
NA
1(043
NA
1,2, 4,5
Tctrachloroben~enc
o—Diohloroboncenc
p—fl I
~
1,2,4 Trichiorobencenc
2, 4—Dichiorophenol
2,6 Dichlorophcno
2,4,5 Triohlorophenol
2,4, 6—Trichlorophenol
letraunLoropncnoio
lotal)
Tetrachloroethcnc
Hcxaohlorodibenco-p-
dioxino
Hcxachlorodibenzofurpnp
t’entachiorcdibcn~op-
dioxins
Pcntachlorodibenco furans
Totrochlorodibcnzo p-
dioxino
Tctraohlorodibcnco -furano
91 20—3
95
48
7
35—01—8
108—95—2
129 00—0
298—04—4
298 04
4
-1-08
-
88—3
298—02—2
298 02—2
8001 35—1
95 94—3
9-S-SO-i
106—46—7
608 93
5
-120-82
1
-120-83—2
187—65
0
95—95
4
88—06—2
87
86
5
79
01
6
7430
92
1
71—43—2
50—32—8
117
81
7
218—01—9
-84~
74—2
100
41
4
86—73 7
91—20—3
8-5 01—8
108 95
2
120
00
0
108-88—3
57—12 5
7440
47
32
7-43
9—92—1
120
12
7
71
43
2
0.059
B
0.11
B
0.059
B
0.039
0.067
B
0.025
B
0.025
B
0.080
B
0.025
0.025
0.0095 B
0-.-0-55 B
0.088
B
0.090
B
0.055
B
0.-055
B
0.044
0.044
0.18
0.035
NA
0.089
0.056
0. 000063
0.00006-3
0.000063
0. 000063
0.-000063
0-.-000063
0.037
0.14
-B
0.061 B
0.28 B
0.059
B
0.057
B
0.057
B
0.059 B
0.059 B
0.059
B
0.039
B
0.067
B
0.080
B
0.32
B
0.028
It
0-.~
03-7
0.059
B
0.14 B
3.4
-It
NA
3-.~4 A
NA
8-.2
A
0.1
it
0.1 A
2-8.
A
0.1
It
0.1 A
2.6 A
4.-4--2t
4.4
it
4.4 A
4.4 A
4.4
it
0.38
A
0.34 A
8.2 A
7.6 A
0.68
A
1.0 A
1-.7 A
0.001
A
0.001
it
0.001 A
0.001 A
0.001 A
0.001
1t
NA
14.
A
12. A
7.3
It
15.
it
3.6
it
14.
it
NA
42.
it
3-4.
it
3-.-? A
36.
A
14. A
22. A
1.3
2~.
NA
NA
28.
It
14. A
1(046
~a~lc
it
Lead
1(048
~ab1c—A
Benccno
Bis(2 cthylhcxyl
phthalate
Chryoerto
Di-n-butylphthalato
Ethylbcnzcne
Fluorenc
Nap~thalene
Phcnanthrenc
Phenol
Pyrcnc
Tolueno
Xylene(a)
Cyanidcc~ (Total)
Chromium
(Total)
Lead
Anthraocne
Ben~cne
1(049
TableIt
276
Chryocnc
2,4
DLmcl
Ethylbcnzeno
Naphthaloflo
Phcnanthrcne
Phenol
Pyrenc
Tolueno
Xylcnc(a-)-
Cyanides
(Total)
Chromium (Total)
eyaniucu
(total-)-
Chromium
(Total-)
Bis (2 cthylhcxyl)
phthalato
Chryacno
Di-n-butyl phthalate
Ethylbcnzenc
Fluorone
Naphthalene
Phenanthrene
Phenol
Pyrene
Toluonc
Xylono (a)-
~yana~aco
(local)
Chromium
(Total)
Lead
Ben
cone
Bc-nco(a)pyrcnc
o—Creool
p-Crecol
2, 4 Dimethyiphenol
Ethylbcncerie
Naphthalone
Phenanthrene
Phenol
Toluene
Xylenca
Cyanides (Total~
Chromium (Total)
117 81—7
-3-6—150—8
75—15—0
2218—01
9
105 67
9
100—11—4
91-20-3
85 01
8
-1-08
95
2
12 9—00—0
108—88—3
56 12—5
7440—47—32
7439 02—1
50
32—8
108—95—2
5-7—12—5
3440 47—32
3-430 29—1
208—96—8
120
12
7
71
43—2-
117—81—7
1-17—31—7
75—15—0
2-218-01—9
105—67—9
-1-00—41
4
86
73—7
91—20—3
85-01—B
108 95
2
-1-2-0
00
0
1-08—88—3
-6-3-
12
5
7440—47
32
7439—29—-I
7
1—43—2
50 32—B
95—48—7
106—14
—&
105—67—9
100
41
4
91—20—3
85—01—8
108
95
2
1-08—88
3
56—12—S
7440-47 32
7430 92—1
71—43—2
50
32
8
91 20—3
0.061
B
0.28 B
0.014
B
0.059
B
0.036 B
0.057
B
0.059
8
0.059
B
0.039
B
0.067
B
0.08
B
0.32
B
0.028 A
0.037-
0.061
B
0.039—B
0.028
A
0.037
p~p~g
B
0.059
B
0.14
B
0.059
B
0.061 B
0.28
B
0.059
B
0.057
B
0.057
B
0.059
B
0.059
B
0.059
B
0.039
B
0.067
B
0.08
-B
0.32 B
0.028 A
0.037
0.14
B
0.061
B
0.11
B
0.77
B
0.036 B
0.057
B
0-.-P-59
B
0.059
B
0.039
B
0.08 B
0.32 B
0.028 A
0.0-3-7-
0.17 B
0.035
B
0.028 B
12.
It
3-.-3
A
NA
15.
A
NA
44-.
A
42.
it
34.
it
3.6 A
36.
Ii
22.
it
1.8
It
NA
NA
1-2.
it
3.6
it
1.8
it
NA
NA
NA
23.
-A
14.
A
2-0.
it
12.
It
7.3 A
15.
A
3~-6—It
14.
A
NA
42.
It
34.
it
3.6
it
36.
Ft
14.
it
22. A
1.8
it
NA
NA
1-4.
it
12.
it
6.2 A
6.-2
it
NA
14. A
42.
A
34.
it
3.6
A
14. A
22.
it
1.8
It
NA
NA
0.071
It
3.6
It
3.4
it
Bie(2-ethylhcxyl)
phthalate
Carbon disulfido
1(050
Table—A Load
Phenol
Lead
1(051
Table
it Accnaphthcnc
Anthraoeno
Bcnzcnc
1(05-2
Table-It
1(0-6-0
NA
Load
Bonseno
277
1(069
TableD
Cadmium
A&D
Load
1(071
Table
A
Mercury
7440—43
9
7439—92—1
0.51
7439—fl 6
NA
NA
Phenol
(Total)
1(061
Table
it
1(062
Table
A
Cadmium
Chromium (Total)
Lead
Niche1
Chromium (Total)
Lead
Nickel
Carbon tetraohloridc
Chloroform
Hexachlorocthanc
Totrach1oroethene
1, 1, l—Triohlorocthanc
Bcnzenc
Aniline
0iphenylamine
0
1(0-73
NA
1(08-3
Table A
1(084
NA
1(085
NA
1(086
Table
it
Cum of Diphenylamine and
Diphcnylnitrooamine
Nitrobenscnc
Phenol
Cyclohexanonc
Nickel
Arsenic
Bcnzcne
Chlorobenzone
—~—r’
4
~..t,
103 95
2
57125
0.042
~9-
B
3.4 A
4-r2
7440—43—9
7440
47
32
7439 92—1
7440—02—0
1.61
0.32
0.51
0.44
NA
NA
NA
NA
7440 47—32
7439—92
1
7440—02—0
0.32
0.04
0.41
NA
NA
NA
0.030
NA
58—23—5
67—66—3
67 72—1
127—18
4
71—55—6
0.057
0.046
0.055
0.056
0.054
B
B
B
B
B
6.2 A
6.2
it
30.
Ft
6.2
A
6.2 A
71—43
2
62 53—3
22—39—4
86-30-6
0.14
0.81
0.52
0.40
NA
B
B
B
B
6.6 A
14.
A
NA
NA
14.
It
98—95—3
108—95—2
108 94—1
7440—02
0
0.068
0-.-0-39
0.36
0.47
B
14.
it
5.6 A
3-0.~ A
NA
7440-38—2
0.79
NA
71
43
2
108 90—7
95—50—1
541
73
1
106
46
7
120—82—1
95—94—3
608
93
5
118
74
1
12674—11—2
11104—28—2
11141—16
5
53460 21—9
12672—29—6
11097—69—1
11096 82—5
0.14
0.057
0.088
0.036
0.090
0.055
0.055
0.055
0.055
0.013
0.014
0.013
0.017
0.013
0.014
0.014
B
B
B
B
B
B
B
B
B
B
B
B
B
B
B
4.4 A
4.4 A
4.4
it
4.4
it
4.4
it
4.4
A
4.4 A
4.4 A
4.4 A
0.9
Ft
0.92 A
0.02 A
0.02 A
0.92 A
1.8
A
1.8 A
67—64—1
96-86—2
117—81-7
71363
85—68—7
108—94—1
95 50
1
84
66
2
0.28
0-~Pl0
0.28
S-r6
0.017
0.36
0.088
0-.-20
B
B
B
160.
it
9.7 A
28. A
2.6A
7.9 A
NA
6.0 A
28. A
Dichiorob-
1~n~cno
1,2,4,S-Totraahlorobon
Pcntaohlorobenzcna
Aroclor 1016
itroclor 1221
Aroclor 1232
Aroclor
124-2
Itroalor 1243
Aroalor 1254
Aroclor 1260
Iteetone
Itoctophenono
Bia(2 cthy1hex~
-Butvl alcohol
1phthalatc
1,2 Diohlorpbcn~eno
278
UlRlCtfl~i
pntnaiatc
Di n-butyl -phthalato
Di-n-ootyl phthalate
Ethyl
acetate
Ethylbontene
flethanol
KCtfl7i
~OODUtyi
J~OtOflO
Methyl ethyl kotone
Methylenc chloride
Naphthalono
Nitrobencono
Toluono
1,1,1 Trichlorocthanc
Trichioroethylenc
Xylcne(a)
(Total)
Cyanides ~Total-)-
Chromium (Total)
Lead
Itccnaphthalcne
Benzcne
Chrysenc
Fluorantheno
Indcno
(1,2,3—cd)
pyrenc
Naphthalcnc
Phcriant hrcnc
Toluonc
Xylenco
Lead
Phthalio anhydride
(measured as Phthalio
acid)
Phthalio anhydride
!mcaaurod
pa
Phthalia
1-31
11
3
8-4
7-4—-2
117—84—0
141-78—6
100
41
4
~7—56
1
108—10—I
78—93—3
75
09—2
98—95—3
108—88—3
71
55
6
79 01—6
57—12—S
7440
47
32
7430
92
1
208—96—8
71
43
2
318
01—9
206—44—0
193—39—5
01-20—3
85 01
8
4-08--88—3
7439
02
1
85—44—9
85—44—9
630—20—6
79—34—6
127
18—4
70 00 5
79-01—6
67—72 —1
76-01
7
630—20—6
79— 34—6
127
18
4
79-00
5
79—01—6
541
73
1
76
01
7
120—82—1
77
47
4
57
74
9
76—44—8
1024—57—3
acid)
1(08-7
Table
it
1(093
NA
1(094
NA
1(095
NA
1(0-96
NA
1(097
NA
0.047
B
0.057 B
0.017
B
0.34 B
0.057
B
5.6 B
0.14
0.28
0.089
B
0.059
B
0.068
B
0.080 B
0.054
B
0.054
B
0.32
B
4-7-9-
0.32
0.03
0.059
B
0.14
B
0.059
B
0.068
B
0.0055
B
0.059
3
0.059
B
0.08
B
0.32
B
0.037
0.069
0.069
0.057
0.057
0.056
0.054
0.054
0.055
0.055
0.057
0.057
0.056
0.054
0.054
0-,-036
0.-P55
0-.-0
55
O-.-057
B
0.0033
B
0.0012
B
0.016
B
28. A
28.
Ft
28.
it
33. A
6.0 A
NA
33.
it
36. A
33. A
3.1
Ii
14. A
28. A
5.6 A
5.6 A
28.
it
4-7-5-
NA
NA
0.071 A
3.4 A
3.4
ii
3.4
it
3.4
A
3.4 A
0.65
A
0.07
it
NA
28. A
28. A
5.6 A
5.6 A
6.0 A
6.0 A
5.6 A
28. A
5.6 A
6.6
it
5.6
it
6.0
It
6.0 A
5.6
It
5.6 A
5.6 A
19. A
~r4
0.26 A
0.066 A
0.066 A
1, 1,2
,
2—Tetrachioroethanc
Tctrachloroethcnc
1,1,2 Triohioroethanc
Trichlorocthylcne
Hexachloroothanc
Pentachioroethanc
1
F
1~1~
2—Tetrpahloroethane
1,1,2,2—Tetraohloroethane
Tetrachioroethene
1,1,2-Trichloroethanc
Triohloroethcne (Tn—
chloroothyleno)
1, 3-Dichlorobenccnc
Pcntachloroethane
1,2, 4-Trichlorobcnzcnc
Eicxachlorocyclopcntadiene
Chlordano
Hoptaohlor
1(098
NA
Toxaphcne
8001
35
1
0.0005
B
2.6
It
•
Nitrobcnzcnc
Phenol
Cyanidca
(Total)
6-2—53—3
71—43—2
51 28—5
9-8—CS
3
108 96—2
57—12—S
1.0 A
0.001
A
0.001
it
0.001 A
0.001 A
0.001 A
0.001
it
4.5
Ft
0.15
it
0.61
it
0.073
it
-1-.-4 A
1.0
-it
0.001 A
0.001 A
0.001 A
0.001 A
0.001
It
0.001
it
5.6 A
6.0
Ft
5.6 A
5.6
It
5.6 A
1.8 A
1(106
Tab-lee
A-& B
Mercury
3-439—97—6
0.030
1(099
NA
279
lj
u~cnioropncnoxyacctic
acid
Hoxaohlorodibcnco-p-
dioxino
HexachlorodibenEafuranri
Pontachlorodibenzo p-
dioxine
Pontaahlorodibenaofurano
~‘ctrach1-orodibcnio-p
dioxinc
Tctraohlorodibcncofurans
1(100
Table-h Cadmium
1(10-I
NA
1(102
Table
It
1(103
NA
94
75
7
7440-43—9
7440—47
32
7439—92—1
3440 38
2
74 40—43—9
-3-439—92—i
7439
97
6
7440—3 8—~
3-440
43
9
7439
92
1
7439—97—6
6-2—53
3
71
43—2-
51-28—6-
98-95—3
108 95—2
enromium
(~IotaL)
Load
o Nitroaniline
Arsenic
Cadmium
Lead
Mercury
o
Nitrophcnol
Arsenic
Cadmium
Lead
Mercury
Aniline
Bcnzcne
2. 4-Dinitrophonol
4-~6
0.32
0.51
NA
NA
NA
0.27
it
0.79
0.24
0.17
0.08-2
14.
A
NA
NA
NA
NA
0.028 A
0.79
0.24
0.17
0.082
13. A
NA
NA
NA
NA
4.5
A
0.15 A
0.61 A
0.073
it
1.4
A
5--~-6
6.0
it
5.6 A
5~.6 A
5--.-6-ii
Nitrobenzcnc
Phenol
1(104
NA
Aniline
Bencene
~1
1(10-5
NA
Bcnccne
~,
~~i;~i;;;jcno1
2,4,6—Triohlorophcnol
~
~
1
Phenol
71 43—2
0.14
4.4 A
-1-0-8—90—7
0.057
4.4 A
95-50-1
0.085
4.4 A
1-06 46
7
0.09-0
4.4
it
0-5 05 4
0.18
4.4 A
88-06—2
0.035
4.4
It
95—67—8
0.04-4
4.4
it
108 95
2
0.03-9
4.4
it
1(1-15
Table
It
Nickcl
1(111
NA
1(117
NA
2,6
Dthitrotoluone
Ethylene dibromido
Moth’~rl
hrornirh-’
7440
02
0
1-21—14—2
606—20 2
-1-06—93—4
74—83—9
6-7
66
3
0.47
0.32
0.55
0.028
0.11
0.046
NA
NA
140.
it
28. A
15. A
15. A
5.6
Ft
—--4
Chloroform
280
, mm..
—
n
-
~un
ml
-r
,-emt,n
Gemmoro
Lal
W-aate
Ghemica1-
Code
Name
flegulated
Bee
Hacardouc
Also
Ce-natituoflt
GAS
No.
for
Regulated
Hat
ardott~
Conatituont
Cenccntra
tion (mg/b)-
W-aatowater-G
Concentra-
tion
(mg/L)
Nonwaote—
~atero
P004
Aldri-n
NA
Aldnin
309
P0—2-
0.21 B
0.066 A
POlO
Arsenic acid Table
It
Arsenic
P0-li
Aroenle
pent
OX
ide
P012
Araeni—e
~rioxid.e
P013
Barium
eyanide
2020
2-aoa-Butyl- NA
4,6—dinitro
phenol
-(-Difl000b)-
P02-I
Calcium
eyanido
20-22-
Carbon di
eu-i-f ide
P024
p Chlor-e—
at9ri
l~fle
202-9
Copper
eyanide
P0-30
Cyanidee
-(-aolubl-e
e-alto
and
eewp1cxoD~
Tab-ic
it Arsenic
Table
it Arsenic
Table A
Cyanidec
(Total-)-
Cyanidec
(Amenable-)-
3440—38—2-
0.79
7440—38—2-
2—oco—Butyl—
8-8—85—7
4,6 dinitro
phenol
(Dinocob)-
NA
Cyanidcc
(Total)
Cyanidea
-~Itmenable)-
Table B
Carbon di-
o-ulfide
NA
p Chloro—
aniline
NA
Cyanidos
(Total)
Cyanidcc
(Amenable)
NA
Cyanidcs
(Total)
Cyanidcc
(Amenable)
NA
1(118
NA
1(13-I
NA
1(1-32-
NA
1(136
NA
Ethylene dibromide
Methyl bromide
Chloroform
Methyl bromide
Methyl bromide
~Whv1~nc dibromide
bromide
Hcthyl
Chloroform
106 93—4
74 83 9
67-66—3
0-.-028
0.11
0.046
15.
A
15.
it
-6-.-~-A
74
83
9
0.11
1-5.
A
3-4—83—9
0.-I-I
15.
A
1-06
03
3-4—83—9
67—66—3
4
0.028
0.11
0.046
1-5.
It
15. A
5.6
it
7440
38—2
5-7— 12—5-
57
12
5
NA
0.79
NA
110.
0.066
2.5-A
1-1-0.
0~4
0-.-0-1
4
NA
0.46
16.
it
-l 10-,-
0,4
5-7
12
5
57—12—S
75
15
0
406
47
8
?-7
12
5
6-7
12
5
6-7
12
5
281
P036
Dichloro—
Table A
Ztr~enic
7440 38—2
0.79
NA
phenylaroine
2037
Dieldrin
NA
Dicldrin
60 67—1
0.017
B
0.13 A
P038
Diethyl—
Table A Arsenic
7440 38-2
0.79
NA
arcinc
2039
Dieulfoton
NA
Dioulfoton
298—04
4
0.017
0.1 A
204-7
4,6—Dinitro—NA
4,6—Dinitro—
534—52—4
0.28 B
160.
A
o—orecol
o—cresol
2048
2,4—Dinitro
NA
2,4 Dinitro
51 28-5
0.12
B
160. A
phenol
phenol
P050
Endosulfan
NA
Endooulfan
I
930-98 8
0.023
B
0.066 A
Endoculfan
II
33213
6
5
0.029
B
0.13 A
Endosulfan
1031—07--S
0.029
B
0.13 A
sulfate
P06-I
Endrin
NA
Endrin
32 20 -8
0.0028- 3
013
A
Endrin
7421—93—4
0.025 B
0.13 A
aldchydc
2056
Fluoride
Table B
Fluoride
18694 48 8
NA
P059
Heptaohlor
NA
Hcptaohlor
76-44-8
0.0012 B
0.066 A
Hcptachlor
1024
57—3
0.016
B
0.066 A
epoxide
206-0
Isodrin
NA
Icodrin
465—73—6
0.021
B
0.066 A
P063
Hydrogen
NA
Cyanides
57
12-5
4-~9
110.
cyanide
-(Total)
Cyanidos
57—12—5
0.10
(Amenable)
#065
Mercury
Tables
Mercury
7439—97—6
0.030
NA
fulminate
A ~ D
2071
Methyl
NA
Methyl
208-OP 0
0.025
0.1 A
parathion
parathion
2073
Nickel
Table
It
Nickel
7440 02—0
0.32
NA
carbony-1
2074
Nickel
Table A
Cyanidca
57-12—5
4.-~-9-
110.
cyanide
(Total)
Cyani-dea
57
12-6-
0.10
(Amcn~b1c)
Nickel
7440-02—0
0.44
NA
2077
p Nitro
NA
p Nitro-
100 01
6
0.028 3
28. A
aniline
aniline
2082
N Nitrosodi
Table D
N Nitrosodi
62
75
9
0.40 B
NA
methylamine
mcthylaminc
2089
Parathion
NA
Parathion
56 33-2
0.025
0.1 A
282
2092
Phenylmcr—
Tables
Mercury
7439—97-6
0.030
NA
eury acetate A & B
2094
Phorato
NA
Phorato
299—02-2
0.025
0.1
It
2097
~-amphur
NA
Famphur
52
85
7
0.025
0.1 A
P09-B
Potassium
NA
Cyanidea
57—12—5
l-~4
110.
cyanide
(Total)
Cyanides
57—12—5
0.10
9,-I
(Amenable)
2099
Potaaaiuxn
Table
A
Cyanides
57
1-2
S
110.
silver
(Total)
-eyanido
Cyanidcc
67-12—S
0.-I
-(Amenable-)
Cilver
7440—22-4
0.29
NA
P10-i
Ethyl oyan—
NA
Ethyl cyanide
107-12—0
0.24
B
360. A
ide (Pro—
(Propane
panonitrile)
nitrile)
2103
Belenourca
Table A
Cclenium
7782-49-2
1.0
B
NA
21-04
&ilver
Table A
Cyanides
57 12-5
4.--9
110-.
eyanide
-(-Total)
Cyanidcs
57-12—5
0.10
Amenablc)
Cilvcr
7440
22
4
0.29
NA
2106
SodIum
NA
Cyanides
57—12—5
4-~-9-
110.
-cyanide
(Total)
Cyanidec
5-7
12
5
0.10
(Amenable)
2110
Tetracthyl
Tables
Lead
7439—92—1
0.040
NA
lead
A&D
2113
Thallic
Table D
Thallium
7440—28—0
0.14
B
NA
oxide
2-1-14
Thallium
Table A
Belenium
7782-49-2
NA
solenito
2115
Thallium(I)
Table D
Thallium
7440 28—0
0.14
B
NA
sulfate
2119
Ammonia
Table
D
Vanadium
7440-62
2
28-.
B
NA
vanadat-e
2120
Vanadium
Table D
Vanadium
7440—62-—-2-
28.
B
NA
pentoxide
2121
Zinc cyanide NA
Cyanidcc
57—12—5
110.
(Total)
Cyanidec
57
12
5
0.10
(Amenable)
2123
Texaphone
NA
Toxaphcno
8001—35—1
0.0096
2
1.3 A
U002
Acetone
NA
Acetone
67 64
1
O.-28
160. A
283
U003
Aectonitrile Table B
itcetonitrile
75
05
8-
0.17
0.17
U004
AectophononeNA
Aoetophcnonc
98
8-6-2
0.010 A
9.7
It
U005
2 Acetyla—
NA
2—ltcetylami—
53-
96
3
0.059
B
140-. A
minofluorcnc
nofluorenc
U009
Acrylo—
NA
Acrylonitrilc
107—13-1
0.24
Ft
84.
A
nitrilc
U012
itniline
NA
An-iline
62—53—3
0.81
14.
A
UO13
B-cn~(a)-—
NA
Bcn~(a)
56-
55
3
0.059
B
8.2 A
anthraocno
anthracone
UP-19
Bcnscnc
NA
Bon~cnc
31-4-3-2
0.14 B
36.
It
U022
Ben~o(a)—
NA
Benzo(a)
50
32
8
0.061
8
8.2 A
pyrcnc
pyronc
U024
Bi~(2chlor
NA
Bis(2—chloro—
111—91
1
0.036
7.2 A
octhoxy)met-
cthoxy
)
meth-
hanc
ane
u025
Bio(2—
NA
Bio(2 chloro—
111—44—4
0.033
7.2 A
ehioroothyl)
ethyl) ether
other
-
U027
B-La-(2
chlor-NA
Bio(2
chioro-
39638
32
9
0.055
7.2
A
oieopropyl)
iaopropyl)
ether
ether
U-028
Bis(2 ethyl—NA
Bis(2 ethyl-
117—81—7
0.28 A
28. A
hoxyl)—
hexyl)—
phthalatc
phthalato
U029
BromomethancNA
Bromomethane
74
63
9
0.11
A
15.
A
(Methyl
(Methyl
bromide)-
bromide)
t3030
4 Bromo-
NA
4 Bromophenyl
101
55
3
0.055 A
15.
A
phenyl
phcnyl ether
phonyl
ether
U031
n Butyl
NA
n Butyl
71-36-3
2.6 A
alcohol
alcohol
tJO32
Calcium
Table A
Chromium
7440-47-32
0.32
NA
-chromatc
(Total)-
tJO36
Chlordano
NA
Chlordanc
57—74—9
0.00033
0.13 A
-(-alpha
and
(alpha and
g
gamma-)
gamma)
U037
Chioro—
NA
Ch1orobcn~cnc 108—90-7
0.057 B
5.7
it
bontone
U-038
0-hioro—
Table
B
Chioro
510 15
6
0.10
8
NA
bcn~ilato
ben~i1ato
U039
p Chloro m-
NA
p Chloro-m
59 50
7
0.018
B
14.
It
crecol
orecol
284
U043
Vinyl
chloride
U044
Chloroform
U045
Ohloromcth-
ano
(Methyl
chloride-)
U047
2-Chloro
naphthalene
U048
2-Chloro-
phenol
Chryoeno
Creosote
13063
Dibon~o(a,
NA
h) anthrace~e
U066
1,2—Dibromo—
NA
3-ohioro—
propane
tJO67
1,2-Dibromo—
NA
eth-ano
(Ethylene
dibromidc)-
11068
Dibromocth-
NA
a~e
NA
o,p’-DDD
p,p’-DDD
NA
o,p’-DDT
p, p’ -DDT
o,p’-DDD
p,p’-DDD
e,p’-DDE
PiP’ DDE
Dibenco(a,h)—
anthracene
1, 2—Dibromo—
3—oh
loro-
propane
1, 2—Dibromo—
ethano
-(Ethylene di—
bromide)
0.059
B
0.031
0.18
0.031
0.028
0.028
0.032
0.037
0.11 B
8.2
it
1.5 A
7.4 A
1.5
A
28.
It
33. A
NA
NA
5.6 A
75
01
4
0.27
B
33.
A
67—66—3
0.046 B
5.6 A
74
8-7-3
0.19
B
33.
It
U05p
UOS 1
91
58
7
0.055
B
5.6
A
95
57
8
0.044 B
NA
Vinyl
chloride
NA
Ohioroform
NA
Chloromcthanc
(Methyl chl-
oride)
NA
2-Chlprc
naphthaleno
NA
2 Ohloro--
phenol
NA
Chrycei~o
Table A Naphthalene
Pcntaohlore
—
phenol
Phcnanthrcne
P1yrenc
Tolucnc
Xylcncc
(Total)
Lead
NA
o-Crcsol
Crcsolc
(m—
and p-iso-
mer8
Cvolohcxanone
5.7 A
218—01—9
91 20
3
87—86—5
85
01—8
129-00—0
102—88—3
7439—92
1
95—48—7
U052
Creeds
(Crccylic
acid)
1105-7
Cyclohexan-
Table
B
U060 D~
U061
~
0.77 B
10-8—94—1
0.36
53
19
0
72—54—8
789—02—6
50
29
3
53-19-—P
72—54—8
3424 62—6
72
55
9
53—70—3
0.023 B
0.023 B
0.0039
B
0.0039
B
0.023 B
0.023 B
0.031
B
0.031
B
0.055-
R
3.2 A
NA
0.08-7 A
0.087
A
0.083
It
0.087 A
0.087 A
0.087 A
0.087 A
0.087 A
8.2 A
15.
A
15.
A
96—12—8
0.11 B
106—93—4
P.028
B
74 —95—3
0.11 B
15.
A
Di-n butyl
NA
phthalate
o-Diohloro—
NA
bcnEcnc
zn—Diohlpro-
NA
bcnseno
p Dichia-ro
NA
bcn~enc
Dichlore
NA
difluoro-
methane
1,1 Di
NA
chlorocthanc
1,2—Di—
Nit
chioroethanc
1,1 Dichior—NA
octhylcnc
1,2
Dichlor-NA
octhylcne
Methyl-enc
Nit
ohloEi-do
2,4 Di—
NA
chlorophcnol
2,6—Dichior— NA
ophenol
1,2—Dichior— Nit
opropan-c
1,3 Dichlor—NA
opropone
Diothyl
NA
phthalatc
p—Dimethyl—
Table
D
aminoa~oben—
~ene
2,4—Di—
Nit
methylphcnol
Dimethyl
NA
phthalato
2,4
Dinitro
NA
toluene
1,1 Dichlc
~—
75-34
3
ethanc
1,2-Diohlo~u—
ethanc
1, 1-Diohloro—
,.,
~--
-~
ethylene
trenu—1,2
Dir—
156—60—5
chloroethyl—
e~e
Methylcne
chloride
2, 4-Dichiutu
phenol
2,6—Dichioro
phenol
1,2-Dichloro—
78-’--87—5
propane
cia-i,3 Dich—
Ie~opropylen
t-Ee
~
e1~
Bicthyl
phthalatc
p—Bimothy1—
aminoazo-
benzenc
2, 4—Di
phenol
Dimethyl
phthalato
2, 4—Dinitro—
tolueno
se—
oroor
84—66—2
60—11—7
methyl—
105—67-9
285
Di n butyl
plithalatc
o-Dichloro-
bcnccne
rn—Biohloro—
ben~enc
p Dichioro
bcnzeno
Bichlorodi
84
74
2
95—50—1
541—73—i
104 46
7
75
71
8
107—06—2
U069
UP70
11071
U072
U075
U076
U07 7
tJO7G
11079
U080
U0e-i
U082
U083
U084
U088
U093
Ulol
Ui02
Ui 0-6-
75 08
2
12-0—83—2
7~•~
_f\
0.057
it
0.088
B
0.03-6
0.090 B
0.23
B
0.059
B
0.21 B
0.025
B
0.054
B
0.089
B
0.044
B
0.044
B
0.85
B
0.036
B
0.036
B
0.13
a
0.036
B
0.047
0.3-2
B
28.
A
6.2 A
6.2
Ft
6.2 A
7.2 A
7.2
It
7.2 A
33. A
33. A
33.
A
14. A
14.
A
18..
A
18.
A
18. A
28.
2~
Nit
14.
it
28.
A
140.
A
10061
01
5
,
~
I
131—11—3
121
14—2
286
U130
Hoxaahloro-
cyc lopertta
dienc
11131
Hoxaohloro—
ethane
U134
Hydrogen
fluoride
U136
Cacodylic
acid
11137
I~ndcno—
(-1,2,3 c,d)
pyre no
11138
lodomethanc
U140
t-sobutyl
alcohol
11141
loosafrolc
2,6
Dinitro-
6-0-6-20-2
tolucnc
Di—rt—ootyl
117—84—P
phthalatc
1,4—Dioxane
123—91—1
Di-n
propyl-
621
64-7
nitrosoaminc
Ethyl acetate
141—78—6
U106
2,6-Dinitr-o-Nh
toluenc
Ul07
Di—n—ooty-1
Nit
phtha late
11108
1,4-Dioxano
WA
Ulil
Di
n-propyl-NA
nitrosoamino
11112
Ethyl
NA
acet-abo
U117
Ethyl ethor
NA
11118
Ethyl moth
Nit
acrylat-e
111-2-0
Fluorantherro
Nit
Ul21
Trichioro—
Nit
monofluoro—
methane
11127
Hax-achloro
NA
bcn~cnc
U128
Hcxachloro
Nit
butadienc
U129
Lindano
NA
0.55
B
28.
A
0.017
28.
A
0.12
B
170.
it
0.40
B
14.
It
0.34- B
33.
It
0.12
B
160. A
0.14
B
160.
A
0.068
B
8.2
it
0.020
B
33.
A
0.055
8
37.
A
0.055
B
28.
A
60—29—7
97
63—2
206—44—0
75-
69
4
118 74—1
87 68 3
319 84—6
319
8-5—7
319 86 8
58 89 0
77—47—7
67—72—1
Ethyl ether
Ethyl methac
rylate
Fluoranthcnc
Trichioro
monofluoro—
methane
He~achloro-
bcn~enc
Hexachioro-
butadiene
alpha-BHC
beta
BHC
Dclta-BHC
gamma-
BUC
(Lindanc)
NA
I-Icxaohloro—
cyclopcnta—
dicne
WA
Hcxachlorp—
cthane
Table
D
Fluoride
Table
It
Arsenic
0.00014
0.00014
B
0.023
B
0.0017
B
0.66 A
0.66 A
0.66
it
0.66 A
16964-48—8
7440
38—2
0.79
0.057
B
3.6
A
0.055
B
28.
it
NA
NA
0.0055 8
8.2 A
NA
Thdeno(1,2,3
193
39—5
e,d)pyrenc
NA
Iodomcthane
Nit
Icobutyl
alcohol
Nit
Iposafrole
74 88 4
78—8-3—1
0.19
B
120
58—1
0.08-1
65. A
170. A
2.6 A
287
U142
~eponc
NA
Keporic
143-50—8
0.0011
0.13 A
U144
Load acetate Table A
Lead
7439-92—i
0.040
Nit
11145
Lead
Table A
Lead
7439 92
1
0.040
NA
phosphate
11146
Load pub—
Table A
Lead
7439-92—i
0.040
NA
acetate
11151
Mercury
Tables
Mercury
7439—97—6
0.030
Nit
it&D
U152
1-tethacrylo-
NA
Hcthacryloni—
126 98—7
0.24
B
84. A
nitrilc
trile
U154
Methanol
NA
Methanol
67
56
1
&~~6
NA
11155
Hetha—
Nit
Mcthapyrilcnc
91-80-5
0.081
1.5
it
pyrilonc
U15~ 3 Methyl—
NA
3 Hcthylchol-
56
49
5
0.0055—B
15.
A
cholanthronc
anthrenc
17158
4-,4’
Methyl-Nit
Mcthylcncbio—
101 14-4
0.50
B
35. A
cncbic(2—
(2 chioro
ohloro—
aniline)
aniline)
11159
Methyl ethyi NA
Methyl ethyl
78 93
3
0.28
36. A
kctonc
ketone
U16l
Methyl iso
NA
Methyl
iso
108-10-1
0.14
33.
A
butyl
kctonc
butyl kctonc
U162
Methyl moth—Nit
Methyl meth—
80-62-6
0.14
160.
it
acrylate
acrylate
11165
Naphthalonc
NA
Naphthalcnc
91—20-3
0.06-9 B
3.1 A
Ui68
2
Naphthyl—
Table
D
2
Naphthyl
9-1
59
8
0.52
B
NA
amine
amine
U169
Nitrobonceno-Nit
Nitrobeneenc
98-95-3
0.068—B
14. A
Ui70
4 Nitro—
NA
4 Nitrophcno~. 100—02—7
0.12 B
29. A
phenol
11172
II tiitropodi—NA
t~Nitropodi-
9-24 16
3
0.40 B
17.
A
n
butylamine
n-butylaminc
U174
N-t7itropodi-NA
N—Nitrosod-i—
55—18—5
0.40
B
28.
it
ethylamine
ethylaminc
U179
N—Nitroao—
NA
N—Nitroso—
100—75—4
0.013
B
3-5.
A
piporidine
pipcridinc
U180
N Nitroc3o
NA
N Nitroso-
930-55-2
0.013 B
35. A
pyrrolidinc
pyrrolidine
11181
5--Nitro
p
NA
S
Nitro p
99 55
8-
0.32
B
28. A
teluidinc
toluidine
288
U183
Pcntachloro-NA
Pontachloro
608-93-5
0.055
B
37.
It
~enzcnc
bentenc
11185
Pcntaohioro—NA
Pentaohloro-
82—68—8
0.055
B
4.8 A
nitroben~eae
nitrobenzcnc
11187
t’hcnaactin
NA
Phcnacctin
62—44—2
0.081
16. A
11188
Phenol.
NA
Phenol
108-95-2
0.039
6.2 A
11190
Phthalio
NA
Phthalic
85—44—9
0.069
28. A
anhydrids
anhydrido
(measured
as
(measured as
Phthalic
Phthalic
acid)-
acid)-
U192
Pronamide
NA
Pronamidc
2-3-950
58-5
0.093
i.S
A
tJi96
Pyridinc
NA
Pyridinc
110-86-i
0.014
B
16.
A
U203
Cafrole
NA
Safrole
94-59
7
0.081
22. A
U204
gclcnium
Table
A
Colonium
7782—49—2
NA
dioxide
U205
Cclcnium
Table
A
Belenium
7782
49-2
NA
sulfide
U207
1,2,4,5—
NA
1,2,4,5—
95 94
3
0.055
B
19.
A
Tetrachioro—
Tctrachloro—
bensene
bensene
U20-8
1,1,1,2—
NA
1,1,1,2—
630
20-6
0.057
42.
A
Tctrachloro—
Tctrachloro-
othanc
ethane
U209
1,1,2,2—
NA
1,1,2,2—
70
34
5
0.057
B
42. A
Tetrachloro
Tctrachloro
ethanc
ethanc
U21P
Tetrachloro—NA
Tetrachioro—
127-18-4
0.056 B
5.6
A
ethylene
ethylene
U211
Carbon tot-
NA
Carbon tctra—
56—23—S
0.057
B
5.6 A
~-ach1oridc
chloi~-i4e
U214
Ta-llium(I)
Table D
Thallium
7440—28-p
0.14 B
NA
-
aoctat-e
11215
Thallium(I)
Table D
Thallium
7440-28—0
0.14 B
NA
carbonate
11216
Thallium(I)
Table
D
Thallium
7440-28
0
0.14
B
NA
chloride
U217
Thallium(I)
Table D
Thallium
7440—28—0
0.14 B
NA
nitrate
11220
Tolucno
NA
Tolucnc
108—38-3
0.080
B
2-8-.
A
289
11-225
Tribromo—
NA
Tribromo-
75-25-2
0.63
B
15. A
mcthano
methane
(Bromoform)
(Bromoform)
13226
1,1,1
Tn—
NA
1,1,1-Tn—
71—55—6
0.054
B
5.6 A
chloroethanc
chlorocthanc
U227
i,1,2—Tri-—
NA
1,1,2—Tn—
79—00—5
0.051
B
5.6 A
chlorocthane
chloroethanc
U228
Tniohioro—
Nit
Trichloro—
79—01—6
0.054
B
5.6 A
-
ethylene
ethylene
11235
tnio—(2,3—
NA
tnis
(2,3 Di—
126 72—7
0.025
0.10 A
Dibrornoprop-
uromopropy.
)
—
yl)—
phosphate
phosphate
13-239
Xylcnc-o
Nit
Xylcne
0.32
8
28.
Zt
11240
2-,4-Dichlor
NA
2,4 Dicn~oro- 94-75-7
0.72
10.
A
o-phenoxya—
phcnoxvaectic
petic acid
acid
11-243
Hcxachloro-
NA
Hexachloro
1888
71
7
0.035
B
~ropenc
propcne
11247
4othoxychlor
Nit
1icthoxychlor
72—43—5
0.25 B
0.18
It
Treatment etanaar~s
organic
constituent
were cotaeii.anca eacoc
upon incineration in units operated in acoordanco with the technical
~oquircmcntc of
35
Ill.
Adm.
Code 724.Eubpart
Q
or 725.Subpart
Q,
or
based upon combuetion
in fuel oubcititution units operating in accor-
dance with applicable technical requirements.
it facility may certify
oomplianoe with these treatment standards according to provisions
in
Section 728.107.
C
Ito analysed using SW-846 Method 9010 or 9012
sample aizot 10g~
distillation
one nour anu riitccn minutes.
Reserved.
NA
Not
itr~o.LicpuJ.c.
(Source:
Amended at
19
Ill. Reg.
________,
effective
_______________
Section 728.Table C
Technology Codes and Description of Technology—Based
Standards
Technology
code
Description of technology-based standard
ADGAS
Venting of compressed gases
into an absorbing or reacting media
(i.e.,
solid or liquid)——venting can be accomplished through physical release
utilizing va1t*~es~
or piping physical penetration of the container;
and/or penetration through detonation.
AMLGM Amalgamation of liquid, elemental mercury contaminated with radioactive
materials utilizing inorganic reagents such as copper,
zinc,
nickel,
gold,
and sulfur that result in a nonliquid, semi—solid amalgam and
290
thereby reducing potential emissions of elemental mercury vapors to the
air.
BIODG Biodegradation of organica or non-metallic inorganics
(i.e., degradable
inorganics that contain the elements of phosphorus,
nitrogen,
and
sulfur)
in units operated under either aerobic or anaerobic conditions
such that a surrogate compound or indicator parameter has been substan-
tially reduced in concentration in the residuals
(e.g., ~otal
QQrganic
Ocarbon
(T0C~can often be used as
an indicator parameter for the
biodegradation of many organic constituents that cannot be directly
analyzed in wastewater residues).
CARBN Carbon adsorption
(granulated or powdered)
of non—metallic inorganics,
organo—metallics,
and/or organic constituents, operated ~uch~
that a
surrogate compound or indicator parameter has not undergone breakthrough
(e.g., c~otalOQrganic Gçarbon
(TOC’)
can often be used as an indicator
parameter for the adsorption
of many organic constituents that cannot be
directly analyzed in wastewater residues).
Breakthrough occurs when the
carbon has become saturated with the constituent
(or indicator
parameter) and substantial change
in adsorption rate associated with
that constituent occurs.
CROXO Chemical or electrolytic oxidation utilizing the following oxidation
reagents
(or waste reagents)
or combinations or reagents:
1)
N~ypoch1orite (e.g.~.bleach);
2)
chlorine;
3)
chlorine dioxide;
4)
ozone or
1W
(ultraviolet light) assisted ozone;
5)
peroxides;
6)
persulfates;
7)
perchlorates;
8)
permangantes; and/or
9)
other oxidizing reagents of equivalent efficiency,
performed in
units operated such~that a surrogate compound on indicator
parameter has been substantially reduced in concentration in the
residuals
(e.g., ~otal
Qorganic ~arbon
(TOC)
can often be used
as an indicator parameter for the oxidation of many organic
constituents
that cannot be directly analyzed in wastewater
residues).
Chemical oxidation specifically includes what is
commonly referred to as alkaline chlorination.
CHRED Chemical reduction utilizing the following reducing reagents
(or waste
reagents)
or combinations of reagents:
1)
S~u1furdioxide;
2)
sodium,
potassium,
or alkali salts of
sulfites,
bisulfites,
metabisulfites,
and polyethylene glycols
(e.g., NaPEG and KPEG);
3)
sodium
hydrosulfide;
4)
ferrous salts;
and/or
291
5)
other reducing reagents of equivalent efficiency, performed in
units operated such that a surrogate compound or indicator
parameter has been substantially reduced in concentration in the
residuals
(e.g., ~otal
QQrganic l4~alogens(T0X~can often be used
as an indicator parameter for the reduction of many halogenated
organic constituents that cannot be directly analyzed in
wastewater residues).
Chemical reduction is commonly used for the
reduction of hexavalent chromium to the trivalent state.
CMBST Combustion in
incinerators, boilers,
or industrial furnaces operated in
accordance with the applicable requirements of 35
Ill.
14dm.
Code
724.Subpart 0 or 35
Ill.
14dm.
Code 726.Subpart H.
DEACT Deactivation to remove the hazardous characteristics of
a waste due to
its ignitability,
corrosivity, and/or reactivity.
FSUBS ~‘uelsubstitution in units operated in accordance with applicable
technical operating requirements.
HLVIT Vitrification of high level mixed radioactive wastes in units
in
compliance with all applicable radioactive protection requirements under
control of the federal Nuclear Regulatory Commission.
IMERC Incineration of wastes containing organics and mercury in units operated
in accordance with the technical operating requirements of 35
Ill.
14dm.
Code 724.Subpart 0 or 725.Subpart 0.
All wastewater and nonwastewater
residues derived from this process must then comply with the
corresponding treatment standards per waste code with consideration of
any applicable
subcategories (e.g., ~jigh or ~jow M~ercury&~ub-
categories).
INCIN Incineration in units operated in accordance with the technical
operating requirements of
35 Ill.
14dm.
Code 724.Subpart 0 or 725.Subpart
0.
LLEXT Liquid-liquid extraction (often referred to as solvent extraction)
of
organics from liquid wastes into an
immiscible solvent for which the
hazardous constituents have
a greater solvent affinity, resulting in an
extract high in organics that must undergo either incineration, reuse as
a fuel,
or other recovery.,L or reuse and
a raffinate
(extracted liquid
waste) proportionately low in organics that must undergo further
treatment as specified in the standard.
MACRO Macroencapsulation with surface coating materials such
as polymeric
organics
(e.g.4
resins and plastics)
or with a jacket of
inert inorganic
materials
to
substantially
reduce
surface
exposure
to
potential
leaching
media.
Macroencapsulation specifically does not include any material
that would be classified as
a tank or container according to
35 Ill.
14dm.
Code 720.110.
NEUTR Neutralization with the following reagents
(or waste reagents)
or
combinations of reagents:
1)
A~cids;
2)
bases;
or
3)
water (including wastewaters)
resulting in a pH greater than 2 but
less than 12.5 as measured in the aqueous residuals.
NLDBR No land disposal based on recycling.
292
PRECP Chemical precipitation of metals and other inorganics as insoluble
precipitates of oxides,
hydroxides,
carbonates,
sulfides,
sulfates,
chlorides,
fluorides,
or phosphates.
The following reagents (or waste
reagents)
are typically used alone or in combination:
1)
~jime
(i.e.,
containing oxides and/or hydroxides of calcium and/or
magnesium;
2)
caustic
(i.e., sodium and/or potassium hydroxides;
3)
soda ash
(i.e.,
sodium carbonate);
4)
sodium sulfide;
5)
ferric sulfate or ferric chloride;
6)
alum; or
7)
sodium sulfate.
Additional flocculating,
coagulation,
or similar
reagents~or processes that enhance sludge dewatening
characteristicB are
not precluded from use.
RBERY
Thermal
recovery
of
8~ery1lium.
RCGAS Recovery/- or reuse of compressed gases including techniques such as
reprocessing of the gases for reuse1L or resale;
filtering,’- or adsorption
of impurities; remixing
for direct reuse or resale;
and use of the gas
as
a fuel source.
RCORR
Recovery of acids or bases utilizing one or more of the following
recovery technologies:
1)
Bdistillation
(i.e., thermal concentration);
2)
ion exchange;
3)
resin or solid adsorption;
4)
reverse osmosis;
and/or
5)
incineration for the recovery of acid——
Note:
this does not preclude the use of other physical phase
separation or concentration techniques such as decantation,
filtration
(including ultrafiltration),
and centrifugation, when
used in conjunction with the above listed recovery technologies.
RLEAD
Thermal recovery of lead in secondary lead smelters.
RMERC
Retorting
or
roasting
in
a
thermal
processing
unit capable of volatiliz-
ing mercury and subsequently condensing the volatilized mercury for
recovery.
The retorting or roasting unit
(or facility) must be subject
to
one
or
more
of
the
following:
a)
A N~ationa1E~missioris?~tandard for Nhazardous
itair ~pollutants
(NESRAP)
for
mercury
(40
CFR
61,
Subpart
E);
b)
A B~estA~vailab1eGçpntrol ~echnology
(BACT) or
a ~owest
A~chievab1eBemission Rrate
(LAER) standard for mercury imposed
pursuant to a ~prevention of 6~ignificantB~eterioration (PSD)
permit
(including 35
Ill.
14dm. Code 201 through 203);
or
293
c)
A state permit that establishes emission limitations
(within
meaning of Section 302
of the Clean Air Act)
for mercury, includ-
ing a permit issued pursuant to 35 Ill.
14dm.
Code 201.
All
wastewater and nonwastewater residues derived from this process
must then comply with the corresponding treatment standards per
waste code with consideration of any applicable subcategories
(e.g.,
44I~ighor ~jow Mg~ercury6~ubcategories).
RMETL Recovery of metals or inorganics utilizing one or more of the following
direct physical,’. or removal technologies:
1)
3~on exchange;
2)
resin or solid (i.e.,
zeolites)
adsorption;
3)
reverse osmosis;
4)
chelation,L or solvent extraction;
5)
freeze crystallization;
6)
ultrafiltration; and/or
7)
simple precipitation
(i.e., crystallization)
Note:
this
does
not
preclude
the
use
of
other
physical
phase
separation
or concentration techniques such as decantation, filtration
(including
ultrafiltration), and centrifugation, when used in conjunction with the
above listed recovery technologies.
RORGS Recovery of organics utilizing one or more of the following technolo-
gies:
1)
Distillation;
2)
thin film evaporation;
3)
steam stripping;
4)
carbon adsorption;
5)
critical fluid extraction;
6)
liquid—liquid extraction;
7)
precipitation,’- or crystallization
(including freeze
crystallization);
or
8)
chemical phase separation techniques
(i.e., addition of acids,
bases, demulsifiers,
or similar chemicals)-t..
Note:
This does not preclude the use of other physical phase separation
techniques such as decantation, filtration
(including ultrafiltration),
and centrifugation, when used in conjunction with the above listed
recovery technologies.
RTHRM Thermal recovery of metals or inorganics from nonwastewaters in units
defined as cement kilns,
blast furnaces,
smelting, melting and refining
furnaces,
combustion devices used to recover sulfur values from spent
sulfuric acid and “other devices~’determined by the Agency pursuant to
35
Ill.
14dm.
Code 720.110,
the definition of “industrial
furnace”.
294
RZINC Resmelting in high temperature metal recovery units for the purpose of
recovery of zinc.
STABL Stabilization with the following reagents
(or waste reagents)
or
combinations of reagents:
1)
Portland cement; or
2)
lime~~
or pozzolans
(e.g.,
fly ash and cement kiln dust)—-this does
not preclude the addition of reagents
(e.g.,
iron salts, sili-
cates, and clays)
designed to enhance the set,L or cure time and/or
compressive strength, or to overall reduce the leachability of the
metal or
inorganic.
SSTRP Steam stripping of organics from liquid wastes utilizing direct
application of steam to the wastes operated such that liquid and vapor
flow rates,
as well as, temperature and pressure ranges have been
optimized, monitored,
and maintained.
These operating parameters are
dependent upon the design parameters of the unit such as,
the number of
separation stages and the internal column design.
Thus,
resulting in a
condensed extract high in organics that must undergo either incinera-
tion,
reuse as a fuel,
or other recovery,& or reuse and an extracted
wastewater that must undergo further treatment as specified
in the
standard.
WETOX Wet
air
oxidation
performed
in
units
operated
such
that
a
surrogate
compound
or
indicator
parameter
has
been
substantially
reduced
in
concentration
in
the
residuals
(e.g.,
T~otal QQrganic
0~arbon
(TOC’)
can
often be used as an indicator parameter for the oxidation of many
organic constituents that cannot be directly analyzed in wastewater
residues).
WTRRX Controlled reaction with water for highly reactive inorganic or organic
chemicals with precautionary controls for protection of workers from
potential violent reactions as well as precautionary controls for
potential emissions of toxic7~-or ignitable levels of gases released
during the reaction.
Note
1:
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 Section 728.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.
Note
2:
When more than one technology
(or treatment train)
are specified
as alternative treatment standards, the five letter technology
codes
(or the treatment trains
are separated by a semicolon
(;)
with the last technology preceded by the word “OR”.
This indi-
cates that any one of
these BDAT technologies or treatment trains
can be used for compliance with the standard.
(Source:
Amended at
19
Ill. Reg.
,
effective
_____________________
Section 728.Table D
Technology-Based Standards by RCRA Waste Code
BOARD NOTE:
For the requirements previously found in this Section,
refer to
Sections
728.140
and
728.Table
T.
~1asto
Codes
Sec Also
295
Technology
Code,
Waste-
CAB No.
waters
NA
D~ACT, and
meet
F039p
or FSUBB;
RORCS;
or
INCIN
Nit
OEACT
and
meet F039
NA
DEZtCT
(but
not in-
cluding
dilution
as a sub—
stitute
for
ade-
quate
treatment)
NA
DEACT
Technology
Cods, Non—
waste—
waters
DEACT,
and
meet F039p
or FSUBS
RORCC;
or
INCIN
DEACT and
meet F039
DEACT
(but
not in-
cluding
dilution
as a sub—
at itut-c
for ade-
quate
treatment
DElICT
(a) (6-)
(a)
(84
r.T,.
-.4-.~
uoaonLptL~.-.....-
Treatment Cuboategory
All descriptions based
on 35 Ill.
Adm.
Code
721.121,
ecoept for the
Bection 721.121(a) (1)
High
TOO
suboatogory,
managed in non CW2t/non—
CWA—oquivalcnt/non—Clasa
I CDWA systems
All
descriptions
baocd
~c
T11
7~-~-~
~—-~-
NA
DEACT
NA
DEACT
NA
PSUBS;
RCRCC;
or
INCIN
721.121, except for the
Gection
261.l2l(a)(1
High TOC
auboatcgory,
managed in
ct-UI,
CWA—
equivalent,
or Class
I
6DWA
systems
All descriptions ba~cd
‘~
T11
‘“~m
(‘.-~
DOP1
Tables
it
DOOl
NA
DOOl
NA
D002
Tables A
D002
NA
0003
NA
0-003
NA
721.121(a)(l)—fligh
TOO
Ignitable Liquido Cub-
category——Creator
than
or equal to 10
total
organic carbon
Acid,
alkaline,
and
other subcategory based
‘——-
.,~
.r,
•)
~
Nit
DEACT
DEACT
721.122
managed
in
non—
CWA/non-CWZt-cquivalcnt/
non
Class
I
CDWA
systems
Acid,
alkaline,
and
other suboategory based
on 35 Ill. Adm. Code
721.122
managed
in
CWA,
CWA-cquivalent,
or
Class
I
CDt-UI
systems
Reactive
sulfides
based
on 35
Ill.
Adm.
Co-dc
721.123(a) (5)
Explosives baced on 35
Iii..
Yuim.
Cc~dc~
721.i2~
,
(a)(7),
-;~t~
Water rcactiv—~-
35 Ill.
14dm.
tc
721.123(a) (2).
and
(a)(4)
Other
rcac
b~scdon
(a(3),
—
-
tivtu
.~.
0003
NA
NA
D003
NA
NA
DO0&
NA
7440
43
9
0008
NA
7439 92-1
0009
Tables A
7439—97—6
0009
Tables
11
7439—97-6
296
NA
DElICT
DEACT
DEACT
Nit
RTHEFkH
NA
TILEZID
NA
IHERC;
or
IUIEflC
NA
RMERC
721.123(a)
(1)
Cadmium containing bat-
teries
Lead acid batteries
(Notci
This standard
only applies to lead
ai~idbatteries that are
identified as flORA
hazardous wastes and
that arc not excluded
elsewhere from
regulation under the
land disposal re-
strictions of this Part
or exempted under other
regulations
(ace
35
Ill.
Adm. Code 726.180).)
Mercury:
(High Mercury
Subcatcgory
greater
than or equal to 260
mg/kg total
Mercury--
contains mercury and or—
ganico (and arc not
incinerator residues))
Morcuryi
(High Mercury
Cubcatcgory
greater
t-I~an or equal
to 260
mg/kg total Mercury-—
inorganico (including
-incinerator residues and
residues from
~U1EflC))
0012
Table--B
72-20-8
BIODCp
INCIN
or
NA
D013
Table—B
58-89-9
CMLBN;
INCIN
or
NA
D014
Table-B
72 43-5
WETOX;
INCIN
or
NA
D0l5
Table—B
8001-35
1
BIODC;
INCIN
or
NA
D016
!Pa~bleB
94—75—7
CHO~cD-~-
BIODC;
INCIN
or
NA
CHOXD;
-I-NC-IN
or
NA
L indanc
tethoxychlor
Toxaphene
2, 4—D
0-017
Table—B
93—72—1
2, 4, S—TP
—
——--—--._i
-.
Distillation
bottoms
from the production of
nitrobcnzenc by the
nitration of bcnzcnc
stripping still tails
from the production of
methyl
ethyl
pyridincs
Centrifuge and
distillation residues
from tolucnc di—
isocyanata production
Filter cake from the
filtration
of
dicthyl—
phosphorodithioc acid
~n
the production of phor
e~e
wastowa-cer
treatment
sludges from the manu
faturing and processing
of oxplosivea
from the
Lpcnt carbon
~catment
~
containing cxplosivco
Pink/red water from TNT
operations
Emission control dustf
ludge from secondary
lead omelting~ Non-
Calcium
Sulfate
Sub—
category
Wastcwater treatment
-s-l~*dgo from
the
mercury
-sell
process
in
chlorine
productionz
(High
~1ercury
Cubcategory
greater
than
or equal to
260
mg/kg
total
mercury)
297
F005
~a~lcs
A
79-46-9
(WETOX
or
CHOXD)- fb
CARBN)
or
INCIN
F005
Tables A
110 80
S
BIODC; or
INCIN
F024
Tables A
NA
INCIN
K025
NA
NA
LLEXT
fb
SSTRIP fb
CARBN;
or
INCIN
K026
Nit
NA
INCIN
K027
NA
NA
CAREN; or
INC
IN
K039
NA
NA
CARBN; or
INCIN
K014
NA
INCIN
INCIN
INCIN
INCIN
INCIN
FEUBS; or
INC
IN
F~UBC or
INCIN
NA
DElICT
DElICT
~045
1W47
K069
NA
NA
Tables A
NA
DElICT
NA
DElICT
NA
Nit
DElICT
DElICT
BLEAD
1~106
Tables A
NA
Nit
RMERC
NA
INCIN;
or
CHOXD
fb,
CARBN~
or
BIODC
fb
CARDII
NA
INCIN;
or
CHOXO
fb,
C14R1311;
or
BIODC fb
CZIRBN
NA
INOIN;
or
CHOXD fb,
CAREN; or
BIODC
fb
CARBN
INCIN;
or
CHOXD
fb,
CAREN; or
BIODC
fb
CARBN
NA
INCIN
or
CHOXD
fb,
CARBN;
or
BIODC
fb
CARBN
298
Column bottoms
from
product separation from
the production of
1,1-
dimcthylhydracinc
(UDHM)
from carboxylic acid
hydra~idec
Condensed
column
overheads from product
separation
and
condensed
reactor vent gases from
the production of
1,1-
dimcthylhydrazinc (UDHH)
from carboxylia acid
hydracidcs
Spent filter cartridges
from
product
purification from the
production of 1,1-
NA
l~107
NA
KlCB
NA
Kl09
NA
NA
Kl12
NA
X1l3
NA
K114
NA
K115
NA
dimethylhydrazinc
(UDMH)
from carboxylic acid
hydrazidcs
Condensed column
overheads from
intermediate ceparatiori
INCIN.
INCIN.
INCIN.
INCIN.
INCIN.
FCUBC; or
INCIN
FSUBSf
or
INCIN
FSUBS;
or
INC
IN
from the
k,..
Hl-,-l
dimethyl..1~..-~..~
(UDMH~
from aarboxylic
l....4.._
-
--4
Reaction by product
--
4~om
the
dryi...,
~-
NA
CARBMp or
INCIN
NA
CARBNI
or
INCIN
NA
CZIRBN;
or
INCIN
prouuucwn
of
tolucncdiaminc
via
hydrogenation of
dinitrotoluenc
Condensed liquid light
ends from the
purification of
toluencdiaminc
in
the
production
of
tolucncdiaminc via
hydrogenation of di—
nitrotoluone
Vicinals from the
purification of tol
ucncdiaxnine
in
the
production of toluenodi—
amine via hydrogenation
of dinitrotoluenc
r,f
purif~—--~--
in
t-hc
tolucncdiaminc
production of tol—
ucncdiaminc via
•~2
—
nitrotolucnc
299
NA
INCIN;
or
INCIN.
CHO)W fb
(CIODO or
CZIREN
)-
NA
INCIN;
or
INCIN.
CHOXD fb
(BIODC or
CZIBBN)
NA
INCIN;
or
INCIN.
CHOXD
fb
(BIODC
or
CZ1RBN)
NA
INCIN~or
INCIN.
OHOXD
fb
(BIODC or
CARBN)-
POOl
NA
81—81-2
(WETOX
or
CIJOXD)
fb
CARBN;
or
INCIN
FS-UBS?
or
INCIN
Warfarin
(-0.3)
P002
NA
591082
(WETOX or
CHOXD)
lb
Cl\RBN or
INCIN
INCIN
l-Acctyl
2 thiourca
NA
F~UBC;
or
INCIN
Pop~
NA
107186
(WETOX
or
GHOXD) lb
CAREN; or
INCIN
F~UaC; or
INC
IN
Allyl
alcohol
P006
NA
-20859—73
8
CIIOXD
-
CHRED;
O-E
I-NCIN
CHOXD 1-
CHRED;
or
INCIN
Aluminum
phosphidc
NA
CARON;
or
INCIN
FCTJBC;
or
INCIN
1(116
NA
1(123
NA
1(124
NA
K125
NA
1(12-6
Nit
Organic condensate from
the solvent recovery
column in the production
of toluono diiaooyanate
via phoogonation of
toluenedianiine
Process wactcwatcr
(including cupcrnatcs,
filtrates, and
washwatcro)
from
the
production of
ethylcncbis
dithiocarbamic acid and
its salts
Reactor vent
scrubber
water from the
production of
ethylcnebisdi—
thiocarbamic
acid
and
its
salts
Filtration,
evaporation,
and ccntrifugation
solids
from
the
production
of
ethylenebisdi-
thiocarbamic acid and
its
salts
Baghouse dust and
floor
ewcepinga in milling and
packaging operations
from the production or
formulation
of
ethylene
bisdithiocarbamic acid
and
its salts
P003
NA
~0-7
02-8
Acrolcin
300
P007
NA
2763964
(~ETOXor
CHOXD)
fb
CARBN; or
INCIN
INCIN
5 2’Iminocthyl 3-
isoxazolol
r014
NA
108955
(WETOX
or
CHOXD)
fb
CZIRBN or
INCIN
INCIN
Thiophenol
thiol)
(WETOX
or
NCIN
01101W)
lb
CAREN; or
INCIN
P017
NA
598—31
2
(WETOX or
CHOXD)- fb
CZIRBN;
or
INCIN
INCIN
Bromoacctonc
P018
NA
357—57—3
P022
Table
B
75—15—0
P023
NA
107 20
0
(WETOX
or
INCIN
CHOXD)
lb
CARI3N or
INCIN
NA
INCIN
(WETOX or
I-NC-I-N
CHOXD)
lb
CARBN;
or
INCIN
P026
P027
NA
5344—82—1
Nit
542—76—7
(WETOY.
or
CHOXD)
fb
CARBN
or
INCIN
(WETOX or
01101W)
lb
CAnON;
or
INC
IN
INCIN
INCIN
1—(o-Chlorophenyl)thio—
urea
P028
NA
100—44—7
(WETOX or
CHOXD)
fb
CAnON;
or
INCIN
INCIN
Bcnzyl
chloride
P008
NA
504—24-5
(WETOX or
CHOXD)
lb
CARENp or
INCIN
P009
NA
131—74--S
CHOXD;
CHRED;
GARBN;
BIODC;
INCIN
or
INCIN
FSUBS;
CH—
OXD-
CHRED;
or
INCIN
4 Aminopyridinc
Z~mrnoniumpier-ate
P015
P016
NA
7440
41-3
NA
542881
RM~-e~
RTHRM
RHETL;
or
RTHRH
Beryl1 i
.i
—,
Bruci~e
~1
301
P031
NA
460195
CHOXD;
WET-OX;
or
INCIN
CHOXD;
WETOX;
or
INCIN
Cyanogen
P034
NA
131895
(WETOX
or
CHOXD
fb
C2IRBNp
or
INCIN
INCIN
2—Cyclohexyl
4,6
di—
nitrophcnol
P040
NA
297072
CAnON;
or
INCIN
FCUBC;
or
INCIN
0,0
Diethyl
0
pyratinyl
phosphorothiopto
±,
~thv1
1——-—.—I———.—..1
-~
--~
—
~,
phosphate
P042
NA
51—43—4
(WETOX
or
Ct-IOXD)
fb
CARBN;
or
ENCIN
INCIN
Epiricphrinc
P043
P044
P045
P046
NA
55—91-
4
NA
60—51—5
NA
39196—18—4
NA
122—09—8
CARBN;
or
INCIN
CARBN;
or
INCIN
(WETOX
or
CHOXD)
fb
CAnON; or
INCIN
(WETOX or
CHOXD)
fb
CARDN; or
INCIN
F&UBS;
or
INC
IN
F-SUBS; or
INCIN
INCIN
I-NCIN
iioopropyl luorophos—
phat-e
(DFP)
Dimethoato
Thiofanox
alpha, alpha-Dimcthyl—
(WETOX
or
INCIN
CHOXD)
lb
CARBN; or
INCIN
(~ETOXor
INCIN
CHOXD)
fb
CAnON; or
INCIN
(WETOX
or
INCIN
CHOXD)
fb
CARBU;
or
INCIN
NA
2~DCAC fb
NEUTR
(WETOX
or
I-NCIN
CHOXD)
fb
CARBN;
or
INC
IN
rG33
NA
506—77
4
CHOXD;
WETOX-
or
INCIN
OHOXD
WETOX;
or
INCIN
—-4
P041
NA
311
45
5
CARBN;
or
INCIN
FCUBC;
or
INCIN
4,6 D~-~
salts
o—cres-ol
P047
NA
5-34 52—1
P049
NA
541—53
7
P054
Nit
151—56—4
P056
Table B
7782-41 4
PQ57
NA
640—19—7
2, 4-Dithiobiuret
Asiriding
Fluorine
Fluoroacetamide
302
P058
NA
62-74
8
(WETOX
or
CHOXD)
lb
CAnON;
or
INCIN
INCEN
sodium salt
P0~5
Tables
A
628--86
4
(WETOX
or
INCIN
CHOXD)
lb
CARBN;
or
INCIN
NA
RMERC
residues from
RHERC)
P065
Tables A
628-86-4
P06-6
P067
NA
16752—77
5
NA
75558
NA
IMERC
-(--WETOX
or
CHOXD)
fb
CAnON;
or
INCIN
-(WETOX
or
CHOXD~ Lb
CItRBN;
or
INCIN
INC IN
INCIN
Mercury fulminate:
(-All
nonwastewators that arc
not incinerator residues
or arc not residues
from
RHERC:
rcaardlcos of
Mercury Content)
Hcthomyl
2 Methylatiridinc
P068
NA
60—34—4
CHOXD CH-
RED;
CAREN;
BIODC;
or
INCIN
FSUBS;
CH—
OXD;
CHRED;
OR
INCIN
Methyl hydracinc
r069
P070
P072
NA
75-86—5
NA
116063
NA
86-88-4
(WETOX
or
INCIN
CHOXD)
lb
CARBN? or
INCIN
(WETOX or
INCIN
CHOXD)- lb
CARBN;
or
INCIN
(WETOX
or
INCIN
CHOXD)
Lb
CARON;
or
INC
IN
Aldicarb
P062
NA
757
58
4
P064
NA
624 83
9
0AnON
or
INCIN
FCUBS or
INCIN
Isocyanic acid,
ethyl
ester
Mercury fulminate
(High Mercury Cub—
catcgor~——grcater
~1
mg/kg
~~~~~~.1
I
_~I.~.-t.4-1~.1
~
~1
P092
Tables A
62 38
4
NA
IMERC;
or
RMERC
t~ncnyLmercury acetate:
(All nonwastewatcrs that
are not inoinerator
re~iduocand arc not
residues from
RflERC:
recardicec of Mercury
Content)
NA
84-1-15
NA
10102
43
9
NA
10103—44—0
NA
55630
__—~
_I3~~.
Nitric oxide
P075
P0Th
P0
7-8
P081
P082
P084
P085
P087
P088
--
Nitroglyccrin
Table B
NA
62—75—9
4549-40—0
303
(WETOX
or
CHOXD)
fb
CAnON; or
INCIN
ADCAC
ADCAS
CHOXD; CH
PiED;
CAnON;
BIODC
or
INCIN
NA
(WETOX
or
CHOXD)
fb
CARBN;
or
INCIN
CARBN; or
-IN-GIN
RHETLp or
RTHEM
-(WETOX
or
CHOXD)
Lb
C2\RBN
-or
INCIN
INCIN
ADCAC
r~DCA8
FCUBC;
CU-
OXD;
CHRED;
or
INCIN
INC
IN
INCIN
FSUBC; or
INCIN
RHETL;
or
RTHRM
FCUBC;
or
INCIN
NA
152—16—9
NA
20816—12
0
Nit
145733
P092
Tablco—A
62
3-8
4
N Nitrosomethylvinyl-
amine
Octamethylpyrophoophor-
am-ide
Osmium tctroxidc
Endothall
t’hcnyl
mercury
acetate:
-(High Mercury Sub-
oatcaor”——aroator
Nit
RHERC
~.
~al
to 260
~
total Mercury
either
inoinerator residues or
residues from
RHERC~
P09~3
NA
103
85- 8
(WETOX sr
INCIN
CHOXD)
lb
CABEN;
or
INCIN
P095
NA
75—4-4-5
(WETOX
CHOXD)
CAnON;
INC
IN
or
f.b
or
INCIN
P096
NA
7-803-51-2
CHOXD;
RED;
-or
INCI-N
-CH-
CHOXD;
RED;
or
INCIN
CU-
Phosgcnc
Phosphine
304
P102
NA
107
19—7
(WETOX or
CHOXD)
fb
CAnON;
or
INCIN
FCUBC; or
INCIN
P105
NA
26628-22
8
OUOXD CU
RED;
CAnON
EIODC; or
INCIN
FCUBS;
CU—
OXD
CURED; or
INCIN
Codium azidc
Plop
NA
57-2’i—9
A
(WETOX
or
CHOY.D)
fb
CARBN or
INCIN
CHOXD CU-
RED;
CARBNi
010CC;
or
INCIN
INCIN
NA
RTURH
or
STABL
NA
RTHR;
or
STABL
(WETOX
or
INCIN
CHOXD-)
fb
CABBN
or
INCIN
(WETOX
or
INCIN
CHOXD
fb
CARBN;
or
INC IN
UOO1
NA
75070
(WETOX or
CUOXD)
fb
CARON;
or
INCIN
INCIN
Acctaldchydc
U003
Table B
75 05—S
NA
INCIN
Acctonitrilc
U006
NA
75
36—-B
(WETOX or
CHOXD)
lb
CARBN;
or
INCIN
INCIN
CABEN;
or
INCIN
FSUBS; or
INCIN
FSUBS;
CU-
OXD
CURED; or
INCIN
P10-9
NA
3689—24—5
P112
NA
509—14—8
P113
Table B
1314—32
5
-P115
Table B
-7446—18-6
P116
NA
79—19—
P~118
NA
75—70—7
P119
Table B
7803-55 6
P120
Table B
1314—6-2-1
P122
NA
1314—84
7
phosphate
Tctran itromethano
Thallic oxide
Thallium
(I)
sulfate
Thiosemicarbaside
Triohloromcthanethiol
Arnmonium
vanadatc
Vanadium pentoxide
Zinc
Phosphidc (~l0)
NA
CTABL
NA
STABL
CHOXD;
CU
RED;
or
INCIN
CUOXD;
Cli
RED;
or
IIWIN
305
UO0 7
NA
79 06—i
(-WETOX or
CHOXD-)
fb
CAROM; or
INCI-N
-I-NC-IN
Acrylamida
UOO-8
NA
79—10
7
(WETOX or
CHOXD)
Lb
CARON;
or
INCIN
F-CUBS;
or
INC
IN
Acrylic acid
U010
NA
50
07—7
-(-WETOX
or
CHOXD)
fb
OABBN;
or
INCIN
INCIN
Mitomycin C
U011
NA
61—82—5
(WET0X
or
CIIOXD)
fb
CAnON;
or
INC
I-N
INCIN
Amitrole
U014
NA
492
80—8
(WETOX or
CUOXD
fb
CAnON;
or
INCIN
INCIN
Auraminc
Up
is
NA
115
02-6
(WETOX
or
CUOXD)
lb
CARON;
or
INCI N
INC
IN
asorifle
U01 6
U-U-i
7
Nit
225—51—4
NA
98—87—3
(WETOX
or
CUOXD)
Lb
CAROM; or
N0IN
(WETOX or
0~1OXD) lb
CAItBN; or
-INCIN
FSUBC;
or
INCIN
INCIN
Bcns
(
c) acridinc
Bcnzal
chloride
U020
NA
98
09—9
-?WETOX or
CHOXD)-
lb
CAROM; or
INCIN
INCIN
1
__1
.1.1
U02 1
NA
92
87-5
(WETOX or
CHOXD)
fb
CAROM; or
INCIN
Bcnzidinc
U023
NA
98—07—7
CHOXDp CU-
RED;
CARBNt
BIODC; or
INCIN
FSUBSp CU—
0XD,
CURED;
or
INCIN
U02 6
NA
494 03—1
(WETOX or
CHOXD)
fb
CAROM;
or
INCIN
INCIN
Chlornaphazin
306
U033
NA
353504
(WETOX
or
CHOND)
lb
CAROM;
or
INCIN
INCIN
U034
NA
75 87—6
(WETOX
or
CHOXD)
Lb
CAROM; or
INCIN
1110111
(Chloral)
U035
NA
305—03—3
(WETOX or
CHOXD)
Lb
CAROM; or
INCIN
INCIN
Chlorambuoil
U038
Table B
510-15-6
NA
INCIN
1
(WETOX
or
INCIN
CHOXD
Lb
CAROM;
or
NCI-N
NA
INCIN
(WETOX
or
INCIN
CHOXD
fb
CAROM;
or
‘11Cm
(WETOX
or
INCIN
CHOXD) lb
CAROM; or
INCIN
(WETOX
or
CHOXD
fb
CAROM; or
INCIN
U055
NA
98828
(WETOX
or
CHOXD)
lb
CAROM;
or
INCIN
FCUBC;
or
INCIN
Cumcne
U056
NA
110 82—7
(WETOX
or
CHOXD)
fb
CAROM;
or
INCIN
PSUEC;
or
IIWIN
Cyclohexane
U057
T-able B
103 94—1
NA
F-SUBS;
or
INCIN
UPS 9
NA
20a30-81-3
(-WETOX or
CHOXO)
fb
CriRDN~
or
INCIN
INCIN
Daunomycin
U04l
NA
106 89-8
U042
Table--B
110-75-8
U046
Nit
107-30-2
U-049
NA
3165—93—3
U053
NA
4170—30—3
1-Chloro-2, 3-epoxy-
propane
(Epichioro—
hydrin)
2-Chlorocthyl
vinyl
ether
Chl-oromcthyi methyl
ether
4—Chloro-o-toluidine
hydrochloride
Crotonaldchyde
FSUBS
or
INCIN
U058
NA
50-18
0
CAROM; or
F&UBC; or
INCIN
INCIIX
—-4
U062
NA
230~—16-4
307
(WETOX or
INCIN
CHOXD)
Lb
CAROM;
or
INCIN
Diallate
U064
UP73
U074
Upes
U086
U087
U-PC9
U090
U0-9
I
U092
NA
189 55—9
NA
91—94—1
WA
1476—11—5
NA
1464 53—5
NA
1615—80—1
Nit
3288—58—2
NA
56 53—1
NA
94—58—6
NA
119904
NA
124—40
3
U093
Table
B
621—90-9
(WETOX
or
CHOXD)
lb
CAROM;
or
INCIN
(WETOX
or
CHOXO)
fb
CARBN
or
INCIN
(WETOX or
CHOND)
Lb
CAROM; er
INCIN
(WETOX or
CHOXD)
fb
CAROM; or
INCIN
CUOXD;
CURED;
CAROM;
BIODCp or
INCIN
CARBN;
or
INCIN
(WETOX or
CHOXD)
lb
CAROM;
or
INCIN
(WETOX
or
~H0-XD)
lb
CAROM;
or
INCIN
(WETOX
or
CUOXD)
lb
CAROM;
or
INC IN
(WETOX
or
CHOXD)
fb
CARBUp
or
INC IN
Nit
FCUB6;
or
INCIN
INCIN
INCIN
FCUBC;
or
INCIN
FSUB6;
CHOXD
CURED;
or
I-NCIN
FSUBS~or
INCIN
FSUBS;
or
-I-NC-IN
FStJBS~
or
INCIN
INCIN
INCIN
INCI-N
1,2,7,8 Dibcn~opyrene
3,3 ‘—Diohiorobencidine
ole—i,
4—Diohloro—2-bu—
tcne trans 1,4 Di—
ohloro-2---butone
1,2:3,4 Dicpoxybutanc
N,N
Dicthylhydratine
0,0-Diethyl C-methyl-
dithiophosphate
Diethyl stilbcotrol
Dihydrosafrolc
3,3’ Dimothoxybcn~idinc
Dimcthyiamine
p—CimcthylaminoaBo-
benccne
U09 4
NA
5797?
(WETOX or
CHOND)
fb
CABBN; or
INCIN
PSUOC;
or
I-MCIN
7,i2—Dimcthy~”
anthraoono
IUUIIL
U)
—
308
U09 5
U09-6
U097
NA
119—93
7
NA
80159
NA
79—44—7
(WETOX
or
INCIN
CHOXO)
Lb
CARBN
or
INCIN
CHOXD;
F-CUBS;
CURED;
CHOXDg
CARBN;
CURED;
or
BIODC;
or
INCIN
1110111
~(WET0X
or
INCIN
CHOXD
fb
CAROM;
or
INCIN
3,3’
Dirncthylbcntidino
alpha, alpha Dimcthyl-
bancyl hydroporoxido
Dimethyloarbamoyl
ohior—
~e
0110XO;
CU-
FCUBC;
CU
~-~-1-~
RED;
OXD-
CAROM;
CURED;
or
BIODC
or
INCIN
INCIN
CHOXD;
CU-
FSUBS;
OH-
1,2 Di
RED-
OXD
CAROM;
CURED;
or
BIODC;
or
INCIN
INCIN
CUOXD
CII
FCUBC;
CII-
0*
RED;
OND;
CAnON;
CUBED;
or
010CC;
or
INCItI
INCIN
CHOXD; CU-
FSUBCp
CU-
~-
RED;
OXD;
CAROM;
CURED;
or
010CC; or
1110111
I-NCIN
Ulip
NA
142—84 7
(WETOX
or
CHOXD)
fb
CAROM;
or
INCIN
INCIN
Dipropylamine
U1l3
NA
140-88
5
(WETOX
or
CHOXD)
Lb
CAROM;
or
INCIN
FCUBC~o~
INCIN
——.-_g—
———-j
Nit
111—54—6
(WETOX
or
INCIN
CHOXD)
Lb
CARBN; or
INCIN
carbamic
acid
UI15
Nit
75—21—8
(WETOX
or
CHOXD) Lb
CAROM;
or
INCIN
CUOND;
or
INCIN
• ~metnylhydrai~inc
U098
NA
57147
U09-9
NA
540—73—8
U103
NA
77781
U-I-09
NA
122—66—7
—--4
1
U114
A 4 -4~1.
309
~WETOX
or
1110111
CHOXD)
lb
CARBN;
or
INCIN
-(WETOX
or
INCIN
CI4OXD)
lb
CAnON;
or
INCIN
U122
NA
50—00-0
(WETOX or
CHOXD)
fb
CAROM;
or
INCIN
FCUB&;
or
INCIN
Formaldehyde
Ui23
NA
54-13-6
-(-WOTOX or
CHOND)
fb
CAROM;
or
INC
IN
FCUBS;
or
1-110111
Formic acid
tJ124
NA
110 00-9
(WETOX
or
CUOXD)
fb
CAROM;
or
INCIN
FCUBS;
or
1110111
Furan
U125
NA
98011
(WETOX
or
CHOXD)
f-b
CAROM;
or
1110111
FCUBC;
or
INCIN
Furfural
-(WETOX
or
CHOXD)
Lb
CAROM;
or
1110111
(WETOX
or
1110111
OHOND)
fb
CARBI;
or
1110111
FCUBS;
CUOXD
CURED;
or
-INC
IN
NA
ADCAS
lb
NEUTR;
or
NEUTR
Ui 43
NA
303—34—4
(WETOX
or
1110111
CHOXD) fb
CAROM; or
INCIN
Lasiocarpinc
U116
WA
96-45—7
U119
NA
62-50 0
Ethylene
FEUBS; or
111dM
U-126
NA
765—34—4
U132
NA
70—30—4
U133
NA
~-02—01---2-
U134
Table
B
7664-39-3
U135
NA
7783—06—4
CHOXD;
CURED;
CIiBBN;
BIODC;
or
INCIN
Hcxachlorophcne
Hydratme
Hydrogen
Fluoride
u~droacn
Sulfide
CUOXD;
CU-
CHOXD
CU-
~
RED; or
RED; or
1110111
111dM
U147
NA
108
31
6
U146
NA
123 33
1
310
(ti7ETOX
or
CHOXD)
Lb
CAROM;
or
INCIN
(WETOX
or
INOIN
CHOXD)
Lb
CARBNJ
or
1110111
U149
NA
109—77—3
(WETOX
or
CUOXD)
fb
CAROM;
or
INCIM
INCIN
Malonon-itrilo
U150
NA
148—92—3
(WETOX
or
CHOXD) Lb
CAROM; or
1110111
1110111
Mclphai-an
U151
Tablec A
7439-97
6
U153
NA
?4O~1
U154
NA
67—56—1
U156
NA
79—22—1
(WETOX
or
INCIN
CHOXD) fb
CAROM; or
INCIN
(WETOX
or
CHOXD)
Lb
CARBN;
or
INCIN
(WETOX
-or
1110111
CIIOXD)
fb
CAROM;
or
1110111
(WETOX or
INCIN
GHGXD)
Lb
CAROM;
or
INCIN
(WETOX
or
INCIN
CHOXD
Lb
CitRBN;
or
1110111
(WETOX
or
CHOXD)
fb
OARBt’I;
or
INC
IN
FCUBS; or
INCIN
faicic
anhydridc
Jialcic
hydra~id~
NA
RHERC
norcury:
(iu.gn
Mercury
Cubcategory
greater
than or
equal
to
2-60
mg/kg
total
Mercury)
Methanethiol
Methanoi
Methyl chlorooarbonatc
FSUBS;
or
INCIN
U160
Nit
1338-23-4
CHOXD;
FSUBS
CURED;
CHOXD~
CAROM,
CURED; or
010CC;
or
INCIN
INCIN
Methyl
oxide
Ui6~
NA
70—25—7
U164
NA
56—04—2
U166
NA
130—15
4
N-Methyl-N’
-nitro-N—
Nitrocoguanidino
Mothyithiouracil
1, 4-Naphthoguin-one
FSUDC;
or
INCIN
311
U167
NA
134—32—7
(WETOX
or
CHOXD)
lb
CAROM;
or
INCIN
INCIN
I Naphthylamine
U168
Table
B
91-59
8
Ui71
NA
79
46—9
NA
1110111
(WETOX
or
CHOXD)
lb
CAROM;
-or
1110111
INCIN
U17 3
U. 76
U17 7
NA
1116—54—7
Nit
759739
Nit
684—93—S
(WETOX
or
CHOXD)
Lb
CARBN;
or
INCIN
(WETOX
or
CHOXD)
fb
CAROM;
or
1110111
(WETOX
or
CHOXD)
Lb
CAROM;
or
INC
IN
I-NCI-N
INCIN
-INC-IN
N Nitroso dicthanolzuninc
tI Nitrooo-N ethylurca
N—Nitrooo—N-mothylurca
(WETOX
or
INCTh
CHOXD)
fb
CAROM; or
INCIN
(WETOX or
CHOXD)
lb
CAROM;
or
INCIN
(WETOX
or
1110111
CHOXD)
fb
CAROM;
or
INCIN
(WETOX
or
CEJOND)
lb
CAROM;
or
INCIN
CUOXD; CU-
RED;
or
INCIN
(WETOX
or
INCIN
CHOXD)
lb
CAROM;
or
1110111
(WETOX
or
INCIN
CHOXD)
lb
CAnON; or
1110111
F-CUBS; or
1110111
U178
Nit
615—53—2
U1-82
NA
123—63—7
U184
NA
76017
U186
NA
504—60-9
U189
NA
1314—80—3
U191
WA
109—06—8
U193
Nit
1120 71—4
urethane
Paraldchyde
Pcntachloroothanc
1, 3—Pent adicnc
Phosphoruc oulfide
2—Picolinc
1,3-Propane
aultone
F-SUBS;
or
INCIN
CHOXD CU-
RED;
or
INCIN
312
U19 4
Nit
107
10-8
(WETOX or
CHOXD-)
lb
CAROM; or
INCIN
INCIN
13197
NA
106
51—4
-(WETOX
or
CHOXD)
Lb
CAROM; or
INCIN
FCUBC;
or
INCIN
1320-P
NA
50—55—5
(WETOX
or
CHOXD)
lb
CAROM;
or
INCIN
INCIN
Rceorpino
U201
NA
108—46—3
(WETOX
-or
CHOXD)
lb
CAROM;
or
INCIN
FOUBS;
or
INCIN
Rocorpinol
U202
NA
81072A
(WETOX
or
CUOXD)
lb
CAROM;
or
INC
IN
INCIN
(WETOX
or
INCIN
CHOXD)
lb
CARBN;
or
INC
IN
(WETOX or
CHOXD)
lb
CAnON;
or
1110111
U214
Table-B
563—68—8
U215
Table B
6533—73-9
NA
RTURM
or
CTADL
NA
RTHRM;
or
CTABL
Thallium
(I) acetate
Thallium
(1) carbonate
1.1216
Table B
7791
12
0
NA
flTHrU~p
or
CTABL
Thallium
(I)
chi-oride
U217
Table B
10102-45
1
NA
UTURM;
or
CTAOL
Thallium
(I) nitrate
U2 18
U219
U221
Nit
62—55—5
NA
62
56—6
Nit
25376
45
3
(WETOX
or
CHOXD)
Lb
CARBN~
or
1110111
(WETOX
or
CHOXD)
Lb
CAROM;
or
INCIN
CAROM;
or
INCIM
1110111
INC
IN
Thioacctamidc
Thioure-a
Tolucnediainino
U206
NA
18883-66
4
U213
NA
109 99—9
Streptozatocin
Tctrahydrofuran
FEUDS;
or
1110111
FSUBC; or
INCIN
313
(WETOX
or
INCIN
CHOXD) Lb
CAROM; or
INCIN
CARBU; or
INCIN
-(WETOX
or
INCIM
OHOXD)
Lb
CAROM;
or
1110111
U236
NA
72—57
1
(WETOX or
CHOXD)
fb
CAROM; or
1110111
INCIN
Trypan Blue
(WETOX
or
INCIN
CHOXD)
fb
CARBN; or
INCIN
2, 4—Dichlor~
accti
~
cetera)
U328
NA
95—53—4
INCIN;
or
CHOXD
Ib,
(010CC
or
CAROM);
or
BIODC fb
CAROM
INCIN; or
Thcrm~
Dcetructio
o-toluidinc
U222
NA
636—21
5
U223
NA
26471
62
5
U234
NA
99354
FCUBC;
or
INCIN
o ioiuipinc nyaro
chloride
Tolucnc diiaocyanatc
ayxn
Trinitrobcnzcnc
1110111
INC-IN
(WETOX
or
CHOXD)
lb
CAROM; or
INCIN
(WETOX
or
CHOXD)
fb
CAnON; or
INCIN
~~~~2~
U2
3~7
13238
13240
U244
U246
U248
tJ2
49
NA
~6—75
1
NA
51—79
6
NA
94757.k
NA
137-26-B
NA
506—68—3
NA
81
81—2
NA
1314—8’1—7
(aaita- and
(WETOX or
CHOXD)
fb
CAROM; or
INCIN
CUOXD;
WETOX;
or
INCIN
(WETOX
or
CHOXD)
fb
CAROM;
or
INCIN
CHOXDp CU-
RED; or
INCIN
INCIN
CUOXO;
WETOX;
or
INCIN
FEUDS; or
INCIN
CUOXD; CU-
RED; or
1110111
Thiram
Cyanogcn bromide
lace)
Narfarin
(0.3
or
Zinc Phoephidc
(10)
INCIN;
or
CIIOXO
Lb,
(01000 or
CARBN;
or
010CC
lb
CAROM
111dM;
or
p
toluidinc
Thermal
Dcctructio
n.
B
This waste cede exists
in gaseous lorm and is not aatagori~edae
waotcwatcr or nonwaatowatcr forms.
NA
Not Applicable.
BOARD
NOTE,
When a
combin-ation
of these technologiac
(i.e.,
a treatment
train)
ic specified as a
aingl-e treatment atandard, the order of application
ic c~pecifiodin thia Table by indicating the five letter technology code that
must be applied first, then the dccignation
“fb”
(an abbreviation
for “Fol-
lowed by”),
then the five letter technology code for the technology that
must
be applied next,
and co on.
When more than one technology
(or treatment
train-) are specified a alternative treatment otandardo, the five letter
technology codea
(or the treatment trains)
are separated
by
a
semicolon
(,,)
with the last technology preceded by the word “or”.
This indicates that any
one of those BOAT tochnologico or treatment traina can be uocd for compliance
~-ziththe standard.
Soc Section 725.Tabio C br
a hating
of the toohnology
codas and technology based treatment standards.
Derived from 40 CFR 268.42,
Table
2
(1992),
as amended at
57 Fed.
flog.
37273
(Aug.
18,
1992)
and 59 Fed.
Beg.
~iS52 (June 20,
1994).
(Source:
Amended at 19
Iii. Reg.
effective
Section 728.Table E
Standards for Radioactive Mixed Waste
BOARD NOTE:
For the requirements previously found in this Section,
refer to
Sections 728.140 and 728.Table T.
I
314
U353
U3 59
NA
106490
NA
110-80—5
INCIN;
or
CHOXD
Lb,
(BIODC or
CARBN)f
or
010CC
Lb
CAROM
—--—--4
1110111;
or
FOUBS.
d only.
and/or t~
category
Waste
code
0002
D004
CAd No.
NA
NA
Radioactive high level
waotcc generated
during the
reproccacing of fuel
rode oubeatcgory
Radioactive high level
waotco generated
during the
reproocecing of fuel
rode cubcatcgory
level
Radioactive high
Wastcwatcro
NA
NA
Nonwacte
watera
HLVIT
HLVIT
0005
NA
NA
HLVIT
thiring the
are not
ii
all
forrno
mited to,
of icad
chic~lding, and other
elemental formo of
mfr.~-”~
DO0~
Radioactive high
.cvol
~J~tc~
generated
Eapr00000ing of fuel
rode ouboategory
fladioaetivc high level
wactea generated
during -t~c
~-eproccooingof fuci
rode oubcategory
Radioactive hi-gh level
waatee generated
during the
reproccocing of
fuel
rode
ouboategory
fladioactivc lead
eolido ouboategory
‘Note, thoce lead
solido include
0006
0003
0008
0008
000-9
0009
315
NA
NA
7439—92
1
NA
NA
7439 07—6
7439076
NA
lead
lead
oplido do not include
treatment reeiduala
such ac hydroxide
eludgco, other
waatcwatar treatment
recidualo, or
incinerator achec that
can undergo
conventlanai
poccolania
n’rrinl
t~j~1 r~r~
-
nn~
r1r~
HLVIT
HLVIT
MJ~CR0
HLVIT
2~flLCM
IflERC
HLVIT
O~yaflOi~.~u
1u1.~i~
that ean be
incinerated and
otabilizcd ac
aoh).
R~dioactivohigh level
waotco generated
during the
roprooccoing of fuel
rode ouboategory
Elemental mercury
contaminated with
radioactive niatorialo
Hydraulic oil
contaminated with
mcrcury~radioactive
meteriale euboategory
during the
1
316
~‘edo
sub category
DOlO
Radioactive
hi-gh
level
tii~tert
generated
during the
~‘-eprocceeing
a-f fuel
rode auboategory
Ttadioactive high level
waotco generated
during the
~eproecooing
-of fuel
rode aubczitcgory
Mcrcuryi Elemental
mercury contaminated
~ith radioactive
materiale
NA
NA
For the treatment standards previously found in this Section and Section
728.146, refer to Sections
728.140 and 728.Table T,
“Treatment Standards for
Hazardous Wastes”.
W-aatc code
Ccc Alco
Regulated
Hacardouo
Conat ituent
cAB
No.
for
Regulated
Hazardou-o
Conotituent
(-mg/i)
TCLP
Antimony
Arocnic
&ariuin
Beryllium
Cadmium
Chromium
(total)
Cyanide
(mg/kg)
(total)
Lead
Mercury
Nickel
Sclcnium
Cilvcr
Thallium
Zinc
Antimony
Araenic
Barium
Beryllium
Cadmium
Chromium
(total)
Lead
Mercury
Nickel
7440—36—0
7440 38—2
7440-39-3
7440—41—7
7440—43—9
7440 47—32
57—12—5
7439—92
1
7439—97—6
74 40—02—0
7782
49—2
7440—22
4
7~.40—66—6
7440
36—0
7440-38—2
7440—39—3
7440—41—7
7440 43—9
7440
47—32
7439—92—1
743997
6
7440
02
0
2.1
0.055
0.014
0.19
0.33
0.37
0.009
5.0
0.16
0.30
0.078
2.1
0.055
0~
014
0.19
0.33
0.37
0.009
Doll
NA
HLVIT
NA
NA
HLVIT
7 439—97—6
AMLCM
Notes NA meano Not Applicable.
(Source:
Amended at
19
Ill.
Reg.
_______,
effective
_____________________
Section 728.Table G
Alternative Treatment Standards Based on HI4TMR
P006
K062
Tablec A & B
Tablea
A £ B
-
317
Cclcnium
7782-43
2
0.16
Cilvcr
7440
2-2-4
0.30
Thallium
0.~078
ama
7440—66—6
(Source:
Amended at
19
Ill.
Reg,
________,
effective
______________________
Section 728.Table T
Treatment Standards
for Hazardous Wastes
Note:
The treatment standards that heretofore appeared in tables in Sections
728.141,
728.142,
and 728.143 have been consolidated into this table.
Waste Code
Waste Description and Treatment or Regulatory Subcategory’
Regulated Hazardous Constituent
Wastewaters
Nonwastewaters
Common Name
CAS2 Number
Concentration
Concentration
mg/l3
or
in mg/kg3 un—
Technology
less noted as
Code4
“mg/i TCLP”;
or Technology
Code4
DOOl
Ignitable Characteristic Wastes,
except for the Section 721.121(a)(1) High TOC
Subcateqory, that are managed
in non—CWA or non—CWA—eguivalent or non—Class
I
SDWA systems.
NA
NA
DEACT and meet
DEACT and meet
Section
Section
728.148
728.148
standards; or
standards;
or
RORGS; or
RORGS;
or
CMBST
CMBST
D001
Ignitable Characteristic Wastes,
except for the Section 721.121(a) (1) High TOC
Subcateqory, that are managed in CWA or CWA—equivalent or Class
I SDWA systems
DEACT
DEACT
DOOl
High TOC Ignitable Characteristic
Liquids
Subcategory based on 35
Ill.
Adm.
Code 721.121(a) (1)
—
Greater than or equal to
10
total organic carbon.
(Note:
This subcategorv consists of nonwastewaters only.’i
NA
NA
RORGS;
or
CMBST
D002
Corrosive Characteristic Wastes that are managed
in nori-CWA or non-CWA
equivalent or non—Class
I SDWA systems.
DEACT
DEACT
and meet
and meet
Section
Section
728.148
728.148
standards
standards
D002,
0004, D005,
0006, D007,
D008, 0009,
DOlO, 0011
Radioactive high level wastes generated during the reprocessing of fuel rods.
(Note:
This aubcategory consists of nonwastewaters only.)
Corrosivity
(pH)
NA
NA
HLVIT
Arsenic
7440—38—2
NA
HLVIT
Barium
7440—39—3
NA
HLVIT
318
Cadmium
7440-43-9
HLVIT
Chromium (Total)
7440-47-3
NA
HLVIT
Lead
7439-92-1
NA
HLVIT
Mercury
7439—97-6
HLVIT
Selenium
7782—49-2
HLVIT
Silver
7440—22—4
HLVIT
0003
Reactive Suifides Subcategory based on
35
Ill. Adm.
Code 721.123(a)(5).
NA
NA
DEACT
DEACT
0003
Explosive subcateqory based on 35
Ill. Mm.
Code 721.l23(a)(6),
(a)(7),
and
(a~(8).
DEACT
DEACT
0003
Other Reactives Subcateqory based on
35
Ill. Adm. Code 721.123(a)(1).
NA
NA
DEACT
DEACT
0003
Water Reactive Subcateqory based on 35
Xli. Adm. Code 72l.123(a)(2),
(a)(3),
and (a)(4).
(Note:
This
subcategory
consists
of
nonwastewaters
only.)
DEACT
0003
Reactive Cyanides Subcategory based on 35
Iii.
Adm. Code 721.123(a) (5).
Cyanides
(Total)7
57—12—5
—-
590
Cyanides
(Amenable)7
57—12—5
0.86
30
0004
Wastes that exhibit,
or are expected to exhibit, the characteristic of
toxicity for arsenic based on the extraction procedure (EP~in SW—846 Method
1310.
Arsenic
7440-38—2
5.0
5.0 mg/l EP
Arsenic;
alternate6
7440-38—2
5.0 mg/l TCLP
standard for
nonwastewaters only.
0005
Wastes that exhibit,
or are expected to exhibit, the characteristic of
toxicity for barium based on the extraction procedure
(EP)
in SW—846 Method
1310.
Barium
7440—39-3
100
100 mg/i TCLP
0006
Wastes that exhibit,
or are expected to exhibit, the characteristic of
toxicity for cadmium based on the extraction procedure
(EP)
in SW—846 Method
1310.
Cadmium
7440—43-9
1.0
1.0 mg/i TCLP
0006
Cadmium Containing Batteries Subcateqory
(Note:
This subcateqory consists of nonwastewaters only.)
Cadmium
7440—43—9
NA
RTHRM
D007
Wastes that exhibit, or are expected to exhibit,
the characteristic of
toxicity for chromium based on the extraction procedure
CE?)
in SW-846 Metod
1310.
Chromium
(Total)
7440-47—3
5.0 mg/i TCLP
319
0008
Wastes that exhibit,
or are expected to exhibit,
the characteristic of
toxicity for lead based on the extraction procedure
(EP)
in SW-846 Method
1310.
Lead
7439—92—1
5.0 ma/i F~P
Lead;
alternate6
7439—92—1
NA
5.0 ma/l TCLP
standard for
nonwastewaters only
D008
Lead Acid Batteries Subcategory
(Note:
This standard only applies to lead acid batteries that are identified
as RCRA hazardous wastes and that are not excluded elsewhere from regulation
under the land disposal restrictions of this Part or exempted under other
regulations
(see 35
Xli. Adm. Code 726.180).).
(Note:
This subcategory consists of nonwastewaters only.)
Lead
7439-92—1
RLEAD
D008
Radioactive Lead Solids Subcategory
(Note:
These lead solids include, but are not limited to,
all
forms of lead
shielding and other elemental forms of lead.
These lead solids do not include
treatment residuals such as hydroxide sludges, other wastewater treatment
residuals, or incinerator ashes that can undergo conventional pozzolanic
stabilization,
nor do they include organo—lead materials that can be
incinerated and stabilized as ash.)
(Note:
This subcategory consists of nonwastewaters only.)
Lead
7439-92-1
MACRO
0009
Nonwastewaters that exhibit, or are expected to exhibit, the characteristic of
toxicity for mercury based on the extraction procedure
(B?)
in SW—846 Method
1310;
and contain greater than or equal to 260 mg/kg total mercury that also
contain organics and are not incinerator residues.
(High Mercury—Organic Subcateqory)
Mercury
7439—97—6
IMERC;
or
RMERC
0009
Nonwastewaters that exhibit, or are expected to exhibit, the characteristic of
toxicity for mercury based on the extraction procedure
(B?)
in SW—846 Method
1310;
and contain greater than or equal to 260 mg/kg total mercury that are
inorganic,
including incinerator residues and residues from RMERC.
(High Mercury—Inorganic Subcategory~
Mercury
7439-97-6
RMERC
D009
Nonwastewaters that exhibit, or are expected to exhibit, the characteristic of
toxicity for mercury based on the extraction procedure
(EP)
in SW—846 Method
1310;
and contain
less than 260 mg/kg total mercury.
(Low Mercury Subcategory)
Mercury
7439-97—6
0.20 mg/i TCLP
All 0009 wastewaters.
Mercur~i
7439-97—6
0.20
0009
Elemental mercury contaminated with radioactive materials.
(Note:
This subcategory consists of nonwastewaters only.)
Mercury
7439-97-6
AMLGM
320
0009
Hydraulic oil contaminated with Mercury Radioactive Materials Subcateaory.
(Note:
This subcateaorv consists of nonwastewaters only.)
Mercury
7439—97-6
IMERC
0010
Wastes that exhibit, or are expected to exhibit, the characteristic or
toxicity for selenium based on the extraction procedure
(B?)
in SW—846 Method
1310.
Selenium
7782—49—2
5.7 ma/l TCLP
Doll
Wastes that exhibit, or are expected to exhibit, the characteristic of
toxicity for silver based on the extraction procedure
(B?)
in SW—846 Method
1310.
Silver
7440—22—4
5.0 ma/i TCLP
0012
Wastes that are TC for Endrin based on the TCLP
in SW—846 Method 1311.
Endrin
72-20—8
BIODG;
or
0.13
INCIN
and meet
Section
728.148
standards
Endrin
aldehyde
7421-93-4
81000;
or
0.13
INCIN
and meet
Section
728.148
standards
0013
Wastes that
are TC for Lindane based on the TCLP in SW—846 Method 1311.
alpha—BHC
319-84-6
CARBN; or
0.066
INCIN
and meet
Section
728. 148
standards
beta-BHC
319-85-7
CARBN; or
0.066
INCIN
and meet
Section
728. 148
standards
delta-BHC
319—86-8
CARBN;
or
0.066
INCIN
and meet
Section
728. 148
standards
ganixna—BHC
(Lindane)
58—89—9
CARBN; or
0.066
INCIN
and meet
Section
728.148
standards
D014
Wastes that are TC for Methoxychlor based on the TCLP in SW-846 Method 1311.
Methoxychlor
72—43—5
WETOX or INCIN
0.18
and meet
-
Section
728.148
standards
321
0015
Wastes that are TC for Toxaphene based on the TCLP in SW—846 Method 1311.
Toxaphene
8001—35-2
31000 or INCIN
2.5
and meet
Section
728.148
standards
0016
Wastes that are TC for 2,4—D
(2,4—Dichlorophenoxyacetic acid) based on the
TCLP in SW—846 Method 1311.
94—75-7
CHOXD,
81000,
or INCIN
10
and meet
Section
728. 148
standards
2,4—0
(2,4—Dichloro-
phenoxyacetic
acid)
0017
Wastes that are TC for 2,4,5—TP (Silvex) based on the TCLP in SW—846 Method
1311.
2,4,5—TP
(Silvex)
93—72-1
CHOXD or INCIN
7.9
and meet
Section
728.148
standards
0018
Wastes that are TC for Benzene based on the TCLP
in SW-846 Method 1311 and
that are managed
in non—CWA or non-CWA equivalent or non—Class
I SDWA systems
only.
Benzene
71—43—2
0.14
10
and
meet
and
meet
Section
Section
728.148
728.148
standards
standards
D019
Wastes that are TC for Carbon tetrachloride based on the TCLP
in SW—846 Method
1311 and that are managed
in non—CWA or non-CWA equivalent or non—Class
I SDWA
systems only.
Carbon tetrachloride
56—23—5
0.057
5.0
and meet
and meet
Section
Section
728.148
728.148
standards
standards
0020
Wastes that are TC for Chlordane based on the TCLP in SW-846 Method 1311 and
that are managed in non—CWA or non—CWA equivalent or non—Class
I SDWA systems
only.
Chlordane
(alpha and
57—74—9
0.0033
0.26
gamma isomers)
and meet
and meet
Section
Section
728.148
728.148
standards
standards
0021
Wastes that are TC for Chlorcbenzene based on the TCLP
in
SW—846 Method 1311
and that are managed
in non—CWA or non—CWA equivalent or non—Class
I SDWA
systems only.
322
Chlorobenzene
108—90—7
0.057
and
meet
and
meet
Section
Section
728.148
728.148
standards
standards
0022
Wastes that are TC for Chloroform based on the TCLP in SW—846 Method 1311 and
that are managed in non—CWA or non—CWA equivalent or non—Class
I SDWA systems
only.
Chloroform
67—66—3
0.046
6.0
and meet
and meet
Section
Section
728.148
728.148
standards
standards
D02 3
Wastes that are TC for o-Cresol based on the TCLP
in SW-846 Method 1311 and
that are managed
in non-CWA or non—CWA equivalent or non—Class
I
SDWA systems
only.
o—Cresol’
95—48—7
0.11
5.6
and meet
and meet
Section
Section
728.148
728.148
standards
standards
0024
Wastes that are TC for
m—Cresoi
based
on
the
TCLP
in
SW—846 Method 1311 and
that are managed in non—CWA or non—CWA equivalent or non—Class
I SDWA systems
only.
m—Cresol
108—39—4
0.77
5.6
(difficult to
and meet
and meet
distinguish from p-
Section
Section
cresol)
728.148
728.148
standards
standards
0025
Wastes
that
are
TC
for
p-Cresol
based
on
the
TCLP
in
SW—846 Method 1311 and
that are managed in non-CWA or non—CWA equivalent or non—Class
I SDWA systems
only.
p—Cresol
106—44—5
0.77
5.6
(difficult to
and meet
and meet
distinguish from m—
Section
Section
creed)
728.148
728.148
standards
standards
0026
Wastes that are TC for Cresols
(Total) based on the TCL? in SW-846 Method 1311
and that are managed in non—CWA or non—CWA equivalent or non—Class
I SDWA
systems only.
Cresol—mixed isomers
1319—77—3
0.88
11.2
(Cresylic
acid)
and meet
and meet
(sum of
0—,
m—,
and P—
Section
Section
cresol concentrations)
728.148
728.148
standards
standards
0027
Wastes
that
are
TC
for
p-Dichlorobenzene
based
on
the
TCLP
in
SW-846 Method
1311
and
that
are
managed
in
non—CWA
or
non—CWA
equivalent
or
non—Class
I
SDWA
systems only.
323
p—Dichlorobenzene (1.4—
106—46—7
0.090
6.0
Dichlorobenzene)
and meet
and meet
Section
Section
728.148
728.148
standards
standards
0028
Wastes that are TC for 1,2-Dichloroethane based on the TCLP in SW—846 Method
1311 and that are managed
in non—CWA or non—CWA equivalent or non—Class
I SDWA
systems only.
1,2—Dichioroethane
107—06—2
0.21
6.0
and meet
and meet
Section
Section
728.148
728.148
standards
standards
0029
Wastes
that
are
TC
for
1,l—Dichloroethylene
based
on
the
TCLP
in
SW—846
Method
1311 and that are managed
in non—CWA or non—CWA equivalent or non—Class
I SDWA
systems
only.
i,1—Dichloroethylene
75—35—4
0.025
6.0
and
meet
and
meet
Section
Section
728.148
728.148
standards
standards
D030
Wastes
that
are
TC
for
2,4-Dinitrotoluene
based
on
the
TCLP
in
SW—846
Method
1311
and
that
are
managed
in
non-CWA
or
non-CWA
equivalent
or
non-Class
I
SDWA
systems only.
2,4—Dinitrotoluene
121—14—2
0.32
and meet
and meet
Section
Section
728.148
728.148
standards
standards
0031
Wastes that are TC for Heptachlor based on the TCLP in SW—846 Method 1311 and
that are managed
in non—CWA or non—CWA equivalent or non—Class
I SDWA systems
only.
Heptachlor
76—44—8
0.0012
0.066
and meet
Section
728. 148
standards
Heptachior
epoxide
1024—57—3
0.016
0.066
and
meet
and
meet
Section
Section
728.148
728.148
standards
standards
0032
Wastes
that
are
TC
for
Hexachlorobenzene
based
on
the
TCLP
in
SW—846
Method
1311
and
that
are
managed
in
non-CWA
or
non—CWA
equivalent
or
non—Class
I
SDWA
systems only.
Hexachlorobenzene
118—74—1
0.055
10
and
meet
and
meet
Section
Section
728.148
728.148
standards
standards
324
0033
Wastes that are TC for Hexachlorobutadiene based on the TCL? in SW—846 Method
1311 and that are managed
in non-CWA or non-CWA equivalent or non—Class
I SDWA
systems only.
Hexachiorobutadiene
67-68-3
0.055
and meet
and meet
Section
Section
728.148
728.148
standards
standards
0034
Wastes that are TC for Hexachloroethane based on the TCLP in SW—846 Method
1311 and that are managed
in non-CWA or non-CWA equivalent or non—Class
I SDWA
systems only.
Hexachloroethane
67—72—1
0.055
30
and
meet
and
meet
Section
Section
728.148
728.148
standards
standards
0035
Wastes
that
are
TC
for
Methyl
ethyl
ketorie
based
on
the
TCL?
in
SW—846
Method
1311
and
that
are
managed
in
non-CWA
or
non—CWA
equivalent
or
non-Class
I
SDWA
systems
only.
Methyl
ethyl
ketone
78-93—3
0.28
36
and
meet
and
meet
Section
Section
728.148
728.148
standards
standards
0036
Wastes that are TC for Nitrobenzene based on the TCLP in
SW—846 Method 1311
and that are managed
in non—CWA or non—CWA equivalent or non—Class
I SDWA
systems only.
Nitrobenzene
98—95—3
0.068
14
and meet
and meet
Section
Section
728.148
728.148
standards
standards
0037
Wastes that are TC for Pentachlorophenol based on the TCLP in SW-846 Method
1311
and
that
are
managed
in
non-CWA
or
non-CWA
equivalent
or
non—Class
I
SDWA
systems
oni~~
Pentachiorophenol
87-86—5
0.089
7.4
and
meet
and
meet
Section
Section
728.148
728.148
standards
standards
0038
Wastes
that
are
TC
for
Pyridine
based
on
the
TCLP
in
SW—846
Method
1311
and
that
are
managed
in
non—CWA
or
non—CWA
equivalent
or
non—Class
I
SDWA
systems
only.
Pyridine
110—86—1
0.014
16
and
meet
and
meet
Section
Section
728.148
728.148
standards
standards
0039
Wastes that are TC for Tetrachloroethylene based on the TCLP in SW—846 Method
325
1311 and that are managed in non-CWA or non—CWA equivalent or non—Class
I SDWA
systems only.
Tetrachloroethvlene
127—18—4
0.056
6.0
and meet
and meet
Section
Section
728.148
728.148
standards
standards
0040
Wastes that are TC for Trichloroethylene based on the TCLP in SW—846 Method
1311 and that are managed in non-CWA or non-CWA equivalent or non-Class
I SDWA
systems only.
Trichioroethylene
79—01—6
0.054
6.0
and meet
and meet
Section
Section
728.148
728.148
standards
standards
0041
Wastes that are TC for 2,4,5-Trichlorophenol based on the TCL? in SW—846
Method 1311 and that are managed
in non-CWA or non-CWA equivalent or non—Class
I SDWA systems only.
2,4,5—Trichlorophenol
95—95-4
0.18
7.4
and meet
and meet
Section
Section
728.148
728.148
standards
standards
0042
Wastes that are TC for 2,4,6-Trichlorophenol based on the TCLP
in SW—846
Method 1311 and that are managed in non—CWA or non—CWA equivalent or non—Class
I SDWA systems only.
2,4,6—Trichiorophenol
88—06—2
0.035
7.4
and meet
and meet
Section
Section
728.148
728.148
standards
standards
0043
Wastes that are TC for Vinyl chloride based on the TCLP
in SW—846 Method 1311
and that are managed in non-CWA or non—CWA equivalent or non-Class
I SOWA
systems only.
Vinyl chloride
75-01—4
0.27
6.0
and meet
and meet
Section
Section
728.148
728.148
standards
standards
FOOl,
F002,
P003, F004
& P005
P001, F002,
P003,
P004.
or F005 solvent wastes that contain any combination
of
one_or_more_of_the following spent solvents:
acetone,
benzene, n—butyl
alcohol,
carbon disulfide,
carbon tetrachloride,
chlorinated fluorocarbons,
chloroberizene.
o-cresol,
m—cresol,
p—cresol,
cyclohexanone, o—dichlorobenzene,
2—ethoxyethanol, ethyl
acetate, ethyl benzene,
ethyl ether,
isobutyl alcohol,
methanol,
methylene chloride, methyl ethyl ketone, methyl
isobutyl ketone,
nitrobenzene, 2—nitropropane, pyridine,
tetrachloroethylene, toluene,
1,1,1—
trjchloroethane,
1, 1,2—trichioroethane,
1, 1,2—trichioro- 1,2,2—trifluoro—
ethane, trichloroethylene, trichloromonofluoromethane,
or xylenes
(except as
specifically noted in other subcategories).
See further details of these
listings in
35
Ill. Adm. Code 721.131
Acetone
67—64—1
0.28
160
Benzene
71—43—2
0.14
10
1000
1000
~~00
1000
1000
P1CDOO
1UiUi~
~
1~1~10g~
aft~r~3~izzixxzIP1r
LLIIIHI
III
rr10.r1~°rn°1~
1w ~
II
I~
~
~.
I~
Lm
~P1
h h
I
L
~
to
t
I
I
I
I
I
r~
N
L
LP1
~
P1
1
I
II
~
I
I
10
0
~
IZ 10
0
~
I
I
I
II
I
I
r
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327
P006
Wastewater treatment
following processes:
(1)
on
carbon
steel;
(3)
zinc
aluminum or zinc—aluminum
associated with tin,
zinc
chemical etching and milli
Cadmium
Chromium
(Total)
cy~nides(Total)7
Cyanides
(Amenable)7
110—80—5
BIODG;
or
INCIN
2-Ethoxyethanol
INCIN
sludoes from electroolatinci onerations exceot from the
Sulfuric acid anodizing of aluminum;
(2) tin plating
~iating (segregated basis)
on carbon steel;
(4)
plating on carbon steel;
(5) cleaning or stripping
and aluminum olatina on
carbon
steel:
and
(6)
no of aluminum
7440—43—9
7440—47—3
57—12—5
0.69
2.77
~
0.19 ma/l TCLP
0.86 maIl TCLP
~Q
57—12—5
0.86
~Q
7439—92—1
7440—02—0
7440—22-4
0.69
3.98
NA
0.37 m~/lTCLP
5.0
ma/i
TCLP
0.30 mp/i TCLP
Lead
Nickel
Silver
P007
Spent
cyanide
plating
bath
Cadmium
Chromium
(Total)
Cyanides
(Total)7
Cyanides
(Amenable)’
Lead
Nickel
Silver
solutions
from electroplating operations.
7440—43—9
NA
0.19 ma/l TCLP
7440—47—3
2.77
0.86
ma/i
TCLP
57—12—5
57—12—5
0.86
30
7439—92—1
0.69
0.37 mg/i TCLP
7440—02--0
3.98
5.0 ma/l TCLP
7440—22—4
NA
0.30 ma/l TCLP
P008
Plating bath residues from the bottom of plating baths from electroplating
operations
where
cyanides
are
used
in
the
process.
Cadmium
7440—43-9
NA
0.19 m~/lTCLP
Chromium
(Total)
7440—47—3
2.77
0.86 ma/l TCLP
Cyanides (Total)1
57—12—5
1.2
590
Cyanides (Amenable)7
57—12—5
0.86
30
Lead
7439—92—1
0.69
0.37 ma/l TCLP
Nickel
7440—02—0
3.98
5.0 maIl TCLP
Silver
7440—22-4
NA
0.30 mg/i TCLP
P009
Spent
stripping
and
cleaning
bath
solutions
from
electroplating
operations
where cyanides are used in the process.
Cadmium
7440—43-9
0.19 ma/l TCLP
Chromium
(Total)
7440—47—3
2.77
0.86 mg/i TCLP
Cyanides (Total)7
57-12—5
Cyanides
(Amenable)1
57-12—5
0.86
30
-
Lead
7439—92—1
0.69
0.37 mg/i TCLP
Nickel
7440—02—0
3.98
5.0 ma/l TCLP
Silver
7440—22—4
0.30 ma/l TCLP
FO10
Quenching
bath
residues
from
oil
baths
from
metal
heat
treating operations
where cyanides are used in the process.
1.2
0.88
590
NA
Cyanides
(Total)7
57—12—5
57—12—5
Cyanides
(Amenable)’
POll
Spent
cyanide
solutions
from
salt
bath
pot
cleaning
from
metal
heat
treating
operations.
Cadmium
Chromium
(Total)
7440—43—9
7440-47-3
NA
2.77
0.19 ma/i TCLP
0.86 mg/l TCLP
____________________
57—12—5
_______________________
57—12—5
____
7439—92—1
_______
7440—02—0
_______
7440—22—4
FO12
Quenching wastewater treatment sludges from
where cyanides are used in the process.
Cadmium
7440—43—9
Chromium
(Total)
7440—47—3
Cyanidea
(Total)7
57—12—5
Cyanides
(Amenable)7
Lead
Nickel
1.2
0.86
0.69
3.98
NA
57—12—5
0.86
7439—92—1
_____
7440—02—0
____
590
30
0.37 mg/i TCLP
5.0 ma/l TCLP
0.30 mg/i TCLP
30
0.69
0.37
ma/l
TCLP
3.98
5.0
m~/l TCLP
Silver
7440-22—4
0.30 ma/l TCLP
FO19
Wastewater treatment sludges
from the chemical conversion coating of aluminum
except
from
zirconium
phosphating
in
aluminum
can
washing
when
such
phosphating
is
an
exclusive
conversion
coating
process.
Chromium
(Total)
7440—47—3
2.77
0.86 ma/l TCLP
Cyanides
(Total)7
57—12—5
1.2
590
Cvanides
(Amenable)7
57—12—5
0.86
30
P020,
P021,
F022,
F023,
P026
Wastes (except wastewater and spent carbon from hydrogen chloride
purification)
from the production or manufacturing use
(as a reactant,
chemical intermediate,
or component in
a formulating process) of:
(1) tn— or
tetrachlorophenol, or
of intermediates used to produce their pesticide
derivatives, excluding wastes from the production of Hexachlorophene from
highly purified 2,4,5—tnichlorophenol
(i.e.,
F020);
(2) pentachiorophenol,
or
of intermediates used to produce its derivatives (i.e.,
F021);
(3)
tetra—,
penta—,
or hexachlorobenzenes under alkaline conditions
(i.e.,
F022).
Wastes (except wastewater and spent carbon from hydrogen chloride
purification)
from
the
production
of
materials
on
equipment previously used
for the production or manufacturing use
(as a reactant,
chemical intermediate,
or component in a formulating process)
of:
(1) tn— or tetrachiorophenols,
excluding wastes from equipment used only for the production of Hexachloro—
p~enefrom highly purified 2,4,5—trichlorophenol (P023);
(2) tetra—~penta-,
or hexachioroberizenes under alkaline conditions
(i.e.,
P026).
HxCDD5
(All Hexachloro—
NA
0.000063
0.001
dibenzo-p-dioxins)
HxCDFe
(All Hexachloro—
0.000063
0.001
dibenzofurans)
PeCDD5
(All Pentachloro—
NA
0.000063
0.001
dibenzo—p-dioxins)
PeCDFs
(All Pentachloro-
NA
0.000035
0.001
dibenzofurans)
TCDDS
(All Tetrachloro—
NA
0.000063
0.001
dibenzo-~—dioxins)
TCDF5
(All Tetrachloro—
NA
0.000063
0.001
dibenzofurans)
2,4.,5—Trichlorophenoi
95—95—4
0.18
7.4
2,4,6—Tnichlorophenol
88—06—2
0.035
7.4
2,3,4,6—Tetrachloro—
58—90—2
0.030
7.4
phenol
328
Cyanides
(Total)’
qyanides
(Amenable)7
Lead
Nickel
Silver
metal
heat treatina operations
NA
2.77
1.2
0.19 mall TCLP
0.86 ma/i TCLP
590
329
Pentachlorophenol
87—86—5
0.089
7.4
P027
iiscarded unused
formulations contianing tn—,
tetra—,
or pentachlorophenol or
discarded unused
formulations
containing
compounds
derived
from
these
chloro—
phenols.
(This listing does not include formulations containing hexachloro-
~hene synthesized from prepunified 2,4.5-trichlorophenol as the sole
component. I
HxCDDø
(All Hexachloro—
~
0.000063
0.001
dibenzo-p-dioxins)
HxCDF8
(All Hexachloro-
~
0.000063
0.001
dibenzofurans)
PeCDDs
(All Pentachloro—
~
0.000063
0.001
dibenzo-p-dioxins)
PeCDFB (All Pentachloro-
~th
0.000035
0.001
dibenzofurans)
TCD1~s (All Tetrachloro-
N~
0.000063
0.001
dibenzo-p—dioxins)
TCDFs
(All
Tetrachloro—
i~
0.000063
0.001
dibenzofurans)
2.4,5—Trichlorophenol
95—95—4
0.18
7.4
2,4,6—Trichiorophenol
88—06—2
0.035
7.4
2,3,4,6—Tetrachioro—
58—90—2
0.030
7.4
phenol
Pentachiorophenol
87—86—5
0.089
7.4
P028
Residues resulting from the
incineration
or
thermal
treatment
of
soil
contaminated
with
U.S.
EPA
hazardous
waste
numbers
F020,
F021,
F023,
P026,
P027.
HxCDD5
(All Hexachioro—
~
0.000063
0.001
dibenzo—p-dioxins)
HxCDFs
(All Hexachloro—
~
0.000063
0.001
dibenzofurans)
PeCDDa
(All Pentachloro—
~
0.000063
0.001
dibenzo—p—dioxins)
PeCDFs
(All Pentachloro—
NA
0.000035
0.001
dibenzofurans)
TCDDs
(All Tetrachioro—
NA
0.000063
0.001
dibenzo—p—dioxins)
TCDFS
(All Tetrachloro—
NA
0.000063
0.001
dibenzofurans)
2,4,5—Trichlorophenol
95—95—4
0.18
7.4
2,4,6—Trichlorophenol
88—06-2
0.035
7.4
2,3,4,6—Tetrachloro—
58—90-2
0.030
7.4
phenol
Pentachlorophenol
87—86-5
0.089
7.4
P024
Process wastes,
including but not limited to, distillation residues,
heavy
ends,
tarB,
and reactor clean—out wastes,
from the production of certain
chlorinated aliphatic hydrocarbons by free radical catalyzed processes.
These
chlorinated aliphatic hydrocarbons are those having carbon chain lengths
ranging from one to and including five,
with varying amounts and positions of
chlorine substitution.
(This
listing does not
include wastewaters, wastewater
treatment sludges,
spent catalysts,
and wastes
listed
in
35
Xli.
Adin.
Code
721.131 or 721.132.)
All F024 wastes
NA
INCIN
INCIN
2—Chloro—1,3—butadiene
126—99—8
0.057
0.28
3-Chloropropvlene
107-05—1
0.036
30
l,l—Dichloroethane
75—34—3
0.059
6.0
1,2—Dichloroethane
107—06—2
0.21
6.0
330
1,2—Dichloropropane
78-87—5
0.85
cis—1,3—Dichloro-
10061—01—5
0.036
18
propylene
trane—1,3—Dichloro—
10061—02—6
0.036
propylene
bis(2—Ethylhexyl)
117—81—7
0.28
phthalate
Hexachloroethane
67-72—i
0.055
Chromium (Total)
7440—47—3
2.77
0.86 ma/l TCLP
Nickel
7440—02—0
3.98
5.0 mg/I TCLP
F02 5
Condensed light ends from the production of certain chlorinated aliphatic
hydrocarbons,
by free radical catalyzed processes.
These chlorinated
aljphatic hydrocarbons are those having carbon chain lengths ranging from one
to and including five, with varying amounts and positions of chlorine
substitution.
P025
—
Light Ends Subcateaory
Carbon tetrachioride
56—23—6
0.057
6.0
Chloroform
67—66—3
0.046
6.0
1~2—Dichloroethane
107—06—2
0.21
6.0
1,l—Dichloroethylene
75—35—4
0.025
6.0
Methylene chloride
75—9—2
0.089
30
1,1,2—Trichloroethane
79—00—5
0.054
6.0
Trichloroethylene
79—01—6
0.054
6.0
Vinyl chloride
75—01—4
0.27
6.0
FO25
Spent filters and filter aids,
and spent desiccant wastes from the production
of
certain
chlorinated
aliphatic
hydrocarbons,
by
free radical catalyzed
processes.
These chlorinated aliphatic hydrocarbons are those having carbon
chain lengths ranging from one to and including
five,
with varying amounts and
positions of chlorine substitution.
P025
—
Spent Filters or Aids and Desiccants Subcategory
Carbon tetrachloride
56—23—5
0.067
6.0
Chloroform
67—66—3
0.046
6.0
Hexachlorobenzene
118—74—1
0.055
10
Hexachlorobutadiene
87—68—3
0.055
5.6
Hexachloroethane
67—72—1
0.055
30
Methyiene chloride
75—9—2
0.089
30
1,1,2—Trichloroethane
79—00—5
0.054
5.0
Trichloroethylene
79—01—6
0.054
6.0
Vinyl chloride
75—01—4
0.27
6.0
P037
Petroleum refinery primary oil/water/solids separation sludge—Any sludge
generated from the gravitational separation of oil/water/solids during the
storage or treatment of process wastewaters and oily cooling wastewaters from
petroleum refineries.
Such sludges include, but are not limited to,
those
generated in:
oil/water/solids separators;
tanks and impoundments; ditches
and other conveyances;
sumps;
and stormwater units receiving dry weather flow.
Sludge generated in stormwater units that do-not receive dry weather
flow,
sludges generated from non—contact once—through cooling waters segregated for
treatment from other process or oily cooling waters, sludges generated in
agressive biological treatment units
as defined in 35
Ill.
Adrn. Code
721.131(b)(2)
(including sludaes generated
in one or more additional units
after wastewaters
have been treated
in agressive biological treatment units)
and K05l wastes are not included
in this
listing.
Acenaphthene
83—32—9
0.059
NA
Anthracene
120—12—7
0.059
3.4
Benzene
71—43—2
0.14
10
Benz(a)anthracene
56—55—3
0.059
331
Benzo(a)pyrene
bia (2—Ethylhexyl)
phthalate
Chrvsene
Bi—n—butyl phthaiate
Ethylbenzene
Fluorene
Naphthalene
Phenanthrene
Phenol
Pvrene
Toluene
Xylenes—mixed isomers
(sum of
0—,
m—,
and p—
xylene concentrations)
Chromium
(Total)
Cyanidea
(Total)7
P038
Petroleum refinery secondary (emulsified) oil/water/solids separation sludge
or float generated from the physical or chemical separation of
oil/water/solids
in process wastewaters and oily cooling wastewaters from
petroleum refineries.
Such wastes include, but are not limited to,
all
sludges and floats generated
in:
induced air floatation
(IAF)
units, tanks
and impoundments, and
all sludges generated in DAF units.
Sludges generated
in stormwater units that do not receive dry weather flow,
sludges generated
from non—contact once—through cooling waters segregated
for treatment from
other process or oily cooling waters,
sludges and floats generated in
aaressive biological treatment units
as defined
in
35
Ill.
Adm. Code
72l..131(b)(2)
(including sludges and floats generated in one or more
additional units
after wastewaters have been treated
in agressive biological
units)
and P037, K048,
and K051 are not
included in this listina.
Benzene
71—43-2
0.14
10
Benzo(a)pyrene
50—32—8
0.061
3.4
bis(2—Ethylhexyl)
117—81—7
0.28
28
phthalate
Chrysene
218—01—9
0.059
3.4
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84—74—2
0.057
28
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100—41—4
0.057
10
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86—73—7
0.059
NA
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91—20—3
0.059
5.6
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85—01—8
0.059
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108—95—2
0.039
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129-00-0
0.067
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108—88—3
0.080
10
Xylenes—mixed isomers
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0.32
30
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Chromium
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_________
____
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590
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F02l,
P022, F026,
F027, or
P028.1.
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100—41—4
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2.77
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0.69
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NA
Lead
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Lead
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Cadmium
Chromium
Cyanides
Cyanides
Fluoride
Lead
Mercury
7440—43—9
7440—47—3
57—12—5
57—12—5
16964—48—8
7439—92—1
7439—97—6
7440—02—0
7782—49—2
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8496—25—8
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7440—62—2
0.69
2.77
1.2
0.86
35
0.69
0.15
3.98
0.82
0.43
14
1.4
4.3
0.19
0.86
ma/l
mali
TCLP
TCLP
590
NA
NA
0.37 ma/l TCLP
0.025 mall
TCLP
5.0 mg/i TCLP
0.16 mg/i TCLP
0.30 mg/i TCLP
NA
NA
NA
1(001
Bottom sediment sludge from
the
treatment
of
wastewaters
from wood preserving
processes that use creosote or pentachlorophenol.
91-20—3
0.059
5.6
Naphthalene
Pentachlorophenol
87-86—5
0.089
7.4
85—01—8
0.059
Phenanthrene
Pyrene
129-00-0
0.067
8.2
Toluene
108—88—3
0.080
10
Xylenes—mixed isomers
1330—20—7
0.32
30
7439—92—1
0.69
0.37 mg/I TCLP
(sum of o—, m—,
and p—
xylene concentrations)
Lead
1(002
Wastewater
treatment
sludge from the production of chrome yellow and orange
piaments.
Chromium
(Total)
7440—47—3
2.77
0.86 mg/i TCLP
Lead
1(003
7439—92—1
0.69
0.37 mg/i TCLP
Wastewater treatment sludge from the production of molybdate orange pigments.
Chromium
(Total)
7440—47-3
2.77
0.86 mg/l TCLP
Lead
1(004
7439—92—1
0.69
0.37 mg/i TCLP
Wastewater treatment sludge from the production of zinc yellow pigments.
Chromium
(Total)
7440—47-3
2.77
0.86 rng/l TCLP
7439—92-i
0.69
0.37 mg/l TCLP
Lead
1(005
Wastewater treatment sludge from the production of chrome green pigments.
Chromium
(Total)
7440—47—3
2.77
0.86 mg/i TCLP
Lead
Cyariides
(Total)7
7439—92—1
0.69
0.37 mg/I TCLP
57—12—5
1.2
590
1(006
Wastewater treatment sludge from the production of chrome oxide green pigments
(anhydrous).
Chromium
(Total)
7440—47—3
2.77
0.86 mg/i TCLP
7439—92—1
0.69
0.37 mg/i TCLP
Lead
1(006
Wastew&-’~
~
(hydrated).
Chromium
(Total)
Lead
(Total)
(Total)’
(Amenable)’
Nickel
Selenium
Silver
Sulfide
Thallium
Vanadium
sludge from the production of chrome oxide green pigments
0.86
mall
TCLP
7440—47—3
2.77
7439—92—1
0.69
NA
337
1(007
Wastewater treatment sludge from the production of iron blue pigments.
Chromium (Total)
7440—473
7439—92—1
2.77
0.69
fl-~
mg/i
ma/l
Lead
Cyanides
(Total)7
57-12—5
-
-
—
-
TCLP
0.37
590
TCLP
1(008
Oven residue
Chromium
Lead
from the production of chrome
(Total)
7440—47—3
7439—92—1
oxide
green
2.77
0.69
‘r~
4
rm,~T~*—
a
-
0. 86 ma/I TCLP
0. 37 ma/i TCLP
K009
Dis~411~4’~
‘~“~
from the
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of
Q1d~h~7~
from
~+h~r1~y~
Chloroform
67—66—3
0.046
6.0
1(010
Distillation
side cuts
from
the production of acetaldehyde from ethylene.
Chloroform
67—66-3
0.046
6.0
1(011
Bottom stream from the wastewater
stripper
in
the
production
of
acrylonitrile.
Acetonitrile
75—05-8
5.6
18
Acrylonitriie
107—13—1
0.24
84
Acrylamnide
79-06—1
19
23
Benzene
71-43-2
0.14
10
Cyanide
(Total)
57—12-5
1.2
590
1(013
Bottom stream from the acetonitrile column
in
Acetonitrile
75-05—8
Acrylonitriie
107—13-1
Acrylamide
79-06—1
Benzene
71-43-2
Cyanide (Total)
57-12—5
acrylonitriie.
Acetonitrile
Acrvlonitrile
Acrylaniide
Benzene
Cyanide
(Total)
(difficult to
distinguish from benzo-
(k)
fluoranthene)
Benzo(k)fluoranthene
(difficult to
distinguish from benzo—
b)fluoranthene)
Phenanthrene
Toluene
Chromium (Total)
3.4
6.0
6.8
the production of
5.6
0.24
19
0.14
1.2
1(014
Bottoms from the acetonitrile purification column in the production of
acrylonitrile.
1.8
84
23
10
590
75—05—8
1.8
107—13—1
0.24
79—06—1
71—43—2
0.14
1Q
57—12—5
j.~
1(015
Still
bottoms
from
the
distillation
of
benzyl
chloride.
Anthracene
120—12—7
0.059
Benzal chloride
98—87-3
0.055
Benzo(b)fluoranthene
205—99—2
0.11
Nickel
207—08—9
0.11
6.8
85—01—8
0.059
108—88—3
0.080
10
7440—47—3
7440—02—0
2.77
3.98
0.86 mg/i TCLP
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1(022
Distillation bottom tars from
Toluene
Acetophenone
Diphenylamine
(difficult
to distinguish from
diphenylnitrosarnine)
Diphenylnitrosainine
(difficult to
distinguish from
djphenyianiine)
Phenol
Chromium (Total)
Nickel
K02 3
Distillation light ends from
naphthalene.
Phthalic anhydride
(measured
as
Phthalic
acid or Terephthalic
acid)
Phthalic
anhydride
the production
100—21—0
85—44—9
of
‘ohthalic
anhvdride
from
0.055
0.055
28
28
1(024
Distillation bottoms from
naphthaiene
Phthalic anhydride
(measured
as
Phthalic
acid or Terephthalic
acid)
Phthaiic anhydride
1(025
nist(llation
bottoms
from
-
the production of
nitrobenzene by the nitration of
benzene.
LLEXT fb SSTRP
INCIN
fb CARBN;
or
INCIN
1(026
Stripping still tails from the production of methyl ethyl pyridines.
NA
r~h
INCIN
INCIN
1(027
Centrifuae and distillation residues from the toluene diisocvanate production.
CARBN;
or
CMBST
INCIN
1, 1-Dichioroethane
trans—i,2—Dichioro-
ethylene
Hexachlorobutadiene
Hexachioroethane
Pentachloroethane
1,1, 1,2—Tetrachloro—
ethane
1, 1,2,2—Tetrachloro—
ethane
the production of phenol or acetone from cumene
108—88—3
0.080
10
96—86—2
0.010
9.7
122—39—4
0.92
13
86—30—6
0.92
j~
108—95—2
0.039
.~i
7440-47—3
7440—02—0
2.77
3.99
0.86 mg/l TCLP
5.0 mg/i TCLP
th~
r~roduc-~tion
of
t~hth~1i~~rthvdrids
from
100—21—0
0.055
28
85—44—9
0.055
1(028
Spent catalyst from the hydrochiorinator reactor in the production of 1,1,1—
trichioroethane
75—34—3
156—60—5
87—88—3
67—72—1
76—01—7
630—20—6
0.059
0.054
0.055
0.055
NA
0.057
6.0
30
5.6
30
6.0
6.0
6.0
79—34—6
0.057
340
Tetrachioroethvlene
1,1,1—Trichloroethane
1,1,2—Trichioroethane
Cadmium
Chromium(Total)
Lead
Nickel
K029
Waste from the product
steam
stripper in the production of 1,l,1—trichloro-
ethane.
Chloroform
67-66—3
0.046
~Q
1,2-Dichioroethane
107—06-2
75—35—4
71—55—6
75—01—4
0.21
0.025
0.054
0.27
6.0
6.0
6.0
6.0
1,1—Dichioroethylene
1,l,l—Trichloroethane
Vinyl chloride
1(030
Column bodies or
heavy ends
and perchloroethyle~”~’
-
o—Dichlorobenzene
p—Dichlorobenzene
Hexachlorobutadiene
Hexachloroethane
exachloropropylene
entachlorobenzene
entachloroethane
1,2,4, 5—Tetrachioro—
benzene
etrachioroethylene
1,2,4—Trichlorobenzene
1(031
By-product salts generated
Arsenic
in the production of MSMA and cacodylic acid.
7440—38—2
5.0 mgI 1 TCLP
1(032
Wastewater treatment
sludge from the production of chiordane.
Hexachiorocyclopenta—
77—47—4
0.057
2.4
diene
Chlordane
(alpha and
aamma
isomers)
Heptachlor
Heptachior epoxide
57—74—9
0.0033
0.26
76—44—8
0.0012
0.066
1024—57—3
0.016
0.066
1(033
Wastewater and scrub water from the chlorination of cyclopentadiene in the
production of chiordane.
Hexachiorocyclopenta-
77-47-4
0.057
24
diene
1(034
Filter solids from the filtration of hexachlorocyclopentadiene in the
production of chlordane.
77—47—4
0.057
2.4
Hexachlorocyclopenta—
diene
1(035
Wastewater treatment sludges generated in the production of creosote.
Acenaphthene
83—32—9
NA
3.4
127—18—4
0.056
71—55—6
0054
Q~Q
79—00—5
0.054
~Q
7440-43—9
0.69
7440—47—3
7439—92—1
7440—02-0
2.77
0.69
3.98
0.86 mg/i TCLP
0.37 mg/i TCLP
5.0 ma/i TCLP
from
the
combined
production
of
trichioroethylene
95—50—1
0.088
106—46-7
0.090
87—68—3
0.055
67—72—1
0.055
~Q
1888—71—7
~Q
608—93—5
~Q
76—01—7
~Q
95—94—3
0.055
3~
127—18—4
0.056
~Q
120—82—1
0.055
j~
Anthracene
120—12—7
3.4
341
Benz(a)anthracene
56—55-3
0.059
3.4
Benzo(a)pyrene
50—32-8
0.061
3.4
Chrysene
218-01-9
0.059
3.4
o—Cresol
95—48—7
0.11
5.6
m—Cresol
108—39—4
0.77
5.6
(difficult to
distinguish from p-
creaoj)
p—Cresol
106—44—5
0.77
(difficult to
distinguish from m-
cresol)
Dibenz(a,h)anthracene
53—70—3
NA
8.2
Fluoranthene
206—44-0
0.068
3.4
Fiuoreno
86-73—7
NA
3.4
Indeno(1,2..3—cd)pyrene
193—39-5
NA
3.4
Naphthaiene
91-20—3
0.059
5.6
Phenanthrene
85-01—8
0.059
5.6
Phenol
108—95—2
0.039
6.2
Pyrene
129—00-0
0.067
8.2
1(036
Still bottoms from toluene reclamation distiilaiton in the production of
disulfoton.
Disuifoton
298—04—4
0.017
6.2
1(037
Wastewater
treatment
sludges
from the production of disulfoton.
Disulfoton
298-04—4
0.017
6.2
Toiuene
108-88—3
0.080
10
1(038
Wastewater from the washing and stripping of phorate production.
Phorate
298-02—2
0.021
4.6
1(039
Filter cake from the filtration of diethyiphosphorodithioic acid in the
production of phorate.
NA
CARBN;
or
CMBST
INCIN
1(040
Wastewater treatment sludge from the production of phorate.
Phorate
298—02-2
0.021
4.6
1(041
Wastewater treatment sludge from the production of toxaphene.
Toxaphene
8001-35—2
0.0095
2.6
1(042
Heavy ends or distillation residues from the distillation of tetrachioro—
benzene in the production of 2,4,5—T.
o—Dichlorobenzene
95-50—1
0.088
6.0
p-Dichlorobenzene
106—46-7
0.090
6.0
Pentachlorobenzene
608—93-5
0.055
10
l,2,4,5—Tetrachloro—
95—94—3
0.055
14
benzene
l,2,4—Trichiorobenzene
120—82—1
0.055
19
1(043
2,6—Dichlorophenoi waste from the production of 2,4—D.
2,4—Dichlorophenol
120—83—2
0.044
14
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a’
N) N)
N) ‘0H
•
OA’
0IC.iIa’C~0(4070’a’a’~
~0).
03.
a’
00
a’
o
a’
-o
7)
0
0’
CD
F--
ft
n-
CD
Cl
0
0-.
Cl
C)
ft
F-
0
Ti
-4
A
1:,)
to
I
‘0
N)
I
H
HHW’0HN)N)’~0
(40UC-~’.D0H1--’0O
(4CDlItAta’07I03~’
OlON)l
I IAIF--
I(0,~0(4A0(_a’.0Ti
N)CDI
I’0AC--’l0’
0107t_aIIIN)I
IC_a
U1O’.D
(DO
—~
5
I-I
pt
c-C-
C--
0
C-ft
~
Ti’
Pt
0
a’
‘.0
0
Ti
Q00000000.
(4000000H0
N)(0U1010a’01AU
0’0’001CD’0
‘.0
Ut
H
F-
a
Pt
Ti
n-
0.’
Cl
C-’-
g-
I-ft
Cl
o
.
~
(4IH01U(4(-.’~(4F-.’(4
010
0-
O’ta’AAA
A
0
B
H
ft
n’
1-3
t~
‘0
C.)
A
0’
H
‘.00’
HHH’.O
N)
010
(4l-.0U
O
lcD
C.)CD0’I
I
‘.01
a’IIU1
a)
A’.L)
I-lAO
N)
IC.)
(4AC’I
I
Cal
mIIH
H
Ui
IC-”-t
I_a
o
00
D000
O
00
H000
U
U1U
OUit0C0
U
0101
UO0)
H
IC—’H
HHO’O’
‘.0
lAO
00~
00
C)
It)
Cl
Ut
ft
a
US
001
rtTi’
CD
ClIn
P
(OS
0-Ti
P.
TiUt
H
ftC
n-P.
5
CD
C-is
UI
0
Cl
90
ClCl
H
ftPt
C-ft
OS
TiCl
I-ft
Pt
In
F--n-
TiCD
~.Ut
~ft
Pt
ClTi
OP.
B
0
0
Ti
ft
S
F--
Ti
0010
.‘.D•
(400)
-.4
a’
39
H
I-.’
~3
1-3
0
0
t
~-4
‘-0
‘0
xylene.
Phthalic anhydride
(measured
as
Phthalic
acid or erephthalic
acid~
Phthalic anhydride
100—21—0
0.055
85—44—9
0055
28
28
1(094
Distillation bottoms from
xvleae.
Phthalic anhydride
(measured as Phthalic
acid or Terephthalic
acid)
Phthaiic
anhydride
1(095
Distillation bottoms from
Hexachioroethane
Pentachloroethane
1,1,1,2—Tetrachloro—
ethane
1,1,2,2—Tetrachloro—
ethane
Tetrachioroethylene
1, 1 ,2—Trichioroethane
Trichloroethvlene
1(096
Heavy ends from the heavy
ethane.
m—Dichiorobenzene
Pentachioroethane
1,1, 1,2—Tetrachioro—
ethane
1,
1L2
,2—Tetrachloro-
ethane
Tetrachioroethylene
1,2,4—Trichlorobenzene
1, 1, 2—Trichloroethane
Trichioroethylene
chlordane.
Chiordane
(alpha and
gamma
isomers)
Heptachbr
Heptachior epoxide
Hexachlorocyc lopenta—
diene
the
production
67—72—1
76—01—7
630—20—6
6.0
6.0
6.0
6.0
6.0
19
6.0
6.0
K098
Untreated process wastewater from the production of toxaphene.
Toxaphene
8001—35—2
0.0095
2.6
1(099
Untreated wastewater from the production of 2,4—D.
2,4—Dichborophenoxy—
94—75—7
0.72
acetic acid
HxCDDs
(All Hexachioro-
~
0.000063
dibenzo—p-diox ins)
347
the
Iroduction
of
-chthalic arthvdride from ortho—
100—21—0
0.055
85—44—9
0.055
_____
28
______
28
of
1,1,1—trichioroethane.
0.055
0.055
0.057
_____
6.0
79—34—6
0.057
127—18—4
79—00—5
79—01—6
0.056
0.054
0.054
ends column from the production of
6.0
6.0
6.0
1,1,i—trichloro—
541—73—1
76—01—7
630—20—6
0.036
0.055
0.057
79—34—6
0.057
127—18—4
120—82—i
79—00—5
79—01—6
0.056
0.055
0.054
0.054
K09 7
Vacuum stripper discharge from the chlordane chlorinator in the production of
57—74—9
0.0033
76—44—8
1024—57—3
77—47—4
0. 0012
0.016
0.057
0.26
0.066
0.068
2.4
10
0.001
348
Aniline
Benzene
2, 4-Dinitrophenol
Nitrobenzerie
Phenol
çy~nidee (Total’)7
0. 000063
0. 000063
0.000035
0.000063
0.000063
from
n~t~oben~”~
or
~-‘~
0.81
0.14
0.12
0.068
0.039
1.2
0.001
0.001
0.001
0.001
0.001
me
oroduc-~tiori.
14
10
160
14
6.2
590
1(105
Separated aaueous stream from the reactor product washing step in the
production of chlorobenzenes.
Benzene
71—43—2
0.14
10
Chiorobenzene
108—90-7
0.057
6.0
2—Chlorophenol
95—57—8
0.044
5.7
o-Dichlorobenzene
95—50—1
0.088
6..0
p-Dichlorobenzene
106—46-7
0.090
6.0
HxCDFs
(All Hexachboro—
NA
NA
NA
NA
NA
dibenzofurans)
PeCDDa
(All Pentachioro-
dibenzo-p-dioxins)
PeCDFs
(All Pentachioro—
dibenzofurans)
TCDDS
(All Tetrachioro—
dibenzo-p-dioxins)
TCDF5
(All Tetrachioro-
dibenzofurans)
1(100
Waste leaching solution from acid leaching of emission control dust or sludge
from Becondarv lead smelting.
Cadmium
7440—43—9
0.69
0.19 mg/i TCLP
Chromium (Total)
7440-47—3
2.77
0.86 ma/i TCLP
Lead
7439—92—1
0.69
0.37 mg/i TCLP
1(101
Distillation tar residues from the distillation of aniline-based compounds in
the production of veterinary pharmaceuticals from arsenic or organo—arsenic
compounds.
o—Nitroaniiine
88—74—4
0.27
14
Arsenic
7440—38—2
1.4
5.0
mci/I TCLP
Cadmium
7440—43—9
0.69
NA
Lead
7439—92—1
0.69
NA
Mercury
7439—97—6
0.15
NA
1(102
Residue from the use of activated carbon f-—decolorization in the production
of veterinary pharmaceuticals from arsenic or organo—arsenic compounds.
o—Nitrophenol
88—75—5
0.028
13
Arsenic
7440—38—2
5.0 mci/i TCLP
Cadmium
7440—43—9
0.69
NA
Lead
7439—92—1
0.69
NA
Mercury
7439—97—6
0.15
NA
1(103
Process residues from aniline extraction from the production of aniline.
Aniline
62—53—3
0.81
14
Benzene
71—43—2
0.14
10
2,4-Dinitrophenol
51—28—5
0.12
160
Nitrobenzene
98—95—3
0.068
14
Phenol
108—95—2
0.039
6.2
------
—
--
-
-
--
-
1(104
Combined
‘-‘-.-~~-‘~-~--
streams
‘—~nerated
________
62—53—3
________
71—43—2
-
51—28—5
_____________
98—95—3
_______
108—95—2
___________________
57—12—5
349
Phenol
108—95—2
0.039
6.2
2, 4,5—Trichiorophenol
95—95—4
88—06—2
0.18
0.035
7.4
7.4
2,4,6—Trichiorophenoi
K106
K106
(wastewater treatment sludge from the mercury cell process in chlorine
production)
nonwastewaters
that contain
greater than
or
eaual to
260 ma/ko
total mercury.
Mercury
7439—97-6
NA
RMERC
1(106
K106
(wastewater treatment sludae from the mercury cell process
in
chlorine
production)
nonwastewaters that contain less than 260 mg/kg total mercury that
are residues from
RI4ERC.
Mercury
7439—97-6
NA
0.20 mg/i TCLP
1(106
Other 1(106 nonwastewaters that contain less than 260 mg/kg total mercury and
are not residues from RI4ERC.
Mercury
7439—97—6
0.025 maIl
TCLP
1(106
All Kl06 wastewaters.
Mercury
7439-97—6
0.15
NP’.
1(107
Column
bottoms
from
product
separation
from
the
production
of
1,1—dimethyl-
bycirazine
(UDMH)
from carboxylic acid hydrazides.
INCIN;
or
INCIN
CHOXD
fb
CARBN; or
BIODG fb CARBN
K108
Condensed column overheads from product separation and condensed reactor vent
gases from the production of 1,1—dimethyihydrazine
(UDMH)
from carboxyljc acid
hydrazides.
NA
INCIN; or
INCIN
CHOXD
fb
CARBN; or
BIODG fb CARBN
1(109
Spent filter cartridges from product purification from the production of
1,1—
dimethylhydrazine
ItJDMH)
from carboxylic acid hydrazides.
INCIN;
or
INCIN
CHOXD fb
CARBN; or
BIODG fb CARBN
KilO
Condensed column overheads from intermediate separation from
1.1—dimethvihvdr~~rt~
(UDMB) from
~‘viic acid hv~~
INCIN;
or
CROXD
fb
CARBN;
or
BIODG fb CARBN
1(111
Product washwaters from the production of dinitrotoluene via nitration of
toluene
the production of
INCIN
350
2,4—Dinitrotoluene
121—1—i
0.32
140
2,6—Dinitrotoluene
606—20-2
0.55
1(112
Reaction by—product
water
from the drying column in the production
of
toluenediamine
via
hydrogenation
of
dinitrotoluene.
NA
INCIN; or
INCIN
CHOXO
fb
CARBN;
or
BIODG
fb CARBN
1(113
Condensed
liciuid light ends from the purification of toluenediaxnine
in the
production of toluenediaxnine via hydrogenation of dinitrotoluene.
NA
CPRBN; or
CMBST
INCIN
______
__________
3.98
__________
CARBN;
or
_____
INCIN
1(116
Organic condensate from the solvent recovery column
in the production of
toluene diisocyanate via phosgenation of toluenediamine.
NA
NA
CARBN;
or
CHEST
INCIN
1(117
Wastewater
from
the
reactor
vent
gas
scrubber
in
the
production
of
ethylene
dibromide via bromination of ethene.
Methyl bromide (Bromo—
74—83—9
0.11
methane)
Chloroform
67—66—3
0.046
6.0
Ethylene dibromide
(1,2—
106—93—4
0.028
15
Dibromoethane’)
K118
Spent
absorbent
solids
from
purification
of
ethylene
dibrornide
in
the
production of ethylene dibromide via bromination of ethene.
Methyl bromide
(Bromo—
74-83—9
0.11
15
methane)
Chloroform
67—66-3
0.046
6.0
Ethylene dibromide (1,2—
106—93—4
0.028
15
Dibromoethane
1(123
Process wastewater (including supernates,
filtrates,
and washwaters)
from the
production
of
ethylenebisdithiocarbamic
acid
and
its
salts.
INCIN;
or
INCIN
CHOXD
fb
(BIODG or
CARBN)
1(114
Vicinals from the purification of toluenediamine in the production of
toluenediamine via hydrogenation of dinitrotoluene.
or
CMBST
NA
NA
CARBN;
INCIN
1(115
Heavy
ends
from
the
purification
of
toluenediamine
in
the
production
of
toluenediamine
via hydrogenation
of dinitrotoluene.
Nickel
7440—02—0
li~
5.0
ma/l
CMBST
TCLP
351
1(124
Reactor vent scrubber water from the production of ethylenebisdithiocarbamic
acid and
its
salts.
INCIN;
or
INCIN
CHOXO fb
(BIODG or
CARBN)
1(125
Filtration,
evaporation,
and centrifugation
solids from the production
of
ethylenebisdithiocarbamic
acid and its salts.
INCIN;
or
INCIN
CHOXD fb
(BIODO or
CARBN)
K126
Baghouse
dust
and floor sweepings
in milling
and
pachaging
operations
from
the
production
or
formulation
of
ethylenebisdithiocarbamic
acid
and
its
salts.
NA
NA
INCIN; or
INCIN
CHOXD
fb
(BIODG or
CARBN)
Kl3l
Wastewater from the reactor and spent sulfuric acid from the acid dryer from
the
production
of
methyl
bromide.
Methyl bromide
(Bromo—
74-83—9
0.11
15
methane)
1(132
Spent
absorbent
and wastewater
separator
solids from
the
production
of
methyl
bromide.
Methyl bromide
(Bromo—
74—83—9
0.11
15
methane)
1(136
Still bottoms
from
the
purification
of
ethylene
dibromide
in
the
production
of
ethviene dibromide
via bromination
of ethene.
Methyl
bromide
(Bromo-
74-83—9
0,11
15
methane)
Chloroform
67—66—3
0.046
6.0
Ethylene
dibromide
(1.2—
106—93—4
0.028
15
Dibromoethane’)
1(141
Process residues
from the recovery
of coal tar,
including,
but not limited to,
collecting
sump residues
from the production
of coke or the recovery of coke
by—products
produced
from
coal.
This listing
does
not
include
1(087
(decanter
tank tar sludge from coking operations).
Senzene
71—43—2
0.14
10
Benz(a)anthracene
56—55-3
0.059
3.4
Benzo(a)pyrene
50—2—8
0.061
3.4
Benzo(b)fluoranthene
205—99—2
0.11
6.8
(difficult to
distnguish
from berizo—
(k)fluoranthene)
Benzo(k)fiuoranthene
207-08—9
0.11
5.3
(difficult to
distinguish
from
benzo-
(b’) fluoranthene)
Chrysene
218—01—9
0.059
3.4
352
Dibenz(a,h)anthracerle
53—70-3
0.055
8.2
Indeno(1,2,3—cd~pyrene
193—39—5
0.0055
3.4
K142
Tar stprage tank residues from the production of coke from coal or from the
recovery of
coke by—products produced from coal.
Benzene
‘71—43-2
0.14
10
Benz(a)anthracene
56—55-3
0.059
3.4
Benzo(a)pyrene
50—32—8
0.061
3.4
Benzo(b)fluoranthene
205-99—2
0.11
5.8
(difficult
to
distinguish from benzo—
(k)fiuoranthene~
Benzo(k)fluoranthene
207-08—9
0.11
6.8
(difficult to
distinguish from benzo—
(b)fluoranthene~
Chrysene
218-01-9
0.059
3.4
Dibenz(a,h)anthracene
53—70—3
0.055
Ideno(1,2,3—cd)pyrene
193—39—5
0.0055
3.4
1(143
Process residues from
the
recovery
of
light
oil,
including,
but
not
limited
to,
those
generated
in
stills,
decanters,
and
wash
oil recovery units from the
recovery
of
coke
by—products
produced
from
coal.
Benzene
71—43-2
0.14
10
Benz(a)anthracene
56—55—3
0.059
3.4
Benzota)pvrene
50—32—8
0.061
Benzo(b’tfiuoranthene
205—99—2
0.11
6.8
(difficult to
distinguish from
benzo—
(k)fluoranthene)
Benzo(kjfluoranthene
207—08-9
0.11
6.8
(difficult to
distinguLsh from benzo—
(b)
fiuoranthene’)
Chrysene
218—01—9
0.059
3.4
1(144
Wastewater sump residues
from light oil refining,
including, but not limited
to,
intercepting or contamination sump sludges from the recovery of coke by-
products produced from coal.
Benzene
71-43—2
0.14
10
Benz(a)anthracene
56—55—3
0.059
3.4
Benzo(a)pyrene
50—32—8
0.061
3.4
Benzo(b)fiuoranthene
205—99—2
0.11
6.8
(difficult to
distinguish from benzo—
(k)fluoranthene)
Benzo(k’)fluoranthene
207—08—9
0.11
6.8
(difficult to
distinguish from benzo—
(b)fluoranthene)
Chrysene
218—01—9
0.059
3.4
Djbenz(a,h)anthracene
53—70-3
0.055
8.2
1(145
Residues
from
naphthalene
collection
and
recovery
operations
from
the
recovery
of coke by-products produced from coal.
Benzene
71—43—2
0.14
10
Benz(a)anthracene
56—55-3
0.059
3.4
Benzo(a’)iDyrene
50-32—8
0.061
3.4
353
Chrysene
218—01—9
0.059
3.4
Dibenz(a,h)anthraCene
53—70—3
0.055
6.2
Naphthalene
91-20—3
0.059
5.6
1(147
Tar
storage
tank
residues
from
coal
tar
refininci.
Benzene
71—43—2
0.14
10
Benz(a’)anthracene
56-55-3
0.059
3.4
Benzo(a)pyrene
50—32—8
0.061
3.4
Benzo(b)fluOranthene
205-99-2
0.11
6.8
(difficult
to
distinguish from benzo-
(k)fluoranthene)
Benzo(k)fluoranthene
207—08—9
0.11
6.8
(difficult to
distinguish from benzo—
(bi
fluoranthene)
Chrysene
218—01-9
0.059
3.4
Dibenz(a,h)arkthracene
53-70-3
0.055
8.2
Indeno(l,2,3—cd)pyrene
193—39-5
0.0055
3.4
1(148
Residues from coal tar distillation,
including,
but
not limited
to,
still
bottoms.
Benz(a)anthraCene
56—55—3
0.059
Benzo(a)pvrene
50-32—8
0.061
3.4
Benzo(b)fluoranthene
205-99—2
0.11
6.8
(difficult
to
distinguish from benzo—
(k) fluoranthene)
Benzo(k)fluorarithene
207-08—9
0.11
6.8
(difficult
to
distinguish
from
benzo—
ib) fluoranthene)
Chrvsene
218—01—9
0.059
3.4
Dibenz(a,h)anthracene
53—70-3
0.055
8.2
Indeno(1,2,3—cd)pyrene
193—39—5
0.0055
3.4
1(149
Distillation
bottoms
from
the
production
of
alpha—
(or
methyl-)
chlorinated
toiuenes,
ring-chlorinated
toluenes,
benzoyl
chlorides,
and
compounds
with
mixtures
of
these
functional
groups.
(This
waste
does
not
include
still
bottoms
from
the
distillations
of
benzyl
chloride.)
Chlorobenzene
108—90—7
0.057
6.0
Chloroform
67—66—3
0.046
6.0
Chioromethane
74—87—3
0.19
30
p—Dichlorobenzene
106—46-7
0.090
6.0
Hexachiorobenzene
118—74—1
0.055
10
Perttachlorobenzene
608—93—5
0.055
10
1,2,4,5—Tetrachioro—
95—94—3
0.055
14
benzene
Toluene
108—88-3
0.080
10
1(150
Organic
residuals,
excluding
spent
carbon
adsorbent,
from
the
spent
chlorine
gas and hydrochloric acid recovery processes associated with the production of
alpha—
(or methyl—) chlorinated
toluenes,
ring-chlorinated
toluenes,
benzoyl
chlorides,
and
compounds
with
mixtures
of these functional groups.
Carbon tetrachloride
56—23—5
0.057
6.0
Chloroform
67-66—3
0.046
6.0
Chioromethane
74—87—3
0.19
30
p—Dichlorobenzene
106—46—7
0.090
6.0
354
Hexachlorobenzene
Pentach~orobenzene
1,2,4, 5—Tetrachloro—
benzene
1,1,2,2— Tetrachloro—
ethane
Tetrachioroethylene
1,2, 4-Trichlorobenzene
~~‘-it
at
cor
“~-~4~ns
greate’
81—81—2
(WETOX or
CHOXD)
fb
CARBN; or
INCIN
P002
1-Acetyl—2-thiourea
1-Acety1—2—thiourea
P003
Acrolein
Acrolein
P004
Aldrin
Aidrin
P005
Alivi alcohol
Allyl
alcohol
591—08—2
107—18—6
(WETOX or
CHOXD)
fb
CARBN;
or
INCIN
(WETOX or
CHOXD)
fb
CARBN;
or
INCIN
INCIN
CNBST
P006
Aluminum phosphide
Aluminum phosphide
20859—73—6
CHOXD;
CHRED;
or INCIN
CHOXD; CHRED;
or
INCIN
P007
5—Aminomethyl—3—isoxazolol
118—74--i
608—93—5
95—94—3
0.055
0.055
0.055
79—34—5
0.057
127—18—4
120—82—1
10
10
14
6.0
6.0
19
0.056
0.055
1(151
Wastewater treatment sludges,
excluding neutralization and biological sludges,
generated
during
the
treatment
of
wastewatere
from
the
production
of
alpha—
(or methyl—)
chlorinated toluenes, ring—chlorinated toluenes.
benzoyl
chlorides,
and compounds with mixtures of these functional groups.
Benzene
71—43—2
0.14
Carbon tetrachloride
56—23—5
0.057
6.0
Chloroform
67—66—3
0.046
6.0
Hexachlorobenzerte
118—74—1
0.055
10
Pentachlorobenzene
608-93—5
0.055
10
1,2,4,5—Tetrachioro—
95—94—3
0.055
14
benzene
Tetrachloroethyiene
127—18-4
0.056
6.0
Toluene
108—88—3
0.080
Pool
Warfarin,
& salts,
when
Warfarin
than 0.3
CHEST
107—02—6
0.29
CMBST
309—00—2
0.021
0.068
355
5-Aminomethyl—3-isoxa-
zolol
2763—96—4
(WETOX or
CHOXD)
fb
CARBN; or
INCIN
INCIN
P008
4-Aminopyr
idine
4-Axninopyridine
504—24—5
(WETOX or
CHOXD)
fb
CARBN; or
INCIN
INCIN
P009
Axnmonium
picrate
Ammonium picrate
131—74—8
CHOXD; CHRED;
C~.RBN;BIODG;
or
INCIN
CHOXD; CHRED;
or
CMBST
Polo
Arsenic acid
Arsenic
7440—38—2
1.4
5.0
ma/I
TCLP
POll
Arsenic pentoxide
Arsenic
P012
Arsenic trioxide
Arsenic
7440—38—2
7440—38—2
1.4
1.4
5.0 m~/lTCLP
5.0 ma/l TCLP
P013
Barium cyanide
Barium
Cyanides
(Total)7
Cyanides
(Amenable)7
P014
Thiophenol
(Benzene thiol)
Thiophenol
(Benzene
thiol)
(WETOX or
INCIN
CHOXD)
fb
CARBN; or
INCIN
P015
Beryllium dust
Beryllium
7440—41—7
RMETL;or RTHRM
RMETL; or
RTHR14
P016
Dichloromethyl ether
(Bis(chloromethyl )ether)
Dichloromethvl ether
542—88-1
(WETOX or
CHOXD)
fb
CARBN; or
INCIN
INCIN
P017
Bromoacetone
Bromoacetone
598—31—2
(WETOX
or
CHOXD) fb
CARBN; or
INCIN
INCIN
7440—39—3
57—12—5
5 7—12—5
108—98—5
NA
1.2
0.86
-
TCLP
7.6
rnri/1
590
30
356
P018
Brucme
Brucine
357-57—3
(WETOX or
INCIN
CHOXD)
fb
CARBN; or
INCIN
P020
2-sec—Butvl—4~6—dinitrophenol
(Dinoseb)
2—sec—Butvl—4,6—dinitro—
88—85—7
0.066
2.5
~heno1
(Dinoseb)
P02.
Calcium cyanide
Cvanides (Total)7
57—12—5
1.2
Cyanides (Amenable)7
57—12—5
0.86
30
P022
Carbon disulfide
Carbon disulfide
75-15—0
INCIN
Carbon disulfide;
75-15-0
NA
4.8
ma/l TCLP
alternate6 standard for
nonwastewaters only
P023
Chloroacetpidehyde
Chioroacetaldehyde
107—20-0
(WETOX or
INCIN
CHOXD)
fb
CARBN; or
INCIN
P024
p—Chloroaniline
p—Chloroariiline
106—47—8
.046
16
P026
1- (o-Chlorophenyl )
thiourea
1—(o—Chiorophenvi)thio-
5344-82—i
(WETOX or
INCIN
urea
CHOXD)
fb
CARBN; or
INCIN
P027
3—Chloropropionitrile
3—Chloropropionitrile
542—76-7
(WETOX or
INCIN
CHOXD)
fb
CARBN; or
INCIN
P028
Benzyl chloride
Benzvl chloride
100—44—7
(WETOX
or
INCIN
CHOXD)
fb
CARBN; or
INCIN
P029
CoPper cyanide
Cvanides
(Total)7
57-12-5
1.2
590
Cyanides
(Amenable)7
57-12-5
0.86
30
357
P03~
Cyanides
(soluble
Baits and cornplexes)
Cvanides
(Total)7
57—12—5
1.2
590
Cvanides
(Axnenable)7
57—12—5
0.86
30
P031
Cyanoaen
Cyanogen
460-19-5
CHOXD; WETOX;
CHOXD; WETOX;
or INCIN
or INCIN
P033
Cvanocien chloride
Cvanoaen chloride
506-77—4
CHOXD; WETOX;
CHOXD; WETOX;
or INCIN
or INCIN
P034
2-Cyclohexvl-4,6—dinitrophenol
2—Cyclohexyj-—4,6—
131—89-5
(WETOX or
INCIN
dinitrophenol
CHOXD)
fb
CARBN; or
INCIN
P036
Dichiorophenylareine
Arsenic
7440—38—2
1.4
5.0
ma/i TCLP
P037
Dieldrin
Dielclrin
60—57—1
0.017
0.13
P038
Diethvlarsine
Arsenic
7440—38—2
1.4
5.0 mci/i TCLP
P039
Disuifotori
Disulfoton
298—04—4
0.017
6.2
P040
O
,
O-Diethyl—O-pyrazinvl -phosphorothioate
O,O—Diethyl—O—pvrazinyl—
297-97—2
CARBN; or
CMBST
phoephorothioate
INCIN
P041
Diethvl—p—nitrophenvl phosphate
Diethyl—p-nitrophenyi
311—45—5
CARBN; or
CMBST
phosphate
INCIN
P042
Epinephrine
Epinephrine
51-43—4
(WETOX or
INCIN
CHOXDI
fb
CARBN; or
INCIN
P043
Diisopropylfluorophosphate
(DFPI
Diieoprppvlfluoro-
55—91—4
CARBN;
or
CMBST
phosphate
(DFPI
INCIN
P044
D imetho ate
358
Dimethoate
60—51—5
CARBN; or
CMBST
INCIN
P045
Thiofanox
Thiofanox
39196-18—4
(WETOX or
INCIN
CHOXD)
fb
CARBN; or
INCIN
P046
aipha,plpha-Dimethvlphenethylaxnine
aipha,alpha—Dimethvl-
122-09—8
(WETOX or
INCIN
phenethylamine
CHOXD) fb
CAREN; or
INCIN
P047
4, 6-Dinitro—o—cresol
4,6—Dinjtro—o—cresol
543—52—1
0.28
160
P047
4, 6-Dinitro—o—cresol salts
NA
NA
(WETOX or
INCIN
CHOXD1
fb
CARBN; or
INCIN
P048
2,4—Dinitrophenol
2,4—Dinitrophenol
51—28—5
0.12
160
P049
Dithiobiuret
Dithiobiuret
541—53-7
(WETOX or
INCIN
CHOXD)
fb
CARBN; or
INCIN
P050
Endosulfan
Endosulfan
I
939—98—8
0.023
0.066
Endosulfan
II
33213—6—5
0.029
0.13
Endosulfan sulfate
1031—07—8
0.029
0.13
P051
Endrin
Endrin
72—20—8
0.0028
0.13
Endrin aldehvde
7421—93—4
0.025
0.13
P054
Aziridine
Aziridine
151-56-4
(WETOX or
INCIN
CHOXDI
fb
CARBN; or
INCIN
P056
Fluorine
Fluoride (measured in
16964—48-8
ADGAS
fb
NEUTR
wastewaters only)
359
P057
F.uoroacetamide
Fiuoroacetamide
640—19-7
(WETOX or
INCIN
CHOXD)
fb
CARBN; or
INCIN
P058
Fiuoroacetic
acid,
sodium salt
Fiuoroacetic acid,
62-74—8
(WETOX or
INCIN
sodium salt
CHOXD)
fb
CARBN; or
INCIN
P059
HeptachlOr
Heptachlor
76—44—8
0.0012
0.066
Heptachlor epoxide
1024-57—3
0.016
0.066
P060
Igodrin
Isodrin
465—73—6
0.021
0.066
P062
Hex aethyl
tetraphosphate
Hexaethvl
tetraphosphate
757-58—4
CARBN;
or
CMBST
INCIN
P063
Hydrogen cyanide
Cyanides
(Total)7
57—12—5
1.2
590
Cyanides
(Amenable’i7
57—12—5
0.86
P064
Isocyanic acid,
ethyl ester
Isocyanic acid,
ethyl
624-83-9
(WETOX or
INCIN
ester
CHOXD)
fb
CARBN; or
INCIN
P065
P065
(mercury
fulminate)
nonwastewaters,
regardless
of their total mercury
contant, that are not incinerator residues or are not residues from RMERC.
Mercury
7439—97-6
IMERC
P065
P065
(mercury fulminate)
nonwastewaters that are either ir~cineratorresidues
or are residues from RMERC;
and contain greater than or equal to 260
mci/kci
total mercury.
Mercury
7339—97-6
NA
RNERC
P065
P065
(mercury
fulminate)
nonwastewaters that are residues from RMERC and
contain less than 260 mci/kg total mercury.
Mercury
7439—97—6
0.20
mci/i TCLP
P065
P065
(mercury
fulminate)
nortwastewaters
that
are
incinerator
residues
and
contain lees than
260
mg/kg total mercury.
Mercury
7439—97—6
NA
0.025
mci/i
TCLP
360
P065
All P065
(mercury fulminate) wastewaters.
Mercury
7439—97—6
0.15
NA
P066
Methomyl
Methomvl
16752-77-5
(WETOX or
INCIN
CHOXDI
fb
CARBN; or
INCIN
P067
2—Methyl—aziridine
2—Methyl-aziridine
75-55—8
(WETOX or
INCIN
CHOXD)
fb
CARBN; or
INCIN
P068
MethYl hydrazine
Methyl hydrazine
60—34-4
CHOXD; CURED;
CHOXD;
CURED,
CARBN; BIODG;
or CMBST
or INCIN
P069
2—Methyllactonitrile
2—Methyllactonitrile
75865
(WETOX or
INCIN
CHOXD) fb
CARBN; or
INCIN
P070
Aidicarb
Aldicarb
116—06—3
(WETOX or
INCIN
CHOXD)
fb
CARBN; or
INCIN
Poll
Methyl parathion
Methyl parathion
298—00—0
0.014
4.6
P072
1—Naphthyj-2—thiourea
1—Naohthyl-2-thiourea
86-88-4
(WETOX or
INCIN
CHOXD)
fb
CARBN; or
INCIN
P073
Nickel carbonvl
Nickel
7440—02—0
3.98
5.0 mci/i
TCLP
P074
Nickel cyanide
Cvanides
(Total)7
57—12—5
1.2
590
Cyanides
(P.menable)7
57—i2—5
0.86
30
Nickel
7440—02—0
3.98
5.0 mci/i TCLP
P075
Nicotine and salts
361
Nicotine and salts
54—11-5
(WETOX or
INCIN
CHOXD)
fb
C?,RBN; or
INCIN
P076
Nitric oxide
Nitric oxide
10102—43—9
ADGAS
ADGAS
P077
p—Nitroanilme
p—Nitroaniline
100—01—6
0.028
28
P078
Nitrogen
dioxide
Nitrogen dioxide
10102—44—0
ADGAS
ADGAS
P081
Nitroglycerin
Nitroglycerin
55—63—0
CHOXD;
CHRED;
CHQXD;
CURED;
CARBNI
BIODG
or CMBST
or INCIN
P082
N-Nitrosodimethylamine
N—Nitrosodimethvlamine
62—75—9
0.40
2.3
P084
N-Nitrosomethylvinylamine
N—Nitrosomethvlvi’wl—
4549-40—0
(WETOX or
INCIN
amine
CHOXD)
fb
CARBN; or
INCIN
P085
Octamethylpyrophosphoramide
Octamethylpyrophosphor-
152—16—9
CARBN; or
CMBST
ainide
INCIN
P087
Osmium tetroxide
Osmium tetroxide
20816—12—0
RMETL; or
RMETL; or
RTHRM
RTHRN
P088
Endothall
-
Endothall
145—73—3
(WETOX or
CHEST
CHOXD) fb
CARBN; or
INCIN
P089
Parathion
Parathion
56—38—2
0.014
4.6
P092
P092
(phenyl
mercuric
acetate)
nonwastewaters,
regardless
of their total
mercury content,
that are not incinerator residues or are not residues from
RMERC.
Mercury
7439—97—6
NA
IMERC; or
RMERC
362
P092
P092
(Phenvi mercuric acetate) nonwastewaters that are either incinerator
residues or are residues
from RM~RC~
arid ~ti1l
contain
~
than
or eaual
t-r~.
260
mglkn
total
m~rcnrv
Mercury
__________
_____
-
--—-
-
------
-
—---
—----
-
-———
-—--
---—--
7439—97—6
RMERC
P092
P092 (~henv. mercuric acetate’) nonwastewaters that are residues from RMERC
and
contain less than
260 mci/kci total mercury.
0.20 mci/i
TCLP
Mercury
7439—97-6
P092
P092 (~henvlmercuric acetate) nonwastewaters that are incinerator residues
and contain less than 260 mg/kg total mercury.
Mercury
7439—97-6
NA
__________
0.025
mci/i
TCLP
P092
All P092
(phenyl mercuric
Mercury
P093
Pheriylthiourea
Phenylthiourea
P095
Phosciene
Phosgene
acetate)_wastewaters.
7439—97—6
0.15
103—85—5
7 5—44—5
(WETOX or
CHOXD)
fb
CARBN;
or
INCIN
(WETOX or
CHOXD) fb
CAREN; or
INCIN
INCIN
INCIN
P096
Phosphine
Phosphine
7803—51—2
CHOXD; CHRED;
or INCIN
CHOXD; CURED;
or INCIN
P098
Potassium
cyanide.
Cyanides
(Total)7
Cvanides
(Amenable)7
590
30
0.30 mci/i TCLP
NA
P094
Phorate
Phorate
298—02—2
0.021
4.6
P097
Famphur
Faxnphur
52—85—7
0.017
P099
Potassium silver cyanide
Cvanides
(Total)7
Cyanides
(Amenable)7
Silver
15
590
30
57— 12—5
57—12—5
57—12—5
57—12—5
7440—22—4
1.2
0.86
1.2
0.86
0.43
P101
Ethyl cyanide
(Propanenitrile)
363
Ethyl cyanide
107—12—0
0.24
360
(~ro~anenitrile)
P102
Pro~aravl
alcohol
Pro~arcivlalcohol
107—19-7
(WETOX or
CMBST
CHOXD)
fb
CARBN; or
INCIN
P103
Selenourea
Selenium
7782—49—2
0.82
0.16 mci/i TCLP
P104
Silver cyanide
Cvanides
(Total)7
57—12-5
1.2
590
Cvanides
(Amenable)7
57-12-5
0.86
30
Silver
7440—22—4
0.43
0.30 mci/i
TCLP
P105
Sodium azide
Sodium azide
26628-22-8
CUOXD; CURED;
CUOXD; CURED;
CARBN;
BI000;
or CMBST
or INCIN
P106
-
Sodium cyanide
Cyanides
(Total)7
57—12—5
1.2
590
Cvanidee
(Amenable)7
57-12-5
0.86
30
P108
Strychnine and salts
Strychnine and salts
57—24-9
(WETOX or
INCIN
CUOXD)
fb
CARBN; or
INCIN
P109
TetraethyldithioPvroPhosPhate
-
Tetraethyldithiopyro-
3689—24—5
CARBN; or
CMBST
phosphate
INCIN
P110
Tetraethvl
lead
lead
7439—92—1
0.69
0.37 mci/i TCLP
P11.
TetraethylpyrophosPhate
TetraethylPvroPhosPhate
107-49—3
CARBN; or
CHEST
INCIN
P112
Tetranitromethane
Tetranitromethafle
509—14—8
CUOXD;
CHRED;
CHOXD;
CURED;
CAREN;
BIODG;
or CMBST
or INCIN
P113
Thallic oxide
Thallium (measured in
7440—28—0
RTHRN; or
wastewaters only)
STABL
364
P114
Thallium pelenite
Selenium
7782—49—2
0.82
0.16 mci/i TCLP
P115
Thallium
(I) sulfate
Thallium
(measured in
7440280
RTHRM; or
wastewaters only)
STABL
P116
Thiosemicarbazide
Thiosemicarbazide
79-19—6
(WETOX or
INCIN
CUOXD)
fb
CARBN; or
INCIN
P118
Trichloromethanethioi
Trichioromethanethiol
75-70—7
(WETOX or
INCIN
CUOXD’) fb
CARBN; or
INCIN
P119
Ammortium vanadate
Vanadium
(measured
in
7440-62-2
STABL
wastewaters
only’)
P120
Vanadium pentoxide
Vanadium
(measured in
7440-62—2
STABL
wastewaters
only’)
P121
Zinc
cyanide
çyanides
(Total)7
57—12—5
1.2
590
Cvanides
(Amenable)7
57—12—5
0.86
30
P122
Zinc ~hosphjde
Zn~,P,, when present at concentrations greater than
10
Zinc Phosphide
1314—84—7
CHOXD; CHRED;
CUOXD; CURED;
or INCIN
or INCIN
P123
Toxaphene
Toxaphene
8001—35—2
0.0095
2.6
U00I
Acetaldehvde
Acetaidehyde
75—07-0
(WETOX or
CMBST
CHOXD’)
fb
CARBN; or
INCIN
U002
Acetone
Acetone
67—64—1
0.28
160
U003
Acetonitrile
Acetonitriie
75—05-8
INCIN
365
Acetonitrile;
alternate6
75—05—8
NA
1.8
standard for
nonwastewaters only
U004
Acetophenone
Acetophenone
98—86—2
0.010
9.7
U005
2—Acetylaminofluorene
2—Acetylaminofluorene
53—96-3
0.059
140
U006
Acetyl chloride
Acetyi chloride
75—36-5
(WETOX or
INCIN
CUOXD)
fb
CARBN; or
INCIN
13007
Acrylamj,de
Acrylainide
79—06-1
(WETOX or
INCIN
CHOXD)
fb
CARBN; or
INCIN
13008
Acrylic acid
Acrylic acid
79—10-7
(WETOX or
CMBST
CHOXD)
fb
CARBN; or
INCIN
U009
Acrylonitrile
Acryionitrile
107—13—1
0.24
84
UO
10
Mitomvcin C
Mjtomycin~C
50—07-7
(WETOX or
INCIN
CHOXD) lb
CARBN; or
INCIN
13011
Axnitrole
Amitrole
61—82-5
(WETOX or
INCIN
CUOXD)
fb
CARBN;
or
INCIN
U0 12
Aniline
Aniline
62—53—3
0.81
14
U0
14
Auramine
Auramine
492—80-8
(WETOX or
INCIN
CHOXD)
fb
CARBN; or
INCIN
366
13015
Azaserine
AzaBerine
115—02—6
(WETOX or
INCIN
CUOXD)
fb
CARBN; or
INCIN
U0
16
Benz(clacridine
Benz(c)acridine
225—51—4
(WETOX or
CMBST
CHOXD)
fb
CARBN; or
INCIN
U017
Benzal chloride
Benzal chloride
98—87—3
(WETOX or
INCIN
CHOXD) fb
CAREN; or
INCIN
U018
Benz (a)anthracene
Benz(a)anthracene
56—55—3
0.059
3.4
13019
Benzene
Benzene
71—43—2
0.14
10
U02
0
BenzenesulfonVl
chloride
Benzenesulfonvl
chloride
98-09—9
(WETOX or
INCIN
CHOXD’)
fb
CARBN; or
INCIN
U021
Benzidine
Benzidine
92-87—5
(WETOX or
INCIN
CHOXD) fb
CARBN; or
INCIN
13022
Benzo(a)Pvren~
Benzo(a’)pvrene
50—32—8
0.061
3.4
U023
Benzotrichloride
Benzotrichloride
98—07—7
CUOXD; CURED;
CHOXD; CURED;
CARBN;
BIODG;
or CMBST
or INCIN
13024
bia (2—Chloroethoxy)methane
bis(2—Chloroethoxy)—
111—91—1
0.036
7.2
methane
13025
his(2—Chloroethvl)ether
bis(2—Chloroethvl)ether
111—44—4
0.033
6.0
367
13026
Chlornaphazine
Chlornaphazine
494-03-.
(WETOX or
INCIN
CHOXD) fb
CARBN; or
INCIN
U027
bia(2—Chloroiaopropyl
)
ether
bis(2—ChloroisoproPyl)—
39638—32—9
0.055
7.2
ether
13028
bis(2-Ethylhexyl ‘)phthalate
bia(2—Ethyihexyl)—
117—81—7
0.28
28
phthalate
U029
Methyl bromide
(Bromomethane’)
Methyl bromide (Bromo—
74-83-9
0.11
15
methane’)
U030
4-Bromophenyl phenyl ether
4—Bromophenyl phenyl
101-55—3
0.055
15
ether
13031
n-Eutyl alcohol
n-Butvl alcohol
71—36-3
5.6
2.6
U03
2
Calcium chromate
Chromium (Total)
7440—47—3
2.77
0.86 ma/l TCLP
U033
-
Carbon oxvfluoride
Carbon oxvfluoride
353—50—4
(c1ETOX or
INCIN
CHOXD’)
fb
CARBN; or
INCIN
13034
Trichloroacetaldehvde
(Chloral)
Trichloroacetaldehvde
75—87—6
(WETOX or
INCIN
(Chloral)
CUOXD)
fb
CARBN; or
INCIN
13035
Chloraxnbucil
Chlorambucil
305—03—3
(WETOX or
INCIN
CHOXD)
fb
CARBN; or
INCIN
13036
Chlordane
Clilordane (a1~haand
57—74—9
0.0033
0.26
gamma isomers)
368
13037
Chlorobenzene
Chlorobenzene
108—90-7
0.057
6.0
U038
Chlorobenzilate
Chlorobenzilate
510—15—6
0.10
INCIN
U039
p—Chloro—m—cresol
p—Chloro—m—cresol
59-50—7
0.018
14
U041
Epichlorohvdrin
(1—Chioro-2
,
3-epoxvpropane)
Epichlorohydrin
(1
106—89—8
(WETOX or
INCIN
Chloro—2,3—epoxypropane)
CHOXD)
fb
CARBN; or
INCIN
U042
2—Chloroethvi vinyl ether
2—Ch.oroethyl
vinyl
110—75—8
0.062
INCIN
ether
U04 3
Vinyl chloride
Vinyl chloride
75-01-4
0.27
6.0
13044
Chloroform
Chloroform
67-66-3
0.046
6.0
U04 5
Chioromethane (Methyl chloride)
Chloromethane (Methyl
74-87—3
0.19
30
chloride)
U046
Chioromethyl methyl ether
Chioromethyl methyl
107—30-2
(WETOX or
INCIN
ether
CUOXD’)
fb
CARBN; or
INCIN
U047
2-Chloronaphthalene
2—Chloronaphthalene
91-58—7
0.055
U048
2—Chlorophenoi
2—Chlorophenol
95-57—8
0.044
5.7
U049
4—Chloro—o—toluidine
hydrochloride
4—Chloro—o—toluidine
3165-93—3
(WETOX or
INCIN
hydrochloride
CHOXD) fb
CARBN;
or
INCIN
13050
Chrysene
Chrvsene
218—01-9
0.059
3.4
369
U051
Creosote
Naphthalene
91-20-3
0.059
S.6
Pentachiorophenol
87-86-5
0.089
7.4
Phenanthrene
85-01—8
0.059
5.6
Pyrene
129—00—0
0.067
8.2
Toluene
108—88—3
0.080
10
Xylenes—inixed isomers
1330—20—7
0.32
30
(sum
of o—.
m—,
and
~—
xvlene concentrations)
Lead
7439-92-1
0.69
0.37 mci/i TCLP
U0
52
Cresola (Cresylic acid)
o—Creaol
95-48—7
0.11
5.6
m—Cresol
(difficult to
108—39—4
0.77
5.6
distinguish from p-
cresol)
p—Cresol
(difficult to
106—44—5
0.77
5.6
distinguish from m-
cresol)
Cresol—mixed isomers
1319—77—3
0.88
11.2
(Cresvlic acid)
(sum of o—, m—,
and p—
cresol concentrations’)
U0 53
Crotonaldehvde
Crotonaldehvde
4170-30-3
(WETOX or
CMBST
CHOXD)
fb
CARBN; or
INCIN
13055
Cumene
Cumene
98-82—8
(WETOX or
CMBST
CHOXD’) fb
CARBN; or
INCIN
13056
Cyclohexane
Cyciohexane
110—82-7
(WETOX or
CMBST
CHOXD)
fb
CARBN;
or
INCIN
13057
Cvclohexanone
Cyclohexanone
108—94—1
0.36
CMBST
Cyciohexanone;
108—94—1
0.75 mci/l TCLP
alternate6 standard for
nonwagtewaters only
13058
Cvclophosphamide
Cyclophosphamide
50-18-0
CARBN; or
CMBST
INCIN
13059
Daunomvcin
370
U060
DDD
Daunomycin
20830—81—3
53—19—0
72—54—8
(WETOX or
CHOXD) fb
CARBN; or
INCIN
0.023
0.023
INCIN
0.087
0.087
13062
Diallate
Diallate
2303—16—4
(WETOX or
CHOXD’)
fb
CARBN; or
INCIN
INCIN
U063
Dibenz (a,h anthracene
Dibenz (a,h )anthracene
13064
Dibenz(a, j)pyrene
Dibenz(a, i’)pyrene
13066
1, 2—Dibromo—3—chioropropane
1,2—Dibromo—3—chloro—
propane
U068
Dibromomethane
Dibromomethane
U069
Di—n—butyl phthalate
Di—n-butyl phthalate
13070
o—Dichiorobenzefle
o—Dichlorobenzene
189—55—9
(WETOX or
CHOXD)
fb
CARBN;
or
INCIN
CMBST
13071
m—Dichlorobenzene
m—Djchiorobenzene
o,p’ -DDD
p, p’ -DDD
13061
DDT
o,p’-DDT
p,p’-DDT
o
,
p’ -DDD
p,p’—DDD
o,p’
-DDE
p,p’-DDE
789—02—6
50—29—3
53—19—0
72—54—8
3424—82—6
72—55—9
0.0039
0.0039
0.023
0.023
0.03
1
0.031
0.087
0.087
0.087
0.087
0.087
0.087
53—70—3
0.055
8.2
96—12—8
0.11
13067
Ethylene dibromide
(1,2-Dibromoethane’)
Ethylene dibromide
(1,2-
106—93—4
Dibromoethane)
0.028
15
15
15
28
6.0
74—95—3
0.11
84—74—2
0.057
95—50—1
0.088
541—73—1
0.036
371
U0
72
p—Dichlorobenzene
p—Dichlorobenzene
106—46—7
0.090
6.0
13073
3,3’
—Dichiorobenzidine
3,3’—Dichlorobenzidine
91-94-1
(WETOX or
INCIN
CHOXD’) fb
CARBN; or
INCIN
U074
1,4—Dichloro-2—butene
cis—1,4—Dichloro—2—
1476—11—5
(WETOX or
INCIN
butene
CHOXD)
fb
CARBN; or
INCIN
trans—1,4—Dichloro—2-
764—41—0
(WETOX or
INCIN
butene
CHOXD’) fb
CARBN; or
INCIN
U075
Dichlorodi
f
luoromethane
Dichiorodifluoromethane
75—71—8
0.23
7.2
U076
1,l-Dichioroethane
1,1—Dichioroethane
75—34—3
0.059
6.0
U077
1,2—Dichloroethane
1,2—Dichloroethane
107—06—2
0.21
6.0
13078
1~
1-Dichloroethyiene
l,.—Dichloroethylene
75—35—4
0.025
6.0
U079
1,2—Dichloroethviene
trans—1,2—Dichloro—
156—60—5
0.054
30
ethylene
U080
Methviene chloride
Methvlene chloride
75-09—2
0.089
30
13081
2, 4—Dichlorophenol
2.4—Dichlorophenol
120—83—2
0.044
14
13082
2, 6-Dichlorophenol
2,6—Dichlorophenol
87—65—0
0.044
14
U083
-
1,2—Dichioropronane
1,2—DichioroproPane
78—87—5
0.85
18
13084
1,3—Dichioropropvlene
372
cis—l,3—Dichloro—
10061—01—5
0.036
18
propylene
trans—1,3—Dichloro—
10061—02—6
0.036
18
propylene
U085
1,2:3,
4—Diepoxybutane
1,2:3,4—Diepoxybutane
1464—53-5
(WETOX or
CMBST
CHOXD)
fb
CARBN; or
INCIN
U086
N, N’ —Diethylhydrazine
N,N’-Diethvihvdrazine
1615—80-1
CUOXD; CURED;
CHOXD;
CURED;
CARBN; BIODG;
or CHEST
or INCIN
U087
0,O—Diethvl S—methyldithiophosphate
0,0-Diethyl S-methyl—
3288-58—2
CARBN; or
CMBST
dithiophosphate
INCIN
U088
Diethyl phthalate
Diethyl phthalate
84—66-2
0.20
28
13089
Diethyl stilbestrol
Diethyl stilbestrol
56—53-1
(WETOX or
CMBST
CUOXD) fb
CARBN: or
INCIN
13090
Dihydrosafrole
Dihydrosafrole
94-58-6
(WETOX or
CMBST
CUOXD)
fb
CARBN; or
INCIN
U091
3,3’—Dimethoxybenzidine
3,3’—Dimethoxybenzidine
119-90—4
(WETOX or
INCIN
CHOXD) fb
CARBN; or
INCIN
13092
Dimethylamine
Dimethylamine
124—40-3
(WETOX or
INCIN
CHOXD)
fb
CARBN; or
INCIN
13093
p—~imethy1anhinoazobenzene
p—Dimethyl—
60—11—7
0.13
INCIN
aininoazobenzene
U094
7,12—Dimethylbenz (a)anthracene
373
7,12—Djmethylbenz(a)—
57-97—6
(WETOX or
CMBST
anthracene
CHOXD’)
fb
CARBN; or
INCIN
U095
3,3’—Dimethylbenzidine
3,3’—Djmethvlbenzidine
119—93—7
(WETOX or
INCIN
CHOXD)
fb
CARBN; or
INCIN
13096
alpha, alpha—Dimethy.
benzyl hydroperoxide
alpha, aipha-Dimethyl
80-15-9
CHOXD;
CURED;
CUOXD; CURED
benzvi hydroperoxide
CARBN; BIODG;
or CMBST
or INCIN
U097
Dimethvlcarbamovl chloride
Dimethylcarbamoyl
79-44-7
(WETOX or
INCIN
chloride
CHOXD’)
fb
CARBN; or
INCIN
13098
1,1—Dimethyihvdrazine
1,1—Dimethyihydrazine
57—14-7
CHOXD; CURED;
CHOXD; CURED;
CAREN; BIODG;
or CMBST
or INCIN
U099
1L2—Dimethylhydrazine
1,2—Dimethylhydrazine
540-73—8
CHOXD; CURED;
CUOXD; CURED;
CARBN; BIODG;
or CMBST
or INCIN
13101
2,4—Dimethylphenol
2,4—Dimethylphenol
105—67—9
0.036
14
Ul02
Dimethyl phthalate
Dimethvl phthalate
131—11—3
0.047
28
U103
Dimethyl
sulfate
Dimethyl sulfate
77—78-1
CHOXD; CURED;
CHOXD;
CURED;
CARBN;
EIODG;
or CMBST
or
INCIN
13105
2,4—Dinitrotoluene
2,4—Dinitrotoiuene
121—14—2
0.32
140
13106
2,6—Dinitrotoluene
2,6—Dinitrotoluene
606—20—2
0.55
28
U107
Di—n—octyl
phthalate
Di—n—octyi phthaiate
117—84—0
0.017
28
374
13108
1, 4—Dioxane
1,4—Dioxane
123—91-1
(WETOX or
CMBST
CUOXD)
fb
CARBN; or
INCIN
1,4—Dioxane; alternate6
123—91—1
NA
170
standard for
nonwastewaters only
Ul09
1,2—Diphenyihydrazine
1,2—Diphenylhydrazine
122-66-7
CHOXD; CURED;
CHOXD;
CURED;
CARBN;
BIODG;
or CMBST
or INCIN
1,2—Di~henvihydrazine;
122—66—7
0.087
NA
alternate6 standard for
wastewaters only
Ullo
DiproPylamine
Diprgpylamine
142—84-7
(WETOX or
INCIN
CHOXD)
fb
CARBN;
or
INCIN
Ui
13.
Di-n—propylnitrosamine
Di—n—propylnitrosamine
621—64—7
0.40
14
13112
Ethyl acetate
Ethyl acetate
141—78-8
0.34
33
13113
Ethyl acrvlate
Ethyl acrvlate
140—88—5
(WETOX or
CMBST
CUOXD)
fb
CAREN;
or
INCIN
13114
Ethylenebisdithiocarbamic acid salts and esters
Ethvienebisdithio-
111-54-6
(WETOX or
INCIN
carbamic acid
CHOXD)
fb
CARBN; or
INCIN
13115
Ethylene oxide
Ethylene oxide
75-21—8
(WETOX or
CUOXD; or
CUOXD’)
fb
INCIN
CARBN;
or
INCIN
Ethylene oxide;
75-21-8
0.12
alternate6 standard for
wastewaters only
U1l6
Ethylene thiourea
375
Ethylene thiourea
96—45-7
(WETOX or
INCIN
CHOXD)
fb
CARBN; or
INCIN
U117
Ethyl ether
Ethyl ether
60—29—7
0.12
160
13118
Ethyl methacrylate
Ethyl methacrviate
97—63—2
0.14
160
13119
Ethyl methane sulfonate
Ethyl methane sulfonate
62-50-0
(WETOX or
INCIN
CHOXD’)
fb
CARBN; or
INCIN
U120
Fluoranthene
Fluoranthene
206-44-0
0.068
3.4
13121
Trichioromonofluoromethane
Trichloromonofluoro-
75—69-4
0.020
30
methane
U122
Formaldehyde
Formaldehyde
50-00-0
(WETOX or
CMBST
CHOXD’) fb
CARBN; or
INCIN
U12
3
Formic acid
Formic acid
64-18-6
(WETOX or
CHEST
CUOXD’) fb
CARBN; or
INCIN
U124
Furan
Furan
110—00—9
(WETOX or
CMBST
CHOXD)
fb
CARBN; or
INCIN
13125
Furfural
Furfural
98—01-1
(WETOX or
CMBST
CHOXD’) fb
CARBN; or
INCIN
U126
Glycidvlaldehyde
376
Glycidyialdehyde
765-34-4
(WETOX or
CMBST
CHOXD) fb
CARBN; or
INCIN
U12 7
Hexachiorobenzene
Hexachlorobenzene
118-74—1
0.055
10
13128
Hexachiorobutadiene
Hexachlorobutadiefle
87—68—3
0.055
5.6
13129
Lindane
alpha—BUC
319—84—6
0.00014
0.066
beta—BUC
319—85—7
0.00014
0.066
delta—BUC
319—86—8
0.023
0.066
gamma—BHC
(Lindane)
58—89—9
0.0017
0.066
13130
Hexachlorocyclopentadiene
Hexachlorocyclopeflta—
77—47—4
0.057
2.4
diene
U13 1
Uexachloroethane
Uexachloroethane
67—72—1
0.055
30
U132
Hexachlorophene
Hexachlorophene
70-30-4
(WETOX or
INCIN
CUOXD)
fb
CARBN; or
INCIN
Ui
33
Hydrazine
Uydrazine
302—01-2
CHOXD; CURED;
CHOXD; CURED;
CARBN; BIODG;
or CMBST
or INCIN
Ui34
Hydrogen fluoride
Fluoride
(measured in
16964—48—B
35
ADGAS fb
wastewaters only)
NEUTR; or
NEUTR
13135
Hydrogen sulfide
Hydrogen sulfide
7783—06—4
CHOXD; CURED;
CUOXD: CURED;
or INCIN
or INCIN
13136
Cacodylic acid
Arsenic
7440-38—2
1.4
5.0
mci/I TCLP
U137
Indeno(1,
2,
3—cd)pyrene
Indeno(1,2,3-cd’)pyrene
193—39—5
0.0055
3.4
377
U138
lodomethane
lodomethane
74-88-4
0.19
65
U140
Isobutyl alcohol
Isobutyl alcohol
78—83—i
5.6
170
13141
Isosafrole
Isosafrole
120—58—1
0.081
2.6
Ui42
Kepone
Kepone
143—50—8
0.0011
0.13
Ui43
Lasiocarpine
Lasiocarpine
303-34—4
(WETOX or
INCIN
CHOXD)
fb
CARBN;
or
INCIN
13144
Lead acetate
Lead
7439—92—i
0.69
0.37 mci/i TCLP
U145
Lead phosphate
Lead
7439—92-i
0.69
0.37
mci/i TCLP
Ui4 6
Lead subacetate
Lead
7439—92—i
0.69
0.37 mci/i TCLP
U147
Maleic anhydride
Maieic anhvdride
108-31—6
(WETOX or
CMBST
CHOXD’) fb
CARBN; or
INCIN
U148
Maieic hydrazide
Maleic hydrazide
123-33—i
(WETOX or
INCIN
CUOXD) fb
CARBN; or
INCIN
13149
Malononitrile
Malononitrile
109-77—3
(WETOX or
INCIN
CHOXD)
fb
CARBN; or
INCIN
U150
Meiphalan
Melphalan
148—82—3
(WETOX or
INCIN
CHOXD’) fb
CARBN;
or
INCIN
378
U15l
(3151 (mercury)
nonwastewaters that contain greater than or equal to
260
mci/kci
total
mercury~
7439—97-6
RNERC
Mercury
13151
13153.
(mercury) nonwastewaters that contain less than
260 mci/kci total mercury
and that are xesidues from R4ERC
only.
0.20 mci/i TCLP
Mercury
7439—97—6
NA
Ui5 1
U151
(mercurY’)
nonwastewaters that contair’
~
~
~fl
and that
are not residues from RMERC only.
Mercury
7439—97—6
NA
13151
All
13151
(mercury) wastewater
Mercury
7439—97—6
____
Ui 51
Element Mercury Contaminated
Mercury
Ui52
Methacrylonitrile
Methacrylonitrile
with Radioactive Materials
7439—97—6
126—98—7
0.24
AMLGM
13153
Methanethiol
Methanethiol
74—93—1
(WETOX or
CUOXD’)
fb
CARBN; or
INCIN
INCIN
(3154
Methanol
Methanol
67—56-1
Methanol; alternate6 set
67—56—1
of standards for both
wastewaters and
nonwastewaters
Ui55
Methapyrilene
Methapyrilene
_______
Ui56
Methvi chlorocarbonate
Methyl chlorocarbonate
Ui57
3-Methylcholanthrene
3—Methyicholanthrene
79—22—1
(WETOX or
CUOXD)
fb
CARBN; or
INCIN
INCIN
.
ma/kci total mercury
0.025
mci/i
TCLP
0.15
84
(WETOX or
CUOXD)
fb
CARBN; or
INCIN
5.6
0.081
91—80—5
CMBST
0.75 mci/i TCLP
1.5
56—49—5
0.0055
15
379
Ui 58
4,4’
—Methylene bis(2—chloroaniline)
4,4’—Methylene bis(2—
101—14—4
0.50
30
chloroanilme)
13159
Methyl ethyl ketone
Methyl ethyl ketone
78—93—3
0.28
36
13160
Methyl ethyl ketone peroxide
Methyl ethyl ketone
1338-23-4
CHOXD; CURED;
CHOXD;
CURED;
peroxide
CARBN; BIODG;
or CMBST
or INCIN
U161
Methyl isobutyl ketone
Methyl isobutyl ketone
108-10—1
0.14
33
(3162
Methyl methacryiate
Methyl methacrylate
80—62—6
0.14
160
13163
N—Methyl-N’ —nitro-N-nitrosoguanidine
N—Methyl—N’—nitro—N-
70—25—7
(WETOX or
INCIN
nitrosoguanidine
CHOXD)
fb
CARBN;
or
INCIN
U164
Methylthiouracii
Methyithiouracil
56—04—2
(WETOX or
INCIN
CHOXD’) fb
CARBN;
or
INCIN
13165
Naphthalene
Naphthalene
91—20-3
0.059
5.6
Ui66
1,
4—Naphthoguinone
1,4-Naphthoguinone
130-15-4
(WETOX or
CMBST
CHOXD)
fb
CARBN; or
INCIN
13167
1—Na~hthylamine
1—Naphthylamine
134-32-7
(WETOX or
INCIN
CUOXD’) fb
CARBN; or
INCIN
13168
2-Naphthylamine
2—Naphthylamine
91—59-8
0.52
INCIN
Ui69
Nitrobenzene
Nitrobenzene
98—95—3
0.068
14
380
U170
p—Nitrophenol
p—Nitrophenol
100—02—7
0.12
29
Ui71
2—Nitropropane
2—Nitropropane
79-46-9
(WETOX or
INCIN
CUOXD’)
fb
CARBN; or
INCIN
Ui72
N—Nitrosodi—n—butvlamine
N—Nitrosodi-n—butylamine
924—16-3
0.40
17
Ui73
N—Nitrosodiethanolamine
N—Nitrosodiethanolamine
1116-54—7
(WETOX or
INCIN
CHOXD) fb
CARBN; or
INCIN
13174
N—Nitrosodiethylamine
N—Nitrosodiethyiamine
55-18—S
0.40
28
13176
N-Nitroso-N—ethylurea
N-Nitroso—N-ethvlurea
759-73-9
(WETOX or
INCIN
CHOXD) fb
CARBN; or
INCIN
Ui77
N—Nitroso-N—xnethylurea
N-Nitroso-N-methvlurea
684-93-5
(WETOX or
INCIN
CUOXD)
fb
CARBN; or
INCIN
13178
N—Nitroso-N—methylurethane
N—Nitroso-N-methyl-
615-53-2
(WETOX or
INCIN
urethane
CHOXD)
fb
CARBN; or
INCIN
13179
N—Nitrosopiperidine
N—Nitrosopiperidine
100—75—4
0.013
35
13180
N-Nitrosopyrrolidine
N—Nitrosopvrroiidine
930—55—2
0.013
35
13181
5—Nitro—o—toluidine
5—Nitro—o—toluidine
99-55—8
0.32
28
Ui82
Paraldehyde
381
Paraldehyde
123-63-7
(WETOX or
CMBST
CHOXD)
fb
CARBN; or
INCIN
13183
Pentachlorobenzene
Pentachlorobenzene
608—93—5
0.055
10
U184
Pentachioroethane
Pentachloroethane
76—01—7
(WETOX or
INCIN
CHOXD)
fb
CARBN;
or
INCIN
Pentachloroethane;
76—01—7
0.055
6.0
alternate6 standards for
both wastewaters and
nonwastewaters
13185
Pentachloronitrobenzerie
Pentachioronitrobenzene
82—68—8
0.055
4.8
13186
1, 3—Pentadiene
1,3—Pentadiene
504-60—9
(WETOX or
CHEST
CUOXD)
fb
CARBN;
or
INCIN
13187
Phenacetin
Phenacetin
62—44—2
0.081
16
Ui88
Phenol
Phenol
108-95—2
0.039
6.2
Ui 89
Phosphorus
sulfide
Phosphorus
sulfide
1314-80-3
CHOXD;
CURED;
CUOXD; CURED;
or INCIN
or INCIN
Ui90
Phthalic anhydride
Phthaiic anhydride
100—21—0
0.055
28
(measured
as
Phthalic
acid
or
Terephthalic
acid)
Phthalic anhydride
85—44—9
0.055
28
U191
2—Picoline
2-Picoline
109-06-8
(WETOX or
INCIN
CUOXD)
fb
CARBN;
or
INCIN
U192
pronamide
Pronamide
23950—58—5
0.093
1.5
382
13193
1,3—Propane suitone
1,3—Propane sultone
1120-71-4
(WETOX or
INCIN
CUOXD)
fb
CARBN;
or
INCIN
U19 4
n-Propylainine
n-Propylarnine
107—10-8
(WETOX or
INCIN
CHOXD)
fb
CARBN; or
INCIN
13196
Pyridine
Pyridine
110—86—1
0.014
16
U19 7
p—Benzoguinone
p-Benzoguinone
106—51-4
(WETOX or
CMBST
CHOXD)
fb
CARBN;
or
INCIN
U200
Reserpine
Reserpine
50-55—5
(WETOX or
INCIN
CHOXD)
fb
CARBN; or
INCIN
13201
Resorcinol
Resorcinol
108—46-3
(WETOX or
CMBST
CHOXD)
fb
CARBN;
or
INCIN
13202
Saccharin and salts
Saccharin
81—07—2
(WETOX or
INCIN
CUOXD)
fb
CARBN; or
INCIN
13203
Safrole
Safrole
94—59—7
0.081
U204
Selenium dioxide
Selenium
7782-49—2
0.82
0.16 mg/i TCLP
U205
Selenium sulfide
Selenium
7782—49—2
0.82
0.16 ma/i TCLP
U206
Streptozotoc in
383
Streptozotocin
18883—66-4
(WETOX or
INCIN
CHOXD)
fb
CARBN;
or
INCIN
U207
1,2,4,5—Tetrachlorobenzene
1,2,4,5—Tetrachloro—
95—94—3
0.055
14
benzene
U208
1, 1,1,
2—Tetrachloroethane
1,1,i,2—Tetrachloro—
630—20—6
0.057
6.0
ethane
U209
1, 1,2,
2—Tetrachloroethane
i,1,2,2—Tetrachloro—
79—34—5
0.057
6.0
ethane
13210
Tetrachloroethylene
Tetrachloroethylene
127—18—4
0.056
6.0
13211
Carbon
tetrachloride
Carbon
tetrachioride
56—23—5
0.057
6.0
13213
Tetrahydrofuran
Tetrahydrofuran
109999
(WETOX or
CMBST
CUOXD)
fb
CARBN; or
INCIN
U214
Thallium
(I)
acetate
Thallium
(measured
in
7440-28—0
1.4
RTHRI4;
or
wastewaters only’)
STABL
13215
Thallium
(I)
carbonate
Thallium
(measured in
7440-28—0
LA
RTHRM; or
wastewaters only)
STABL
13216
Thallium
(I)
chloride
Thallium
(measured in
7440—28-0
1.4
RTURM; or
wastewaters only’)
STABL
U217
Thallium
(I)
nitrate
Thallium
(measured in
7440280
LA
RTHRM; or
wastewaters only)
STABL
13218
Thioacetamide
Thioacetamide
62555
(WETOX or
INCIN
CUOXD) fb
CARBN;
or
I NCIN
384
U219
Thiourea
Thiourea
62—56-6
(WETOX or
INCIN
CHOXD’) fb
CARBN; or
INCIN
13220
Toluene
Toluene
108—88—3
0.080
13221
Toluenediamine
Toluenediamine
25376-45—8
CARBN;
or
CHEST
INCIN
13222
o—Toluidine hydrochloride
o-Toluidine hydro-
636-21—S
(WETOX or
INCIN
chloride
CHOXD)
fb
CARBN; or
INCIN
U223
Toluene diisocyanate
Toluene
diisocyanate
26471-62-5
CARBN; or
CMBST
INCIN
13225
Bromoform (Tribromomethane’)
Bromoform (Tribromo—
75—25-2
0.63
15
methane)
U226
1,1,1—Trichioroethane
i,l,i—Trichloroethane
71—55—6
0.054
U227
1,1,2—Tricloroethane
1,l,2—Tricloroethane
79—00-5
0.054
6.0
U228
Trichioroethylene
Trichioroethylene
79—01-6
0.054
U234
1,3,5—Trinitrobenzene
i,3,5-Trinitrobenzene
99-35-4
(WETOX or
INCIN
CHOXD) fb
CARBN; or
INCIN
U23S
tris— (2
,
3—Dibromopropyl)-phosphate
tris—(2,3—Dibromo—
126—72—7
0.11
0.10
propyi)-phosphate
U236
Trypan Blue
385
Trypan Blue
72-57—1
(WETOX or
INCIN
CUOXD)
fb
CARBN; or
INCIN
U237
Uracil mustard
Uracil mustard
66—75—i
(WETOX or
INCIN
CHOXD) fb
CARBN; or
-
INCIN
13238
Urethane
(Ethyl
carbarnate)
Urethane
(Ethyl
51-79-6
(WETOX or
INCIN
carbaxnatel
CHOXD’) fb
CARBN; or
INCIN
13239
Xvienes
Xylenes—mixed
isomers
1330—20—7
0.32
30
(sum of o—, m-,
and p-
xvlene concentrations)
13240
2,4—D
(2,4—Dichlorophenoxyacetic acid)
2,4—D
(2,4—Dichloro—
94—75—7
0.72
10
phenoxyacetic acid)
2,4—D
(2,4—Dichloro—
NA
(WETOX or
INCIN
phenoxyacetic
acid)
CHOXD)
fb
salts and esters
CARBN;
or
INCIN
U2 43
Hexachloropropylene
Uexachloropropyiene
1888—71—7
0.035
30
13244
Thiram
Thiram
137—26-8
(WETOX or
INCIN
CHOXD)
fb
CARBN; or
INCIN
U246
Cyanocien bromide
Cyanogen bromide
506-68-3
CHOXD; WETOX;
CHOXD; WETOX;
or INCIN
or INCIN
13247
Methoxvchior
Methoxychior
72—43—5
0.25
0.18
U248
Warfarin,
& salts, when present at concentrations of 0.3
or less
Warfarin
81-8i-2
(WETOX or
CMBST
CUOXD)
fb
CARBN; or
INCIN
386
13249
Zinc phosphide, Zn~,, when present at concentrations of
10
or less
Zinc Phosphide
1314—84-7
CUOXD; CURED;
CUOXD; CHREDJ
or INCIN
or INCIN
13328
o—Toluidine
o-Toluidine
95—53-4
INCIN; or
INCIN; or
CHOXD fb
Thermal
(BIODG or
Destruction
CARBN); or
BIODG fb CARBN
U353
p—Toluidine
p-Toluidine
106-49—0
INCIN;
or
INCIN; or
CHOXD
fb
Thermal
(BIODG
or
Destruction
CARBN); or
BIODG fb CARBN
U3 59
2—Ethoxyethanol
2-Ethoxyethanol
110-80—5
INCIN;
or
CHEST
CHOXD fb
(BIODG or
CAREN); or
BIODG fb CARBN
Notes:
1
The waste descriptions provided in this
table do not replace waste
descriptions in 35 Ill. Adm. Code
721.
Descriptions
of Treatment or
Regulatory Subcategories
are provided, as needed, to distinguish between
applicability of different standards.
2
CAS means Chemical Abstract Services.
When the waste code or regulated
constituents are described as a combination of a chemical with its salts
or eaters,
the CAS number is given
for the parent compound only.
3
Concentration standards for wastewaters
are expressed
in mg/i are based
on analysis of composite samples.
4
All treatment
standards expressed as a Technology Code or combination of
Technology Codes are explained in detail in 35 Ill. Adm. Code 728.Table
C, “Technology Codes and Descriptions of Technology—Based
Standards”.
“fb” inserted between waste codes denotes “followed by”,
so that the
first-listed treatment
is followed by the second—listed treatment.
“;“
separates alternative treatement
schemes.
5
Except for Metals
(EP or TCLP’) and Cyanides
(Total and Amenable) the
nonwastewater treatment standards expressed as a concentration were
established,
in part,
based upon incineration
in units operated in
accordance with the technical requirements of
35 Iii.
Adm. Code
724.Subpart 0 or 35
Ill.
Adm.
Code 725.Subpart
0, or based upon
combustion
in
fuel
substitution
units
operating
in
accordance
with
applicable technical requirements.
A facility may comply with these
treatment
standards
according
to
provisions
in
35
Ill.
Adm.
Code
728.140(d).
All
concentration
standards
for
nonwastewaters
are
based on
analysis of grab samples.
6
Where an alternate treatment standard or set of alternate standards has
387
been
indicated,
a facility may comply with this alternate standard,
but
only for the Treatment or Regulatory Subcategory or physical form (i.e.,
wastewater or rionwastewater)
specified for that alternate standard.
7
Both Cyanides
(Total) and Cyanides
(Amenable’) for nonwastewaters are to
be analyzed using Method 9010 or 9012,
found in “Test Methods for
Evaluating Solid Waste, Physical or Chemical Methods”, U.S. EPA
Publication SW—846,
as incorporated by reference in
35 Ill. Adin. Code
720.111, with
a sample size of
10 grams and a distillation time of one
hour and 15 minutes.
NA
means not applicable.
(Source:
Added
at 19
Ill. Reg.
_______,
effective
_____________________
Section 728.Table U
Universal Treatment Standards
(UTS)
Nonwastewater
Standard
Concentration
Wastewater
(in mg/kg3
Standard
unless noted as
Regulated Constituent—
Concentration
“mg/i TCLP”)
Common Name
CAS’ No.
(in mg/i2)
Acenaphthylene
208-96-8
0.059
3.4
Acenaphthene
83-32—9
0.059
3.4
Acetone
67—64—i
0.28
160
Acetonitrile
75—05—8
5.6
1.8
Acetophenone
96-86—2
0.010
9.7
2—Acetylaminofluorene
53—96—3
0.0S9
140
Acrolein
107-02—8
0.29
NA
Acrylainide
79—06—1
19
23
Acrylonitrile
107—13—1
0.24
84
Aldrin
309—00—2
0.021
0.066
4—Anhinobiphenyl
92—67-i
0.13
NA
Aniline
62—53—3
0.81
14
Anthracene
120—12—7
0.059
3.4
Ararnite
140—57—8
0.36
NA
aipha—BUC
319—84—6
0.00014
0.066
beta—BUC
319—85—7
0.00014
0.066
delta—BUC
319—86—8
0.023
0.066
garnrna—BUC
58—89—9
0.0017
0.066
Benzene
71-43-2
0.14
10
388
Benz(a)anthracene
56—55-3
98—87—3
205—99—2
207—08-9
191—24—2
50—32—8
75—27—4
74-83—9
0.059
0.055
0.11
0.11
0.0055
0.061
0.35
0.11
3.4
6.0
6.8
6.8
1.8
3.4
15
15
Benzal chloride
Benzo(b)fluoranthene
(difficult to
distinguish from
benzo(k)fluoranthene)
Benzo(k)fluoranthene
(difficult to
distinguish from
benzo(b) fluoranthene)
Benzo(g,h,i)peryiene
Benzo(a)pyrene
Bromodichioromethane
Methyl bromide
(Bromo-
methane)
4—Bromophenyl phenyl
101—55—3
0.055
15
ether
n—Butyl
alcohol
71—36—3
85—68—7
88—85—7
75—15-0
56—23—5
57—74—9
106—47—8
108—90—7
5.6
0.017
0.066
3.8
0.057
0.0033
0.46
0.057
2.6
28
2.5
4.8 mg/i TCLP
Butyl benzyl phthaiate
2—sec—Eutyl—4,6—dinitro—
phenol
(Dinoseb)
Carbon disulfide
Carbon tetrachloride
6.0
0.26
16
6.0
Chlordane (alpha and
gamma isomers)
p—Chloroaniline
Chlorobenzene
Chlorobenzilate
510—15—6
126—99—8
124-48-1
75—00—3
0.10
0.057
0.057
0.27
NA
0.28
15
6.0
2—Chloro—i,3-butadiene
Chlorodibromomethane
Chloroethane
bis(2—Chloro—
ethoxv)methane
bis(2—Chloroethyl)ether
111—91—1
111—44—4
67—66—3
0.036
0.033
0.046
7.2
6.0
6.0
Chloroform
bis(2—Chloro—
isopropyi
) ether
108—60—i
0.055
7.2
389
p-Chloro—m-cresol
59—50—7
0.018
14
2-Chloroethvl vinyl
110-75—8
0.062
NA
ether
Chloromethane
(Methyl
74-87—3
0.19
30
chloride)
2—Ch.oronapKthalene
91—58-7
0.055
2—Chiorophenol
95—57-8
0.044
5.7
3—Chloropropvlene
107—OS—i
0.036
30
Chrysene
218-01—9
0.059
3.4
o-Cresol
95—48—7
0.11
5.6
m—Cresol
(difficult
to
108—39—4
0.77
5.6
distinguish from p-
cresol)
p—Cresol
(difficult to
106—44—5
0.77
5.6
distinguish from m-
cresol)
cyclohexanone
108—94-1
0.36
0.7S ma/l TCLP
1,2—pibromo—3—chloro-
96—12-8
0.11
15
propane
EthYlene dibromide
106-93—4
0.028
15
(1,2-Dibromoethane)
Dibromomethane
74—95-3
0.11
15
2,4—D
(2,4—Dichloro—
94—75-7
0.72
10
phenoxyacetic
acid’)
o,p’—DDD
S3—l9—0
0.023
0.087
p,p’—DDD
72—54—8
0.023
0.087
o,p’—DDE
3424—82—6
0.031
0.087
p,p’—DDE
72—S5—9
0.031
0.087
o,p’—DDT
789—02—6
0.0039
0.087
p,p’—DDT
50—29—3
0.0039
0.087
Dibenz(a,h)anthracene
53—70—3
0.055
8.2
Dibenz(a,e)Pyrene
192—6S—4
0.061
m-Dichlorobenzerie
541—73—1
0.036
6.0
o-Dichlorobenzene
9S—S0—1
0.088
6.0
p-Dichlorobenzene
106—46—7
0.090
6.0
Dichiorpdifluoromethafle
75-71—8
0.23
7.2
390
i,i—Dichloroethane
75—34—3
107—06—2
0.059
0.21
6.0
6.0
1,2—Dichioroethane
i,i-Dichloroethylene
75—35—4
156—60—5
0.025
0.054
6.0
30
trans—1,2—Dichloro—
ethylene
2,4—Dichlorophenoi
120—83—2
87—65—0
0.044
0.044
3~
14
2,6—Dichlorophenol
1,2-Dichloro~roPane
cjs—l,3—Dichioro—
78—87—5
10061—01—5
0.85
0.036
18
18
p~ppvlene
tranp—1,3—Dichloro—
10061—02—6
0.036
18
propylene
Dieldrin
60—57—1
0.017
0.13
Diethyi phthalate
84-66-2
105-67—9
131—11—3
84—74—2
100—25—4
534—S2—1
51—28—5
121—14—2
606—20—2
117—84—0
60—11—7
621-64—7
123—91—1
0.20
0.036
0.047
0.057
0.32
0.28
0.12
0.32
0.55
0.017
0.13
0.40
NA
28
14
28
28
2.3
160
160
140
28
28
NA
14
170
2,4—Dimethyl phenol
Dimethy.
phthalate
Di—n—butyl phthalate
1,4—Dinitrobenzene
4,6—Dinitro—o—cresol
2,4—Dinitrophenol
2,4—Dinitrotoluene
2,6—fljnitrotoluene
Di—n—octyi phthaiate
p—Dimethylaminoazo—
benzene
Di-n-propylnitrosamine
1,4-Dioxane
Diphenylamine
(difficult
122—39—4
86—30—6
0.92
0.92
13
13
to distinguish from
diphenylnitrosarnirie
I
Djphenylnitrosamine
(difficult to
distinciuiahfrom
di~henviaxnine)
1,2—Diphenylhydrazine
122—66—7
298—04—4
0.087
0.017
NA
6.2
Disulfoton
391
Endosulfan
I
939—98—8
0.023
0.066
Endosulfan II
33213—6—5
0.029
0.13
Endosulfan sulfate
1-31—07—8
0.029
0.13
Endrin
72—20—8
0.0028
0.13
Endrin aldehyde
7421—93—4
0.025
0.13
Ethyl
acetate
141-78—6
0.34
33
Ethyl
cyanide
107—12—0
0.24
360
(Propanenitrile)
Ethyl benzene
100—41—4
0.057
10
Ethyl ether
60-29—7
0.12
160
bis(2—Ethylhexyl)
117—81—7
0.28
28
phthalate
Ethyl methacrylate
97—63—2
0.14
160
Ethylene oxide
75—21—8
0.12
NA
Famphur
52—85—7
0.017
15
Fiuoranthene
206-44—0
0.068
3.4
Fluorene
86—73—7
0.059
Heptachlor
76—44—8
0.0012
0.066
Heptachior epoxide
1024—57—3
0.016
0.066
Hexachiorobenzene
118-74—1
0.055
Hexachiorobutadiene
87—68—3
0.055
5.6
Hexachloro—
77—47-4
0.057
2.4
cyclopentadiene
HxCDD8
(All Hexachloro—
NA
0.000063
0.001
dibenzo—p—dioxins)
HxCDF5
(All Hexachloro—
NA
0.000063
0.001
dibenzofurans)
Hexachloroethane
67—72-i
0.055
Hexachloropropylene
1888—71—7
0.035
Indeno
(.,2,3—c,d)
193—39—5
0.0055
3.4
pyrene
Iodomethane
74—88-4
0.19
65
Isobutyl alcohol
78—83-1
170
Isodrin
465—73—6
0.021
0.066
392
I sosafrole
Kepone
Methacrvlonitrile
Methanol
Metha~vrilene
Methoxvchior
3-Methvlcholanthrene
4, 4—Methylene his (2-
chloroaniline)
Methvlene chloride
Methvi ethyl ketone
MethYl ipobutyl ketone
MethYl methacrvlate
MethYl methansulfonate
MethYl
parathion
Naphthaiene
p-Naphthylainine
o-Nitroanilme
p-Nitroaniline
Nitrobenzene
5-Nitro-o—toiuidine
o-Nitrophenol
~-Nitrophenol
N-NitrosodiethVlaxfline
N-Nitrosodimethvlamine
N-Nitroao—di-n-butyl-
amine
N-Nitrosomethvlethyl—
amine
N—NitrosomorphOime
120—58—i
143—50—8
126—98—7
67—56—1
91—80—S
72—43—5
S6—49—5
101—14—4
75—09—2
78—93—3
108—10—1
80—62—6
66—27—3
298—00—0
91—20—3
91—59—8
88—74—4
100—01—6
98—95—3
99—55—8
88—75—S
100—02—7
55—18—5
62—75—9
924—16—3
10595—9S—6
59—89—2
100—7S—4
930—55—2
56—38—2
0.081
0.0011
0.24
5.6
0.08 1
0.25
0. 0055
0.50
0.089
0.28
0.14
0.14
0.018
0.014
0.059
0.52
0.27
0.028
0.068
0.32
0.028
0.12
0.40
0.40
0.40
0.40
0.40
0.013
0.013
0.0i4
2.6
0.13
84
0.75
mci/i TCLP
1.5
0.18
15
30
30
36
33
160
NA
4.6
5.6
NA
14
28
14
28
13
29
28
2.3
17
2.3
2.3
35
35
4.6
N—Nitrosopiperidine
N—Nitrosopyrrolidine
Parathion
393
Total PCBs
(sum of all
1336—36-3
0.10
10
PCB
isomers,
or
all
Aroclorsi
Pentachiorobenzene
608—93-5
0.055
10
PeCDDs
(All Pentachioro—
NA
0.000063
0.001
dibenzo-p-dioxins)
PeCDFs
(All Pentachloro—
NA
0.000035
0.001
dibenzofurans)
Pentachioroethane
76-01—7
0.055
6.0
Pentachloronitrobenzene
82—68—8
0.05S
Pentach1oro~heno1
87-86—S
0.089
7.4
Phenacetin
62—44—2
0.081
16
Phenanthrene
85-01—8
0.059
5.6
Phenol
108—95—2
0.039
6.2
Phorate
298—02-2
0.021
4.6
Phthalic acid
100—21-0
0.055
28
Phthalic
anhydride
85—44—9
0.055
28
Pronamide
23950—58—S
0.093
1.5
Pyrene
129—00-0
0.067
8.2
Pyridine
110—86—1
0.014
16
Safroie
94—59—7
0.081
22
Silvex
(2,4,5—TP)
93—72—1
0.72
7.9
2,4,5—T
93—76—5
0.72
7.9
(2 ,4,5—Trichioro—
phenoxyacetic acid)
1,2,4,5—Tetrachioro—
95—94—3
0.055
14
benzene
TCDDS
fAil Tetrachloro—
NA
0.000063
0.001
dibenzo-p—dioxins)
TCDF5
(All Tetrachloro—
NA
0.000063
0.001
dibenzofurans)
i,i,1,2—Tetrachloro—
630—20—6
0.057
6.0
ethane
1,i,2,2—Tetrachloro—
79—34—6
0.057
6.0
ethane
Tetrachioroethyiene
127-18—4
0.056
394
2,3,4,6—Tetrachloro—
58—90—2
0.030
phenol
Toluene
108-88-3
0.080
10
Toxaphene
8001-35-2
0.0095
2.6
Bromoform
(Tribromo—
75—25—2
0.63
15
methane)
1,2,4—Trichlorobenzene
120—82—1
0.055
19
1,l,i—Trichloroethane
71—55—6
0.0S4
6.0
i,1,2—Trichloroethane
79-00—5
0.054
6.0
Trichloroethyiene
79—01—6
0.054
6.0
Trichioromonofluoro-
75—69-4
0.020
30
methane
2,4,5—Trichlorophenol
9S-95—4
0.18
7.4
2,4,6—Trichlorophenol
88-06—2
0.035
7.4
l,2,3—Trichloropropane
96-18—4
0.85
30
l,i,2—Trichloro—1,2,2—
76—13—i
0.057
30
trifluoroethane
tris—(2,3—Dibromopropyl’)
126—72—7
0.11
0.10
phosphate
Vinyl chloride
75-01—4
0.27
6.0
Xylenes—mixed isomers
1330-20-7
0.32
30
(sum of
o—,
m—,
and p—
xylene concentrations)
Antimony
7440—36—0
Li
2.1 mg/i TCLP
Arsenic
7440-38—2
LA
5.0 mg/i TCLP
Barium
7440-39—3
Li
7.6 mg/i TCLP
Beryllium
7440—41—7
0.82
0.014 mg/l TCLP
Cadmium
7440—43—9
0.69
0.19
mci/i TCLP
Chromium
(Total’)
7440—47—3
2.77
0.86
mci/i TCLP
Cyanides
(Total)4
57—12—5
590
Cyanides
Amenable)4
S7—12—S
0.86
30
Fluoride
16964—48—8
Lead
7439—92—i
0.69
0.37 ma/l TCLP
Mercury—Nonwastewater
7439-97—6
0.20 mg/i TCLP
from Retort
395
Mercury—All Others
7439-97—6
0.15
0.025 mg/i TCLP
Nickel
7440—02—0
3.98
5.0
mci/i TCLP
Selenium
7782—49—2
0.82
0.16 mg/i TCLP
Silver
7440—22—4
0.43
0.30
mci/i TCLP
Sulfide
8496—25—8
14
NA
Thallium
7440-28—0
LA
0.078 mci/i TCLP
Vanadium5
7440-62—2
4.3
0.23 mg/i TCLP
Zinc5
7440—66—6
2.61
5.3 mg/i TCLP
1
CAS means Chemical Abstract Services.
When the waste code or regulated
constituents are described as
a combination of
a chemical with its salts
or esters,
the CAS number is given for the parent compound only.
2
Concentration standards
for wastewaters are expressed
in mg/i are based
on analysis of composite samples.
3
Except for metais
(EP or TCLP)
and cyanides
(total and amenable),
the
nonwastewater treatment standards expressed as
a concentration were
established,
in part,
based on incineration
in units operated in
accordance with the technical requirements of 35
Ill. Adm. Code
724.Subpart 0 or
35
Iii.
Adm. Code 725.Subpart
0
or
on
combustion
in
fuel substitution units operating
in accordance with applicable
technical requirements.
A facility may comply with these treatment
standards according to provisions
in 40 CFR 268.40(d).
All
concentration standards for nonwastewaters are based on anaiysis of grab
samples.
4
Both Cyanides
(Total)
and Cyanides
(Amenable)
for nonwastewaters are to
be analyzed using Method 9010 or 9012,
found in “Test Methods
for
Evaluating Solid Waste,
Physical/Chemical Methods”,
U.S. EPA Publication
SW—846,
incorporated by reference in 35
Ill.
Adrn.
Code 720.111, with a
sample size
of
10 grams and a distillation time of one hour and
15
minutes.
5
Vanadium and zinc are not “underlying hazardous constituents”
in
characteristic wastes, according to the definition at Section
728.102(i).
Note: NA means not applicable.
(Source:
Added at
19
Iii.
Reg.
,
effective
_____________________
TITLE 35:
ENVIRONMENTAL PROTECTION
SUBTITLE
G:
WASTE DISPOSAL
CHAPTER
I:
POLLUTION CONTROL BOARD
SUBCHAPTER d:
UNDERGROUND INJECTION CONTROL
AND
UNDERGROUND
STORAGE TANK
PROGRAMS
PART
730
UNDERGROUND INJECTION CONTROL OPERATING REQUIREMENTS
SUBPART A:
GENERAL
Section
730.101
Applicability,
Scope and Effective Date
396
730.102
Laws Authorizing Regulations
730.103
Definitions
730.104
Criteria
for
Exempted
Aquifers
730.105
Classification of Injection Wells
730.106
Area of Review
730.107
Corrective Action
730.108
Mechanical Integrity
730.109
Criteria for Establishing Permitting Priorities
730.iiO
Plugging and Abandoning Class
I and Class III Wells
SUBPART B:
CRITERIA
AND
STANDARDS APPLICABLE
TO
CLASS
I
NON—HAZARDOUS WELLS
Section
730.111
Applicability
730.112
Construction Requirements
730.113
Operating, Monitoring and Reporting Requirements
730. 114
Information to be Considered by the Agency
SUBPART
C:
CRITERIA AND STANDARDS APPLICABLE
TO CLASS II WELLS
Section
730.121
Adoption of Criteria and Standards Applicable to Class II Wells by
the Illinois Department of Mines
and Minerals
SUBPART
0:
CRITERIA AND STANDARDS APPLICABLE
TO CLASS III WELLS
Section
730. 131
Applicability
730. 132
Construction Requirements
730.133
Operating, Monitoring~and Reporting Requirements
730.134
Information to be Considered by the Agency
SUBPART
F:
CRITERIA
AND
STANDARDS APPLICABLE
TO CLASS V INJECTION WELLS
Section
730.151
Applicability
730.152
Inventory and Assessment
(Repealed)
SUBPART C:
CRITERIA
AND
STANDARDS APPLICABLE TO CLASS
I
HAZARDOUS WELLS
Section
730.161
Applicability and Definitions
730.162
Minimum Criteria for Siting
730.163
Area of Review
730.164
Correction Action for Wells in the Area of Review
730.165
Construction Requirements
730.166
Logging,
Sampling,
and Testing Prior to New Well Operation
730. 167
Operating Requirements
730.168
Testing and Monitoring Requirements
730.169
Reporting Requirements
730.170
Information to be Evaluated by the Director
730.171
Closure
730.172
Post-Closure Care
730.173
Financial Responsibility for Post-Closure Care
AUTHORITY’:
Implementing Sections 13
and 22.4 and authorized by Section 27
of
the Environmental Protection Act
(415 ILCS 5/13,
22.4,
and 27.
SOURCE:
Adopted in R81-32,
47 PCB 93,
at
6 Iii. Reg.
12479,
effective March
3,
1984;
amended
in R82—19,
53 PCB 131
at
7
Ill.
Reg. 14426~effective March
3,
1984;
recodified at
10
Ill.
Reg.
14174; amended in R89—2
at
14 Ill. Reg.
3130,
effective February 20,
1990;
amended in R89—li at
14 Iii. Req.
11959,
397
effective July
9,
1990;
amended in R93—6
at
17
Ill.
Req. 15646,
effective
September 14,
1993;
amended in P.94—S at 18
Ill.
Reg. 18391,
effective December
20,
1994;
amended in P95—4
at
19 Ill. Reg.
_______,
effective
SUBPART A:
GENERAL
Section 730.104
Criteria for Exempted Aquifers
An aquifer or a portion thereof whiohthat meets the criteria for an
“underground source
of drinking water”
in Section 730.103 may be determined by
the Board under
35
Ill.
Mm.
Code 704.103, 704.i23~and 702.105 to be an
“exempted aquifer”
if
it meets the following criteria:
a)
It does not currently serve as a source of drinking water; and
b)
It cannot now and will not
in the future serve as
a source of
drinking water because:
1)
It
is mineral, hydrocarbon~or geothermal energy producing,
or
can
be
dcmonotrated
by
a
permit
applicant
~
demonstrate,
as part of a permit application for a Class
II
or III opcrationin-)ection well, that the aquifer be—contains
minerals or hydrocarbons that considering their quantity and
location are expected to be commercially producible consid-
ering their quantity and location
2)
It
is situated at
a depth or location whichthat makes
recovery of water for drinking water purposes economically
or technologically impractical;
3)
It
is
so contaminated that
it would be economically or
technologically impracticai to render that water fit
for
human consumption; or
4)
It
is
located over a Class III well mining area subject to
subsidence or catastrophic collapse; or
C)
The total dissolved solids content of the groundwater
is more than
3,000 and less than iO,000 mg/i and the aquifer
is not reasonably
expected to supply a public water system.
(Source:
Amended at 19
Ill. Reg.
,
effective
______________________
Section 730.105
Classification of Injection Wells
Injection wells are classified as follows:
a)
Class
I.
1)
Wells used by generators of hazardous wastes or owners or
operators of hazardous waste management facilities to inject
hazardous waste beneath the lowermost formation containing~
within 402 motoro
(1/4 mug)
of tho wail borg,
an
underground source of drinking water within 402 meters
(1/4
mile)
of the well bore.
2)
Other industrial
and municipal disposal wells whiohthat
inject fluids beneath the lowermost formation containing-r
within 402 motoro
(1/4 mile)
of the well boro,
an
underground source of drinking water within 402 meters
(1/4
398
mile)
of the well bore.
b)
Class II.
Wells whiahthat inject fluids:
1)
WhichThat are brought to the surface
in connection with
conventional oil or natural gas production and which may be
commingled with wastewaters from gas plants ‘.thiohthat are an
integral part of production operations,
unless those waters
are classified
as
a hazardous waste at the time of
injection;
2)
For enhanced recovery of oil or natural gas; and
3)
For Btorage of hydrocarbons whichthat are liquid at standard
temperature and pressure.
c)
Class III.
Wells whichthat inject for extraction of minerals,
including:
1)
Mining of sulfur by the Frasch process;
2)
In situ production of uranium or other metals.
This
category includes only in situ production from ore bodies
~hiohthat have not been conventionally mined.
Solution
mining of
conventional mines~such as stopea ieaching.~is
included
in Class
V-s-; and
3)
Solution mining of salts or potash.
(Board NotcBOARD NOTE:
Class III wells include the recovery
of geothermal energy to produce electric power but do not
include wells used in heating or aquacuiture whichthat fall
under Class
V.-)-
d)
Class
IV.
1)
Wells used by generators of hazardous waste or of
radioactive waste, by owners or operators of hazardous waste
management facilities, or by owners or operators of
radioactive waste disposal sites to dispose of hazardous
waste or radioactive waste into a formation whichthat within
402 mctcr~ (1/4 mile)
of the well contains an underground
source of drinking water within 402 meters
(1/4 mile) of the
well.
2)
Wells used by generators of hazardous waste or of
radioactive waste,
by owners or operators of hazardous waste
management facilities,
or by owners or operators of
radioactive waste disposal
sites to dispose of hazardous
waste or radioactive waste above a formation whichthat
within 402 motoro
(1/4 mUa)
of tho wall contains an
underground source of drinking water within 402 meters
(1/4
mile) of the well.
3)
Wells used by generators of hazardous waste or owners or
operators of hazardous waste management
facilities to
dispose of hazardous waste~-whichthat cannot be classified
under
35
Ill,
Mm.
Coda 730.105 subsection (a)(l)~e~
730.i05(d)(1)~as4or
(d)(2)
above
(e.g., wells used to
dispose of hazardous wastes into or above a formation
whichthat contains an aquifer whichthat has been exempted
pursuant to
35 Iii. Mm. CodeSection 730.104j.
399
e)
Class V.
Injection wells not included in Class
I,
Class II,
Class
III~or Class
IV.
Class V wells include:
1)
Air conditioning return flow wells used to return the water
used in
a heat pump for heating or cooling to the supply
aquifer tho water used for heating or cooling in a heat
pump
2)
Ceespools, including multiple dwelling, community~or
regional cesspoois,
or other devices that receive wastesT
whiohthat have an open bottom and sometimes have perforated
sides.
The UIC requirements do not apply to single family
residential cesspoolB or to non—residential cesepools
whichthat receive solely sanitary wastes and have the
capacity to serve fewer than 20 persons a day;
3)
Cooling water return flow wells used to inject water
previously used for cooling;
4)
Drainage wells used to drain surface fluid, primarily storm
runoff,
into a subsurface formation;
5)
Dry wells used for the injection of wastes into
a subsurface
formation;
6)
Recharge wells used to replenish the water in an aquifer;
7)
Salt water intrusion barrier wells used to inject water into
a fresh water aquifer to prevent the intrusion of salt water
into the fresh water;
8)
Sand backfill and other backfill wells used to inject
a
mixture of water and sand, mill tailings~or other solids
into mined out portions of subsurface mines whether what is
injected is
a radioactive waste or not;
9)
Septic system wells used to inject the waste or effluent
from a multiple dwelling, business establishment,
community~
or regional business establishment septic tank.
The UIC
requirements do not apply to single
family residential
septic system wells, or to nonresidential
septic system
wells whichthat are used solely for the disposal of sanitary
waste and which have the capacity to serve fewer than 20
persons a day-~-~
10)
Subsidence control wells
(not used for the purpose of oil or
natural gas production) used to inject fluids into a non—oil
or gas producing zone to reduce or eliminate subsidence
associated with the overdraft of fresh water;
ii)
Radioactive waste disposal wells other than Class IV wells
12)
Injection wells associated with the recovery of geothermal
energy
for heating, aquaculture or production of electric
power;
13)
Weils used for solution mining of conventional mines such as
stopes leaching;
14)
Wells used to inject spent brine into the same formation
from which
it was withdrawn after extraction of halogens or
their
salts; and
400
15)
Injection wells used in experimental technologies.
(Source:
Amended at
19
Ill. Reg.
________,
effective
_____________________
Section 730.110
Plugging and Abandoning Class
I and Class III Wells
a)
Prior to abandoning a Class
I or Class III well, the well shall be
plugged with cement
in a manner whichthat will not allow the
movement of fluids either into or between underground sources of
drinking water.
The Agency may allow Class III wells to use other
plugging materials if
it
is satisfied that such materials will
prevent movement of
fluids into or, between underground sources of
drinking water.
b)
Placement of the cement plugs shall be accomplished by one of the
following:
1)
The Balance Method;
2)
The Dump Bailer Method;—e*
3)
The Two-Plug Method; or
4)
An alternative method approved by the Agency in the permit-,-
whichthat will reliably provide a comparable level of
protection
to
underground
sources
of
drinking
water.
C)
The well to be abandoned ohallmust be in a state of static
equilibrium with the mud weight equalized top to bottom, either by
circulating the mud in the well
at least once or by a comparable
method prescribed by the Agency, prior to the placement of the
cement plug.
d)
The
plugging
and
abandonment
required
in
35
Ill.
Adm.
Code 704.188
and 704.187 ohail,must also demonstrate adequate protection of
USDWs in the case of
a Class III projoatwell whichthat underlies
or
is in an aquifer whichthat has been exempted under Section
730.104, alao demonstrate adequate protection of UCDWo.
The
Agency shall prescribe aquifer cleanup and monitoring where
it
deems it necessary and feasible to insure adequate protection of
USDWs.
(Source:
Amended at 19
Ill.
Reg.
________,
effective
_____________________-
SUBPART D:
CRITERIA
AND
STANDARDS
APPLICABLE TO CLASS III
WELLS
Section 730.132
Construction Requirements
a)
All new Class III wells 3haiimust be cased and cemented to prevent
the migration of fluids into or between underground sources of
drinking water.
The Agency may waive the cementing requirements
for new wells in existing projects or portions of existing proj-
ects where it has substantial
evidence that no contamination of
underground sources of drinking water would result.
The casing
and cement used in the construction of each newly drilled well
shailmust be designed for the life expectancy of the well.
In
determining and specifying casing and cementing requirements, the
following factors ahaiimust be considered:
1)
Depth to the injection zone;
401
2)
Injection pressure,
external pressure,
internal pressure,
axial loading,
etc.;
3)
Hole size;
4)
Size and grade of all casing strings
(wall thickness,
diameter,
nominal weight,
length,
joint specification~and
construction material);
5)
Corrosiveness of injected fluids and formation fluids;
6)
Lithology of
injection and confining zones;
and
7)
Type and grade of cement.
b)
Appropriate logs and other tests eh~-j~j~jbe conducted during the
drilling and construction of new Class III wells.
A descriptive
report interpreting the results of such logs and tests ohailmust
be prepared by a knowledgeable log analyst and submitted to the
Agency.
The logs and tests appropriate to each type of Class III
well ohalimust be determined based on the intended function,
depth, construction~and other characteristics of the well-,-~
availability of similar data in the area of the drilling site~and
the need for additional information that may arise from time to
time as the construction of the well progresses.
Deviation checks
shailmust be conducted on all holes where pilot holes and reaming
are used,
unless the hole will be cased and cemented by
circuiating cement to the surface.
Where deviation checks are
necessary they ohallmust be conducted at sufficiently frequent
intervals to assure that verticai avenues
for fluid migration in
the form of diverging holes are not created during drilling.
C)
Where the injection zone
is a formation whichthat
is naturally
water—bearing, the following information concerning the injection
zone ahailmust be determined or calculated for new Class III wells
or projects:
1)
Fluid pressure;
2)
Fracture pressure;
and
3)
Physical and chemical characteristics of the formation
fluids.
d)
Where the injection
formation is not a water—bearing formation,
the information
in paragraphsubsection
(c)(2)
above must be
submitted.
e)
Where injection is
into a formation w-h-ichthat contains water with
less than 10,000 mg/i TDS, monitoring wells shall be completed
into the injection zone and into any underground sources of
drinking water above the
injection zone whiohthat could be
affected by the mining operation.
These wells
shall be located in
such a fashion as to detect any excursion of injection
fluids,
process by—products~or formation fluids outside the mining area
or zone.
If the operation may be affected by subsidence or
catastrophic coliapse~the monitoring wells shall be located so
that they will not be physically affected.
f)
Where injection
is into a formation whiohthat does not contain
water with less than 10,000 mg/i TDS, no monitoring wells are
necessary in the injection stratum.
402
g)
Where the injection wells penetrate an USDW in an area subject to
subsidence or catastrophic collapse,
an adequate number of
monitoring wells ahalimust be completed into the USDW to detect
any movement of injected fluids, process by—products~or formation
fluids into the USDW.
The monitoring wells shailmust be located
outside the physical influence of the subsidence or catastrophic
collapse.
h)
In determining the number,
location,
construction and frequency of
monitoring of the monitoring wells the following criteria
a-hallmust be considered:
1)
The population relying on the USDW affected or potentially
affected by the injection operation;
2)
The proximity of the injection operation to points of
withdrawal of drinking water;
3)
The local geology and hydrology;
4)
The operating pressures
and whether
a negative pressure
gradient
is being maintained;
5)
The nature and volume of the injected fluid,
the formation
water,
and the process by—products;
and
6)
The injection well density.
(Source:
Amended at
19
Iii.
Reg.
_______,
effective
_____________________
Section 730.133
Operating, Monitoring4~and Reporting Requirements
a)
Operating Requirements.
Operating requirements prescribed
e-)~-allmust, at
a minimum,
specify that:
1)
Except during well stimulation,
injection pressure at the
wellhead
ohaliinust be calculated so as to assure that the
pressure in the
injection zone during injection does not
initiate new fractures or propagate existing fractures in
the injection zone.
In no case shall injection pressure
initiate fractures in the confining zone or cause the
migration of injection or formation fluids
into an
underground source of drinking water.
2)
Injection between the outermost casing protecting
underground sources of drinking water and the well bore is
prohibited.
b)
Monitoring Requirements.
Monitoring requirements
shall,
at a
minimum,
specify:
1)
Monitoring of the nature of injected fluids with sufficient
frequency to yield representative data on its
characteristics.
Whenever the injection fluid
is modified
to the extent that the analysis required by Section
730.134(a)(7)(C)
is incorrect or incomplete, the owner or
operator shall provide the Agency with a new analysis as
required by Section 730.134(a)(7)(C);
2)
Monitoring of injection pressure and either flow rate or
volume semimonthly,
or metering and daily recording of
injected and produced fluid voiumes1 as appropriate;
403
3)
Demonstration of mechanical integrity pursuant to Section
730.108
at least once every five years during the life of
the well for salt solution mining;
4)
Monitoring of the fluid level in the injection zone semi-
monthly, where appropriate, and monitoring of the parameters
chosen to measure water quality
in the monitoring wells
required by Section 730.132(e) semi—monthly; and
5)
Quarterly monitoring of wells required by Section
730.132(g).
6)
All Class III wells may be monitored on a field or project
basis~rather than onan individual well basis~by manifold
monitoring.
Manifold monitoring may be used in cases of
facilities consisting of more than one injection well-,-
operating with a common manifold.
Separate monitoring
systems for each well are
not required provided the owner7L
~~operator
demonstrates that manifold monitoring
is
comparable to individual well monitoring.
c)
Reporting Requirements.
Reporting requirements shall,
at
a
minimum,
include:
1)
Quarterly reporting to the Agency on required monitoring;
2)
Results of mechanical integrity and any other periodic test
required by the Agency reported with the first regular
quarterly report after the completion of the test; and
3)
Monitoring may be reported on a project or field basis
rather than
individual well basis where manifold monitoring
is used.
(Source:
Amended
at
19
Ill.
Reg.
________,
effective
______________________
SUBPART
F:
CRITERIA AND STANDARDS APPLICABLE
TO CLASS V INJECTION WELLS
Section 730.151
Applicability
This
Subpart sets
forth criteria and standards for underground injection
control programs to regulate all injection not regulated in 730.Subparts
B, D~
and E.
Class
II wells, however,
are not regulated by this Subpart.
a)
Generally, wells covered by this Subpart inject non—hazardous
fluids into or above formations that contain underground sources
of drinking water.
It includes all wells listed in Section
730.105(e) but
is not limited to those types of injection wells.
b)
It also includes wells not covered in ClaBs
IV that
inject
radioactive materials listed in 10 CFR
20, Appendix
B,
Table II,
Column
2.
(Source:
Amended at
19
Ill.
Reg.
________,
effective
_______________
SUBTITLE G~ WASTE DISPOSAL
CHAPTER
I:
POLLUTION CONTROL BOARD
SUBCHAPTER
d:
UNDERGROUND INJECTION CONTROL AND UNDERGROUND
STORAGE TANK PROGRAMS
404
PART
738
HAZARDOUS
WASTE INJECTION RESTRICTIONS
SUBPART A:
GENERAL
Section
738.101
Purpose Scope and Applicability
738.102
Definitions
738.103
Dilution Prohibited as
a Substitute for Treatment
738.104
Case—by—Case Extensions of an Effective Date
738.105
Waste Analysis
SUBPART B:
PROHIBITIONS ON INJECTION
Section
738.110
Waste Specific Prohibitions
—
Solvent Wastes
738.111
Waste Specific Prohibitions
—
Dioxin—Containing Wastes
738.112
Waste Specific Prohibitions
—
California List Wastes
738.114
Waste Specific Prohibitions
—
First Third Wastes
738.115
Waste Specific Prohibitions
-
Second Third Wastes
738.116
Waste Specific Prohibitions
-
Third Third Wastes
738.117
Waste Specific Prohibitions
—
Newly—Listed Wastes
SUBPART C:
PETITION STANDARDS
AND
PROCEDURES
Section
738.120
Petitions to Allow Injection of a Prohibited Waste
738.121
Required Information to Support Petitions
738.122
Submission, Review and Approval or Denial of Petitions
738.123
Review of Adjusted Standards
738.124
Termination of Adjusted Standards
AUTHORITY:
Implementing Section 13
and 22.4 and authorized by Section
27 of
the Environmental Protection Act 415
ILCS 5/13,
22.4 and 27.
SOURCE:
Adopted in P.89—2 at 14
Ill.
Reg.
3059, effective February 20,
1990;
amended in P.89-li at
14
Ill. Reg.
11948, effective July
9,
1990;
amended in
R90—14
at
15
Ill. Reg.
11425, effective July 24,
1991;
amended in R92—l3 at
17
Ill. Reg.
6190,
effective April
5,
1993;
amended in
P.93—6 at
17
Iii.
Reg.
15641, effective September 14,
1993; amended in R95-4 at
19
Iii.
Reg.
________,
effective
______________________
SUBPART B:
PROHIBITIONS ON INJECTION
Section 738.117
Waste Specific Prohibitions
—
Newly-Listed Wastes
a)
The wastes specified in 35
Ill. Adm. Code 72i.Subpart D by the
following U.S. EPA H~azardous Wwaste numbers are prohibited from
underground injection:
F03 7
F038
K107
K108
Ki09
K11O
Kill
K?12
Ki17
K118
K12 3
K124
K12 5
K12 6
405
1(131
1(136
U328
U353
U359
ki.
The wastes specified in 35
Ill. Adm. Code 721.Subpart
D by the
following U.S. EPA hazardous waste numbers are prohibited from
underground injection:
K?41
1(142
K143
Ki44
1(145
K?47
1(148
1(149
1(150
1(151
~J
Effective September
19,
1995,
the wastes specified
in
35
Ill.
Adm.
Code 721.Subpart
C by the following U.S. EPA hazardous waste
numbers are prohibited from underground inlection:
DOOl
(high TOC subcategory,
as specified at 35 Ill.
Adm.
Code 728.140)
D012
D0?3
D014
DO15
DO 16
D017
~)
Effective June 30,
1995, the wastes specified
in
35
Ill.
Adm. Code
721.Subpart D by the following U.S. EPA Mi~azardousW~astenumbers
are prohibited from underground injection:
1(117
1(118
1(13?
1(132
e~)
The requirements of subsections
(a) and
(b)
above do not apply:
1)
If
the
wastes
meet or are treated to meet the applicable
standards specified
in 35 Ill.
Adm.
Code 728.Subpart D;
or
2)
If an adjusted standard has been granted in response to a
petition under 738.Subpart
C of
thia Part
or
3)
During the period of extension of the applicable effective
date,
if an extension
is granted under Section 738.104.
BOARD NOTE:
Derived from 40 CFR 148.17,
as added at
57 Fed.
Reg.
37263
(Aug.
18,
1992).
(Source:
Amended at
19
Iii.
Reg.
________,
effective
______________________
TITLE 35:
ENVIRONMENTAL PROTECTION
SUBTITLE G:
WASTE DISPOSAL
406
CHAPTER
I:
POLLUTION
CONTROL
BOARD
SUBCHAPTER c:
HAZARDOUS
WASTE OPERATING REQUIREMENTS
PART 739
STANDARDS FOR THE MANAGEMENT OF USED OIL
SUBPART A:
DEFINITIONS
Section
739. 100
Definitions
SUBPART B:
APPLICABILITY
Section
739.110
Applicability
739.???
Used oil specifications
739.112
Prohibitions
SUBPART C:
STANDARDS FOR USED OIL GENERATORS
Section
739.120
Applicability
739.121
Hazardous waste mixing
739.122
Used oil storage
739.123
On—site burning in space heaters
739.124
Off—site shipments
SUBPART D:
STANDARDS FOR USED OIL COLLECTION CENTERS AND
AGGREGATION POINTS
Section
739.130
Do—it—your8elfer used oil
collection centers
739.131
Used oil collection centers
739.132
Used oil aggregate points owned by the generator
SUBPART E:
STANDARDS FOR USED OIL TRANSPORTER AND TRANSFER
FACILITIES
Section
739.140
Applicability
739.141
Restrictions on transporters that are not also processors
739.142
Notification
739.143
Used oil transportation
739.144
Rebuttable presumption for used oil
739.145
Used oil storage
at transfer facilities
739.146
Tracking
739.147
Management of residues
SUBPART F:
STANDARDS FOR USED OIL PROCESSORS
Section
739.150
Applicability
739.151
Notification
739.152
General facility standards
739.153
Rebuttable presumption for used oil
739.154
Used oil management
739.155
Analysis plan
739.156
Tracking
739.157
Operating record and reporting
739.158
Off—site shipments of
used oil
739.159
Management of residues
SUBPART G:
STANDARDS FOR USED OIL BURNERS THAT BURN
OFF—SPECIFICATION USED OIL FOR ENERGY RECOVERY
Section
739. 160
Applicability
739.161
Restriction on burning
739.162
Notification
407
739.163
Rebuttable presumption for used oil
739.164
Used oil storage
739.165
Tracking
739.166
Notices
739.167
Management of residues
SUBPART H:
STANDARDS FOR USED OIL FUEL MARKETERS
Section
739.170
Applicability
739.171
Prohibitions
739.172
On—specification used oil fuel
739.173
Notification
739.174
Tracking
739.175
Notices
SUBPART
I:
STANDARDS FOR USE AS A DUST SUPPRESSANT DISPOSAL OF USED OIL
Section
739.180
Applicability
739.181
Disposal
739.182
Use as
a dust suppressant
AUTHORITY:
Implementing Section 22.4 and authorized by Section 27 of the
Environmental Protection Act
(415
ILCS 5/22.4 and 27).
SOURCE:
Adopted
in R93—4 at 17
Ill.
Reg.
20954,
effective November 22,
1993;
amended in R93—16 at
18 Iii. Reg.
6931, effective April
26,
1994; amended in
P.94—17
at
18 Ill. Reg.
17616, effective November
23,
1994;
amended in P.95—6 at
19
Ill. Reg.
________,
effective
_____________________
SUBPART B:
APPLICABILITY
Section 739.110
Applicability
This Section identifies those materials which are subject to regulation as
used oil under this Part.
This Section also identifies some materials that
are not subject to regulation as used oil under this Part,
and indicates
whether these materials may be subject to regulation as hazardous waste under
Parts
702,
703,
720 through 726,
and 728.
a)
Used oil.
U.S. EPA presumes that used oil
is to be recycled
unless a used oil handler disposes of used oil, or sends used oil
for disposal.
Except as provided in Section 739.111, the
regulations of this Part apply to used oil, and to materials
identified in this Section as being subject to regulation as used
oil, whether or not the used oil or material exhibits any
characteristics of hazardous waste identified in 35 Ill.
Adm. Code
721.Subpart
C.
b)
Mixtures of used oil and hazardous waste.
1)
Listed hazardous waste.
A)
A mixture of used oil and hazardous waste that is
listed
in
35
Iii.
Adm. Code 72l.Subpart D
is
subject
to regulation as hazardous waste under 35
Ill. Adm.
Code
703,
720 through 726,
and
728, rather than as
uaed oil under this Part.
B)
Rebuttable presumption for used oil.
Used oil
containing more than 1,000 ppm total halogens is
presumed to be a hazardous waste because
it has been
408
mixed with halogenated hazardous waste listed in
35
Ill.
Adm. Code 721.Subpart D.
Persons may rebut this
presumption by demonstrating that the used oil does
not contain hazardous waste
(for example, by using an
analytical method from SW—846, Edition III, to show
that the used oil does not contain significant
concentrations of halogenated hazardous constituents
listed in 35
Ill. Mm.
Code 72i.Appendix H).
U.S. EPA
Publication SW—846,
Third Edition,
is available from
the Government Printing Office, Superintendent of
Documents,
P.O.
Box 371954,
Pittsburgh,
PA 15250-7954,
(202)
783—3238
(document number 95S—001—00000—1).
i)
The rebuttable presumption does not apply to
metalworking oils or fluids containing
chlorinated paraff ins,
if they are processed,
through a tolling arrangement
as described
in
Section 739.124(c), to reclaim metalworking oils
or fluids.
The presumption does apply to
metalworking oils or fluids if
such oils or
fluids are recycled
in any other manner,
or
disposed.
ii)
The
rebuttable
presumption
does
not apply to
used
oils
contaminated
with
chlorofiuorocarbons
(CFC5) removed from refrigeration units where
the CFC8 are destined for reclamation.
The
rebuttable presumption does apply to used oils
contaminated with CFCs that have been mixed with
used oil from sources other than refrigeration
units.
2)
Characteristic hazardous waste.
A mixture of used oil and
hazardous waste that exhibits a hazardous waste
characteristic identified in 35 Ill. Adm. Code 721.Subpart C
and a mixture of used oil and hazardous waste that is
listed
in Subpart B of this Part solely because
it exhibits one or
more of the characteristics of hazardous waste identified
in
35
Ill. Adm. Code 721.Subpart C
is subject to:
A)
Except
as provided in subsection
(b)(2)(C)
of this
Section, regulation as hazardous waste under 35
Iii.
Adm. Code 703,
720 through 726, and 728 rather than as
used oil under this Part,
if the resultant mixture
exhibits any characteristics of hazardous waste
identified
in 35
Iii. Adm. Code 721.Subpart
C;
or
B)
Except as provided in subsection
(b)(2)(C)
of this
Section, regulation as used oil under this Part,
if
the resultant mixture does not exhibit any
characteristics of hazardous waste identified under
35
Ill.
Ad.rn.
Code 721.Subpart
C.
C)
Regulation as used oil under this Part,
if the mixture
is of used oil and a waste which
is hazardous solely
because it exhibits the characteristic of ignitabiiity
(e.g.,
ignitable—only mineral
spirits), provided that
the resultant mixture does not exhibit the
characteristic of
ignitabiiity under 35 Ill.
Adm.
Code
721. 121.
3)
Conditionally
exempt
small
quantity
generator
hazardous
409
waste.
A mixture of used oil and conditionally exempt small
quantity generator hazardous waste regulated under
35
Ill.
Adm. Code 721.105
is subject to regulation as used oil under
this Part.
c)
Materials containing or otherwise contaminated with used oil.
1)
Except
as provided in subsection
(c)(2)
of this Section,
a
material containing or otherwise contaminated with used oil
from which the used oil has been properly drained or removed
to the extent possible such that no visible signs of free—
flowing oil remain in or on the material:
A)
Is not used oil,
and thus,
it
is not subject to this
Part,
and
B)
If applicable,
is subject to the hazardous waste
regulations
of 35
Ill. Adm. Code 703,
705,
720 through
726, and 728.
2)
A material containing or otherwise contaminated with used
oil that
is burned for energy recovery
is subject to
regulation as used oil under this Part.
3)
Used oil drained or removed from materials containing or
otherwise contaminated with used oil
is subject to
regulation as used oil under this Part.
d)
Mixtures of used oil with products.
1)
Except as provided in subsection
(d)(2) below, mixtures of
used oil and fuels or other fuel products are subject to
regulation as used oil under this Part.
2)
Mixtures of used oil and diesel fuel mixed on—site by the
generator of the used oil
for use in the generator’s own
vehicles are not subject to this Part once the used oil and
diesel fuel have been mixed.
Prior to mixing, the used oil
is
subject to the requirements of Subpart C of this Part.
e)
Materials derived from used oil.
1)
Materials that are reclaimed from used oil that are used
beneficially and are not burned for energy recovery or used
in a manner constituting disposal
(e.g., re—refined
lubricants)
are:
A)
Not used oil and thus are not subject to this Part,
and
B)
Not solid wastes and are thus not subject to the
hazardous waste regulations
of Parts
35 Ill. Adm. Code
703, 720 through 726, and 728 as provided in 35
Ill.
Adm. Code 721.103(ee)(~1)-~-A-)-.
2)
Materials produced from used oil that are burned for energy
recovery
(e.g., used oil fuels)
are subject to regulation as
used oil under this Part.
3)
Except as provided in subsection
(e)(4)
below, materials
derived from used oil that are disposed of or used in a
manner constituting disposal are:
410
A)
Not used oil and thus are not
subject
to this Part,
and
B)
Are solid wastes and thus are subject to the hazardous
waste regulations
of 35
Ill.
Adm. Code 703,
720
through
726,
and 728
if the materials are listed or
identified as hazardous waste.
4)
Used oil re—refining distillation bottoms that are used as
feedetock to manufacture asphalt productB are not subject to
this Part.
f)
Wastewater.
Wastewater,
the discharge of which is subject to
regulation under either Section 402 or Section 307(b)
of the Clean
Water Act
(including wastewaters
at facilities which have
eliminated the discharge of wastewater), contaminated with de
minimis quantities of used oil are not subject to the requirements
of this Part.
For purposes of this subsection,
“de minimis”
quantities of used oils are defined as small spills,
leaks,
or
drippings from pumps, machinery, pipes,
and other similar
equipment during normal operations or small
amounts
of oil lost to
the wastewater treatment system during washing or draining
operations.
This exception will not apply
if the used oil is
discarded as a result of abnormal manufacturing operations
resulting in substantial
leaks,
spills, or other releases, or to
used oil recovered from wastewaters.
g)
Used oil introduced into crude oil pipelines or a petroleum
refining facility.
1)
Used oil mixed with crude oil or natural gas
liquids (e.g.,
in a production separator or crude oil stock tank)
for
insertion into a crude oil pipeline is exempt from the
requirements
of this Part.
The used oil
is subject to the
requirements
of this Part prior to the mixing of used oil
with crude oil or natural gas liquids.
2)
Mixtures of used oil and crude oil or natural gas liquids
containing less than
1
used oil that are being stored or
transported to
a crude oil pipeline or petroleum refining
facility for insertion into the refining process at
a point
prior to crude distillation or catalytic cracking are exempt
from the requirements of this Part.
3)
Used oil that
is inserted into the petroleum refining
process before crude distillation or catalytic cracking
without prior mixing with crude oil
is exempt from the
requirements of this Part,
provided that the used oil
contains less than
1
of the crude oil feed to any petroleum
refining facility process unit at any given time.
Prior to
insertion into the petroleum refining process,
the used oil
is
subject to the requirements of this Part.
4)
Except as provided
in subsection
(g)(5) below,
used oil that
is
introduced into a petroleum refining facility process
after crude distillation or catalytic cracking
is exempt
from the requirements of this Part only if the used oil
meets the specification of Section 739.111.
Prior to
insertion into the petroleum refining facility process, the
used oil
is subject to the requirements of this Part.
5)
Used oil that
is incidentally captured by
a hydrocarbon
411
recovery system or wastewater treatment system as part of
routine process operations
at
a petroleum refining facility
and inserted into the petroleum refining facility process is
exempt from the requirements of this Part.
This exemption
does not extend to used oil that
is
intentionally introduced
into a hydrocarbon recovery system
(e.g., by pouring
collected used oil into the wastewater treatment system).
6)
Tank bottoms from stock tanks containing exempt mixtures of
used oil and crude oil or natural gas liquids are exempt
from the requirements of this Part.
h)
Used oil on vessels.
Used oil produced on vessels from normal
shipboard operations
is not subject to this Part until it is
transported ashore.
i)
Used oil containing PCBs.
In addition to the requirements of this
Part,
a marketer or burner of used oil that markets used oil
containing any quantifiable level of PCBs
is
subject to the
requirements of 40 CFR 761.20(e).
(Source:
Amended at
19 Ill. Reg.
________,
effective
