ILLINOIS POLLUTION CONTROL BOARD
June 23,
1994
IN ThE MATTER OF:
)
R94—7
RCRA UPDATE, USEPA REGULATIONS
)
(Identical in Substance Rules)
(7—1—93 THROUGH 12—31—93)
)
Adopted Rule.
Final Order.
ORDER
OF THE BOARD
(by E.
Dunham):
Pursuant to Section 22.4(a)
of the Environmental Protection
Act
(Act), the Board adopts amendments to the RCRA hazardous
waste
(RCRA) regulations.
Section 22.4(a) provides for quick adoption of regulations
that are “identical in substance” to federal regulations adopted
by U.S. EPA to implement Sections 3001 through 3005 of the
Resource Conservation and Recovery Act of 1976
(RCRA,
42 U.S.C.
SS
6921—6925) and that Title VII of the Act and Section 5 of the
Administrative Procedure Act
(APA)
shall not apply.
Because this
rulemaking is not subject to Section 5 of the APA,
it is not
subject to first notice or to second notice review by the Joint
Committee on Administrative Rules
(JCAR).
The federal RCRA
Subtitle C regulations are found at 40 CFR 260 through 268, 270
through 271,
and, more recently,
279.
This order is supported by an opinion adopted on the same
day.
The Board will file
the adopted amendments 30 days after
the date of this order.
The complete text of the adopted rules
follows.
IT IS SO
ORDERED.
I, Dorothy H. Gunn, Clerk of the Illinois Pollution Control
Board, ~
certify that
t~
above order was adopted on the
______________
day of
~
,
1994, by a vote of
Dorothy H. 9~n, Clerk
Illinois Po~LutionControl Board
2
TITLE 35:
ENVIRONMENTAL
PROTECTION
SUBTITLE 0:
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
RCRA
Permits
Specific Inclusions in Permit Program
Specific Exclusions from Permit Program
Discharges of Hazardous Waste
Reapplications
Initial Applications
Federal Permits (Repealed)
SUBPART C:
AUTHORIZATION BY
RULE
AND INTERIM STATUS
Purpose and Scope
Permits by Rule
Application by Existing HWM Facilities and
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
ProcedureB for Closure Determination
SUBPART D:
APPLICATIONS
Applications in General
Contents of Part A
Contents of Part B
General Information
Facility Location Information
Groundwater Protection Information
Exposure Information
Solid Waste Management Units
Other Information
Specific Information
ContainerB
Tank Systems
Surface Impoundments
Waste Piles
Incinerators
Land Treatment
Landfills
Specific Part B Information Requirements for Boiler8 and
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
703.200
703.201
703.202
703.203
703.204
703.205
703.206
703.207
703. 208
Interim
Status
3
Industrial Furnaces
703.209
Miscellaneous Units
703.210
Process Vents
703.211
Equipment
703.212
Drip Pads
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
!ncinerator 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
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
CauseB 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
(Ill.
Rev.
Stat.
1991,
ch.
111½,
pars.
1022.4 and
1027
(415 ILCS 5/22.4 and 27).
SOURCE:
Adopted in R82—19,
53 PCB 131,
at
7
Ill. Reg.
14289, effective
October 12,
1983;
amended in R83—24 at 8
Ill. Reg.
206, effective December 27,
1983;
amended in R84—9 at 9 Ill.
Reg.
11899, effective July 24,
1985;
amended
in R85—22 at 10 Ill. Reg.
1110,
effective January 2,
1987; amended in R85—23
at
10 Ill.
Reg. 13284,
effective July 28, 1986; amended in R86—l at 10
Ill.
Reg.
14093, effective
August
12,
1986;
amended in R86—19 at 10 Ill. Reg.
20702,
effective December
2,
1986;
amended in R86—28
at 11 Ill. Reg.
6121,
effective March 24, 1987;
amended
in
R86—46
at 11 Ill.
Reg.
13543,
effective
August
4,
1987;
amended in R87—5 at 11 Ill. Reg. 19383,
effective November 12,
1987; amended in R87—26 at
12
Ill.
Reg. 2584, effective January 15, 1988;
amended in R87—39 at 12
Ill. Reg.
13069, effective July 29,
1988; amended in
R88—16 at
13 Ill.
Reg.
447, effective December 27,
1988;
amended
in R89—1 at
13 Ill.
Reg. 18477, effective November 13,
1989;
amended in R89—9 at
14
Ill.
Reg.
6278,
effective April
16,
1990; amended
in R90—2
at 14
Ill. Reg.
14492,
effective
August
22,
1990; amended in R90—11 at
15 Ill.
Reg.
9616,
effective
4
June
17,
1991;
amended in R91—1 at
15 Ill. Rag.
14554, effective september 30,
1991;
amended in R91—13 at 16
Ill. Rag.
9767, effective June
9, 1992; amended
in R92—10 at
17
Ill. Rag.
5774, affective March 26, 1993; amended
in R93—4 at
17 Ill.
Rag.
20794, effective November 22,
1993; amended in R93—16 at
18 Ill.
Rag.
6898,
effective April 26,
1994;
amended
in R94—7 at
Ill..
Rep.
effective
SUBPART A:
GENERAL
PROVISIONS
Section 703.110
References
a)
When used in this Part the following publications are incorporated
by reference:
NToot flothode- for Evaluating Solid Waste,
rhyeieal/Chemi..al~
flethode,”
EPA
Publication EW 846
(C-ooond Edition,
1982 as
amended b- Update
I
(April, 1~4) and Update II
(April,
19U)).
The sosond edition of £W-846 end Updates
I and
-~
are available from the Luporintondent of Dosumonta,
U.S.
Covornment
I’rinting Offlee,
Washing-ben, D.C.,
30401
(202-)-
783 3238,
on
a nubsoriptien basis. (See 35
Ill. Adm. Code
720.111.)
b)
The references listed in p-aragraphsubsection
(a) above are also
available for inspection at the offices of the Pollution Control
Board.
This incorporation includes no later amendments or
editions.
(BOARD NOTE:
Derived from 40 CFR 270.6
(1992),
as amended at
58
Fed.
Rep. 46051
(Aup. 31,
3.993~.
(Source:
Amended at
18
Ill.
Reg.
________,
effective
_____________________
SUBPART D:
APPLICATIONS
Section 703.205
Incinerators
For facilities that incinerate hazardous waste,
except
as
35 Ill. Adm. Code
724.440 provides otherwise, the applicant must fulfill the requirements of
paragraphsubsections
(a),
(b)
or
(C)
below in completing the Part
B
application:
a)
When seeking exemption under 35
Ill. Adm. Code 724.440(b) or
Cc)
(ignitable, corrosive or reactive wastes only):
1)
Documentation that the waste is listed as
a hazardous waste
in 35
Ill.
Adm. Code 721-7—~SubpartB solely because it is
ignitable (Hazard Code I),
corro8ive (Hazard Code C), or
both; or
2)
Documentation that the waste is listed as
a hazardous waste
in 35
Ill. Adm. Code
721.,—.~.SubpartD solely because it is
reactive (Hazard Code
R)
for characteristics other than
those listed in 35 Ill. Adm. Code 721.123(a) (4) and
jaj(5),
and will not be burned when other hazardous wastes are
present in the combustion zone;
or
3)
Documentation that the waste
is
a hazardous waste solely
because it possesses the characteristic of ignitability or
corrosivity,
or both,
as determined by the tests for
5
characteristics of hazardous wastes under 35 Ill. Adm. Code
72l,—~SubpartC;
or
4)
Documentation that the waste is
a hazardous waste solely
because it possesses the reactivity characteristics listed
in 35
Ill. Adm. Code 721.123
(&)(l)T (2),throuch jjI(3)r...2~
.LJJ.~(6)T
(7)
orthrouah
j~j(8),and that it will not be burned
when other hazardous wastes are present in the combustion
zone; or
b)
Submit a trial burn plan or the results of
a trial burn,
including
all required determinations,
in accordance with Section 703.222 et
seq.; or
c)
In lieu of a trial burn,
the applicant may
submit the following
information:
1)
An analysis of each waste or mixture of wastes to be burned
including:
A)
Heat value
of the waste in the form and composition in
which
it will be burned;
B)
Viscosity (if applicable), or description of physical
form of the waste;
C)
An identification of any hazardous organic
constituents listed
in 35
Ill. Adm. Code 721,-
~Appendix H~uhichthat are present in the waste to be
burned,
except that the applicant need not analyze for
constituents listed
in 35
Ill. Adm. Code
721,-
~Appendix H uhiohthat would reasonably not be expected
to be found
in the waste.
The constituents excluded
from analysis must be identified and the basis
for
their exclusion stated.
The waste analysis must rely
on analytical techniques specified
in “Test Methods
for the Evaluation of Solid Waste,
Physical/Chemical
Methods”, U.S.
EPA Publication SW—846,
as
+incorporated by reference,
oco at
35
Ill.
Adin.
Code
720.111 and Section 703.110
and
ref
oronood in 3~Ill~-
I~dm.Code 721, Z~ppondbt0),
or their equivalent;
B)
An approximate quantification of the hazardous
constituents identified
in the waste, within the
precision produced by the analytical methods specified
in “Test Methods for the Evaluation of Solid Waste,
Physical/Chemical Methods”1
U.S. EPA Publication SW—
846,
as .4-incorporated by reference, coo at 35
Ill.
Adm. Code 720.111 and Section 7O3.l10-~-;
E)
A quantification of those hazardous constituents
in
the waste whiohthat may be designated as POHC5 based
on data submitted from other trial or operational
burns ~Thichthatdemonstrate compliance with the
performance standard in 35 Ill.
Adrn.
Code 724.443;
2)
A detailed engineering description of the incinerator,
including:
A)
Manufacturer’s name and model number of incinerator;
B)
Type of incinerator;
6
C)
Linear dimension of incinerator unit including cross
sectional area of combustion chamber;
B)
Description of auxiliary fuel system (type/feed);
E)
Capacity of prime mover;
F)
Description of automatic waste feed cutoff system(s);
G)
Stack gas monitoring and pollution control monitoring
system;
H)
Nozzle and burner design;
I)
Construction materials;
J)
Location
and
description of temperature, pressure and
flow indicating devices and control devices;
3)
A description and analysis of the waste to be burned
compared with the waste for which data from operational or
trial burns are provided to support the contention that a
trial burn is not needed.
The data should include those
items listed in pee ~*ap1~subsection (c)(1) above.
This
analysis should specify the POHCs uhiohthat the applicant
has identified in the waste for which
a permit is sought,
and any differences from the POHC5 in the waste for which
burn data are provided;
4)
The design and operating conditions of the incinerator unit
to be used,
compared with that for which comparative burn
data are available;
5)
A description of the results submitted from any previously
conducted trial burn(s)
including:
A)
Sampling and analysis techniques used to calculate
performance standards
in
35
Ill. Adm.
Code 724.443;
B)
Methods and results of monitoring temperatures, waste
feed rates,
carbon monoxide and an appropriate
indicator of combustion gas velocity (including a
statement concerning the precision and accuracy of
this measurement);
C)
The certification and results required by
paragrapheubeection
(b) above
6)
The
expected
incinerator
operation
information
to
demonstrate
compliance
with
35
Ill.
Adm.
Code
724.443
and
724.445
including:
A)
Expected
carbon monoxide (CO)
level in the stack
exhaust
gas;
B)
Waste
feed
rate;
C)
Combustion
zone
temperature;
B)
Indication
of
combustion
gas
velocity;
E)
Expected
stack
gas
volume,
flow
rate
and
temperature;
7
F)
Computed
residence
time
for
waste
in
the
combustion
zone;
G)
Expected hydrochloric acid removal efficiency;
H)
Expected fugitive emissions and their control
procedures;
I)
Proposed waste feed cut—off limits based on the
identified significant operating parameters;
7)
The Agency may, pursuant to
35
Ill. Adm. Code 705.122,
request such additional information as may be necessary for
the Agency to determine whether the incinerator meets the
requirements of 35
Ill. Adm. Code 724,—~.Subpart0,
and what
conditions are required by that Subpart and Section 39(d)
of
the Environmental Protection Act;
8)
Waste analysis data, including that submitted in
paragraphsubsection (c)(1)
above,
sufficient to allow the
Agency to specify
as permit Principal Organic Hazardous
Constituents
(permit POHC5) those constituents for which
destruction and removal efficiencies will be required;
d)
The Agency shall approve a permit application without a trial burn
if
it
finds
that:
1)
The
wastes
are
sufficiently
similar;
and
2)
The incinerator units are sufficiently similar,
and the data
from other trial burns are adequate to specify
(under 35
Ill. Adm. Code 724.445) operating conditions that will
ensure that the performance standards in
35 Ill.
Adrn. Code
724.443 will be met by the incinerator.
(BOARD NOTE:
Derived
from
40
CFR
270.19
(1992),
as
amended
at
58
Fed.
Req.
46051
(Aug.
31,
1993).
See
40
CFR
122.25(b)
(5).)
(Source:
Amended
at
18
Ill.
Reg.
_______,
effective
____________________)
SUBPART
E:
SHORT
TERM
AND
PHASED
PERMITS
Section
703.223
Incinerator
Conditions
Buring
Trial
Burn
For the purposes of determining feasibility of compliance with
the performance standards of 3~Ill.
Adm. Code 724.443 and of
determining adequate operating conditions under
35
Ill. Adm. Code
724.445, the Agency shall establish conditions in the permit to a
new hazardous waste incinerator to be effective during the trial
burn.
a)
Applicants shall propose a trial burn plan,
prepared under
subsection
(b) below with Part B of the permit application;
b)
The trial burn plan must include the following information:
1)
An analysis of each waste or mixture of wastes to be burned
whiohthat includes:
A)
Heat value of the waste in the form and composition
in
8
which
it
will
be
burned;
B)
Viscosity
(if
applicable),
or
description of physical
form
of
the
waste;
C)
An
identification
of
any hazardous organic
constituents
listed
in
35
Ill.
Adm.
Code
721.Appendix
H,
uhiehthat
are
present
in
the
waste
to
be
burned,
except
that
the
applicant need not analyze for
constituents
listed
in
35
11.1.
Mm.
Code
721.Appendix
H
i.thiehthat
would
reasonably
not
be
expected
to
be
found
in
the
waste.
The
constituents excluded from
analysis must be identified, and the basis for their
exclusion
stated.
The
waste
analysis
must
rely
on
analytical techniques specified in “Test Methods for
the Evaluation of Solid Waste, Physical/Chemical
Methods”. U.S. EPA Publication SW—846. as
-4-incorporated by reference,
occ at 35
Ill. Mm.
Code
720.111 and Section 703.110.)-, or their equivalent;
D)
An approximate quantification of the hazardous
constituents identified in the waste, within the
precision
produced
by
the
analytical
methods
specified
in
“Test
Methods
for
the
Evaluation
of
Solid
Waste,
Physical/Chemical
Methods,-”.
U.S.
EPA
Publication
SW-
846,
as
+incorporated
by
reference,
soc
at
35
Ill.
Adm.
Code
720.111
and
Section
7O3.l10-)-~.or
their
equivalent;
2)
A detailed engineering description of the incinerator for
which the
permit
is
sought including:
A)
Manufacturer’s name and model number of
incinerator
(if
available);
B)
Type
of
incinerator;
C)
Linear dimensions of the incinerator unit including
the cross sectional area of combustion chamber;
D)
Description of the auxiliary fuel system
(type/feed);
E)
Capacity of prime mover;
F)
Description of automatic waste feed cut-off
system(s);
G)
Stack gas monitoring and pollution control equipment;
H)
Nozzle and burner design;
I)
Construction materials;
J)
Location and description of temperature, pressure and
flow indicating
and
control devices;
3)
A detailed description of sampling and monitoring
procedures,
including sampling and monitoring locations in
the
system,
the
equipment
to
be
used,
sampling
and
monitoring
frequency
and
planned analytical procedures for
sample
analysis;
4)
A
detailed
test
schedule
for
each
waste
for
which
the
trial
9
burn
is
planned
including
date(s),
duration,
quantity
of
waste
to
be
burned
and
other factors relevant to the
Agency’s decision under subsection
(e) below
5)
A detailed test protocol,
including,
for each waste
identified,
the
ranges
of
temperature,
waste
feed
rate,
combustion
gas
velocity,
use
of
auxiliary
fuel
and
any
other
relevant
parameters
that will be varied to affect the
destruction and removal efficiency of the incinerator;
6)
A description of, and planned operating conditions
for,
any
emission control equipment uhiohthat will be used;
7)
Procedures for rapidly stopping waste feed, shutting down
the
incinerator
and
controlling
emissions
in
the
event
of
an
equipment
malfunction;
8)
Such
other
information
as
the
Agency
reasonably
finds
necessary
to
determine whether to approve the trial burn
plan
in
light
of
the
purposes
of
this
paragrapheubeection
and
the criteria in subsection
(a) below.
Such information
muat be requested by the Agency
pursuant to 35 Ill.
Adm.
Code 705.123.
c~
The Agency,
in reviewing the trial burn plan,
shall evaluate the
sufficiency of the information provided and shall require the
applicant, pursuant to 35
Ill.
Adm. Code 705.123, to supplement
this information,
if necessary, to achieve the purposes of this
paragraphsubsection
d)
Based on the waste analysis data in the trial burn plan,
the
Agency shall specify
as trial Principal Organic Hazardous
Constituents (POHC5), those constituents for which destruction and
removal efficiencies must be calculated during the trial burn.
These trial POHCs must be specified by the Agency based on its
estimate of the difficulty of incineration of the constituents
identified in the waste analysis,
their concentration or mass in
the waste feed, and,
for wastes listed in 35 Ill. Adm. Code
72l.Subpart
D,
the hazardous waste organic constituent of
constituents identified in
35 Ill. Adm. Code 721.Appendix
G or H
as the basi8 for listing;
The Agency shall approve a trial burn plan if
it finds that:
1)
The trial burn is likely to determine whether the
incinerator performance standard required by 35 Ill. Adm.
Code 724.443 can be met;
2)
The trial burn itself will not present
an imminent hazard to
human
health
or
the
environment;
3)
The
trial
burn
will
help
the
Agency
to
determine
operating
requirements
to
be
specified
under 35
Ill. Adm.
Code
724.445;
and
4)
The
information
sought
in
subsection~
(e)(l)
and
(e)(3)
above
cannot
reasonably
be
developed
through
other
means;
f)
During
each
approved
trial
burn
(or
as
soon
after
the
burn
as
is
practicable),
the
applicant
shall
make
the
following
determinations:
10
1)
A quantitative analysis of the trial POHCs,
in the waste
feed
to
the
incinerator;
2)
A quantitative analysis of the exhaust gas for the
concentration
and mass emissions of the trial POHC’s,
molecular
oxygen
and
hydrogen
chloride
(HC1);
3)
A
quantitative
analysis
of
the
scrubber
water
(if
any),
ash
residues
and
other
residues,
for
the
purpose of estimating
the
fate
of
the
trial POHCs;
4)
A computation of destruction and removal efficiency (DRE),
in
accordance
with
the
DRE
formula
specified
in
35
Ill.
Adm.
Code
724.443(a);
5)
If
the
HC1
(hydrogen
chloride)
emission
rate exceeds 1.8
kilograms
of
Nd
per
hour
(4
pounds
per
hour),
a
computation
of
HC1
removal efficiency in accordance with
35
Ill.
Adni.
Code
724.443(b);
6)
A
computation
of
particulate
emissions,
in
accordance
with
35
Ill.
Adm.
Code
724.443(c);
7)
An
identification
of
sources
of
fugitive
emissions
and
their
means
of
control;
8)
A
measurement
of
average, maximum and minimum temperatures
and
combustion
gas
velocity;
9)
A
continuous
measurement
of
carbon
monoxide
(CO)
in
the
exhaust
gas;
10)
Such
other
information
as
the
Agency
specifies
as
necessary
to
ensure
that
the
trial
burn
will
determine
compliance
with
the
performance
standards
in
35
Ill.
Adm.
Code
724.443
and
to
establish
the
operating
conditions
required
by
35
Ill.
Adm.
Code
724.445
as
necessary
to
meet
that
performance
standard.
g)
The
applicant
shall
submit
to
the
Agency
a
certification
that
the
trial
burn
has
been
carried
out
in
accordance
with
the
approved
trial
burn
plan,
and
shall
submit
the
results
of
all
the
determinations
required
in
subsection
(f)
above.
This
submission
must
be
made
within
90
days
of
completion
of
the
trial
burn,
or
later if approved by the Agency;
h)
All data collected during any trial burn must be submitted to the
Agency
following
the
completion
of
the
trial
burn;
i)
All
submissions
required
by
this per.~eep~subsection
must be
certified
on
behalf
of
the
applicant
by
the
signature
of
a
person
authorized
to
sign a
permit
application
or
a
report
under
35
Ill.
Adm. Code 702.126;
j)
Based on the results of the trial burn, the Agency shall
set the
operating requirements
in the final permit according to 35
Ill.
Adm. Code 724.445.
The permit modification must proceed as a
minor modification according to
Section 703.280.
BOARD NOTE:
Derived from 40 CFR 270.62(a)
(19882.a),
as amended at
5~ Fed.
Reg.
37934,
Ccptembcr
23.,
198846051
(AuQ.
31.
1993k.
11
(Source:
Amended
at
18
Ill.
Reg.
________,
effective
_____________________
Section
703.232
Permits for Boilers and Industrial Furnaces Burning
Hazardous
Waste
a)
General.
Owners
and operators of new boilers and industrial
furnaces (those not operating under the interim status standards
of
35
Ill.
Adm.
Code 726.203)
are subject to subsection
(b)
through
(f),- below.
Boilers and industrial furnaces operating
under the interim status standards of 35 Ill.
Adm.
Code 726.203
are subject to subsection
(g),- below.
b)
Permit operating periods for new boilers and industrial furnaces.
A
permit
for
a
new
boiler
or
industrial furnace must specify
appropriate conditions for the following operating periods:
1)
Pretrial burn period.
For the period beginning with initial
introduction of hazardous waste and ending with initiation
of
the
trial
burn,
and
only
for
the
minimum
time
required
to
bring
the
boiler
or
industrial
furnace
to
a
point
of
operation
readiness
to
conduct
a
trial
burn,
not
to
exceed
720
hours
operating
time
when
burning
hazardous waste,
the
Agency
shall
establish
in
the
Pretrial
Burn
Period
of
the
permit
conditions,
including
but
not
limited
to
allowable
hazardous
waste
feed
rates
and
operating
conditions.
The
Agency shall extend the duration of this operational period
once,
for up to
720
additional
hours,
at
the
request
of
the
applicant
when
good cause is shown.
The permit
most
be
modified
to
reflect
the
extension according to Section
703.280
et
seq.
A)
Applicants
must
submit
a statement, with part B of the
permit
application,
that
suggests the conditions
necessary
to
operate in compliance with the standards
of
35
Ill.
Adm.
Code
726.204
through
726.207
during
this period.
This statement should include,
at a
minimum, restrictions on the applicable operating
requirements
identified
in
35
Ill.
Adm.
Code
726.202
(e).
B)
The
Agency
shall
review
this
statement
and
any
other
relevant
information
submitted
with
part
B
of
the
permit
application
and
specify
requirements
for
this
period
sufficient
to
meet
the
performance
standards
of
35
Ill.
Adm.
Code
726.204
through
726.207
based
on
the
Agency’s engineering judgment.
2)
Trial
burn
period.
For
the
duration
of
the
trial
burn,
the
Agency shall establish conditions in the permit for the
purposes of determining feasibility of compliance with the
performance standards of 35 Ill.
Adrn.
Code
726.204
through
726.207
and
determining
adequate
operating
conditions
under
35
Ill. Adm. Code 726.202(e).
Applicants shall propose a
trial burn plan, prepared under subsection
(C)-~
below, to be
submitted
with
part
B
of
the
permit
application.
3)
Post-trial burn period.
A)
For the period
immediately following completion of the
trial burn, and only for the minimum period sufficient
to allow sample analysis, data computation and
submission of the trial burn results by the applicant,
12
and review of the trial burn results and modification
of the facility permit by the Agency to reflect the
trial burn results, the Agency shall establish the
operating requirements most
likely to ensure
compliance with the performance standards of
35 Ill.
Mm. Code 726.204 through 726.207 based on the
Agency’s engineering judgment.
B)
Applicants shall submit
a
statement, with part B of
the application, that identifies the conditions
necessary to operate during this period in compliance
with the performance standards of 35
Ill.
Adni. Code
726.204 through 726.207.
This statement should
include,
at
a minimum, restrictions on the operating
requirements provided by 35 Ill.
Mm.
Code 726.202
(a).
C)
The Agency shall review this statement and any other
relevant information submitted with part B of the
permit application and specify requirements of this
period sufficient to meet the performance standards of
35 Ill.
Adni. Code 726.204 through
726.207 based on the
Agency’s engineering judgment.
4)
Final
permit
period.
For the final period of operation the
Agency shall develop operating requirements in conformance
with 35
Ill. Adm. Code 726.202—(e) that reflect conditions
in the trial burn plan and are likely to ensure compliance
with the performance standards of 35
Ill. Adm.
Code 726.204
through 726.207.
Based on the trial burn results, the
Agency
shall
make
any
necessary
modifications
to
the
operating requirements to ensure compliance with the
performance
standards.
The
permit
modification
must
proceed
according
to
Section
703.280
et
seq.
c)
Requirements
for
trial
burn
plans.
The
trial burn plan must
include
the
following
information.
The
Agency,
in reviewing the
trial
burn
plan,
shall
evaluate the sufficiency of the information
provided
and
may
require
the
applicant
to
supplement
this
information,
if
necessary,
to
achieve the purposes of this
subsection.
1)
An
analysis
of
each
feed
stream,
including
hazardous
waste,
other
fuels,
and
industrial
furnace
feed
stocks,
as
fired,
that
includes:
A)
Heating
value,
levels
of antimony, arsenic,
barium,
beryllium,
cadmium,
chromium,
lead,
mercury,
silver,
thallium,
total
chlorine/chloride
and
ash;
B)
Viscosity
or
description
of
the
physical
form
of
the
feed
stream;
2)
An
analysis
of
each
hazardous
waste,
as
fired,
including:
A)
An
identification
of
any
hazardous
organic
constituents
listed
in
35
Ill.
Adm.
Code
721.Appendix
H
that
are
present
in
the
feed
stream,
except
that
the
applicant
need
not
analyze for constituents listed in
App..endj~
H whiohthat would reasonably not be expected
to
be
found
in
the
hazardous
waste.
The
constituents
excluded
from
analysis
must be identified as the basis
13
for this exclusion explained.
The analysis must be
conducted in accordance with analytical techniques
specified in :Test Methods for the Evaluation of Solid
Waste,
Physical/Chemical Methods”,
U.S. EPA
Publication SW-846,
as fincorporated by reference7
.00
~.35
Ill. Mm.
Code 720.111 and Section 703.110,
or
their equivalent.)-
B)
An approximate quantification of the hazardous
constituents identified in the hazardous waste, within
the precision produced by the analytical methods
specified in :Test Methods for the Evaluation of Solid
Waste,
Physical/Chemical Methods”.
U.S. EPA
Publication SW-846,
as incoreorated by reference at
35
Ill.
Adrn.
Code 720.111 and Section 703.110. or other
equivalent.
C)
A description
of blending procedures,
if applicable,
prior to firing the hazardous waste,
including a
detailed analysis of the hazardous waste prior to
blending,
an analysis of the material with which the
hazardous waste prior to blending,
an analysis of the
material with which the hazardous waste is blended,
and blending ratios.
3)
A detailed engineering description of the boiler or
industrial furnace,
including:
A)
Manufacturer’s name and model number of the boiler or
industrial furnace;
B)
Type of boiler or industrial furnace;
C)
Maximum
design
capacity
in
appropriate
units;
B)
Description
of
the Feed system for the hazardous
waste,
and
as
appropriate,
other
fuels
and
industrial
furnace
feedstocks;
E)
Capacity
of
hazardous
waste
feed
Bystem;
F)
Description of automatic hazardous waste feed cutoff
system(s); and
G)
Description of any pollution control system;
and
H)
Description of stack gas monitoring and any pollution
control monitoring systems.
4)
A detailed description of sampling and monitoring procedures
including sampling and monitoring locations in the system,
the equipment to be used,
sampling and monitoring frequency
and sample analysis.
5)
A detailed teat schedule for each hazardous waste for which
the trial burn is planned, including date(s), duration,
quantity of hazardous waste to be burned,
and other factors
relevant to the Agency’s decision under subsection
(b)(2),-
above.
6)
A detailed test protocol,
including,
for each hazardous
waste identified, the ranges of hazardous waste feed rate,
14
and,
as
appropriate, the feed rates of other fuels and
industrial furnace feedstocks,
and any other relevant
parameters that may affect the ability of the boiler or
industrial furnace to meet the performance standards in 35
Ill.
Adin.
Code 726.204 through 726.207.
7)
A description of and planned operating conditions for any
emission control equipment that will be used.
B)
Procedures for rapidly stopping ;the hazardous waste feed
and controlling emissions in the event of an equipment
malfunction.
9)
Such other information as the Agency finds necessary to
determine whether to approve the trial burn plan in light of
the purposes of this subsection and the criteria in
subsection
(b)(2)-,- above.
d)
Trial burn procedures.
1)
A trial burn must be conducted to demonstrate conformance
with the standards of 35 Ill. Adm. Code 726.104 through
726.107.
2)
The Agency shall approve a trial burn plan if the Agency
finds that:
A)
The trial burn is likely to determine whether the
boiler or industrial furnace can meet the performance
standards of 35 Ill. Adm. Code 726.104 through
726. 107.
B)
The trial burn itself will not present an imminent
hazard to human health and the environment;
C)
The trial burn will help the Agency to determine
operating requirements to be specified under 35
Ill.
Adm. Code 726.102—(e);
and
B)
The information sought
in the trial burn cannot
reasonably be developed through other means.
3)
The applicant shall submit to the Agency a certification
that the trial burn has been carried out
in accordance with
the approved trial burn plan,
and submit the results of all
the determinations required in subsection
(c)-,- above.
The
Agency shall,
in the trial burn plan, require that the
submission be made within 90 days after completion of the
trial burn,
or later if the Agency determines that a later
date is acceptable.
4)
All data collected during any trial burn must be submitted
to the Agency following completion of the trial burn.
5)
All submissions required by this subsection must be
certified on behalf of the applicant by the signature of
a
person authorized to sign a permit application or
a report
under 35
Ill. Adm. Code 702.126.
e)
Special procedures for DRE trial burns.
When
a DRE trial burn is
required under 35 Ill. Adm. Code 726.104, the Agency shall specify
(based on the hazardous waste analysis data and other information
15
in the trial burn plan)
as trial Principal Organic Hazardous
Constituents
(POliCe)
those compounds for which destruction and
removal efficiencies must be calculated during the trial burn.
These trial POHCs will be specified by the Agency based on
information including the Agency’s estimate of the difficulty of
destroying the constituents identified in the hazardous waste
analysis, their concentrations or mass in the hazardous waste
feed,
and,
for hazardous waste containing or derived from wastes
listed in 35
Ill.
Adm. Code 721.Subpart B,
the hazardous waste
organic constituent(s) identified in 35 Ill. Adm. Code
721.Appendix G
as
the basis for listing.
f)
Determinations based on trial burn.
During each approved trial
burn
(or as soon after the burn as is practicable), the applicant
shall make the following determinations:
1)
A quantitative analysis of the levels of antimony,
arsenic,
barium, beryllium,
cadmium, chromium,
lead,
mercury,
thallium,
silver,
and chlorine/chloride,
in the feed streams
(hazardous waste,
other fuels,
and industrial
furnace
feedstocks);
2)
When a DRE trial burn is required under 35 Ill. Mm.
Code
726.204—(a):
A)
A quantitative analysis of the trial PONds
in the
hazardous waste feed;
B)
A quantitative analysis of the stack gas for the
concentration and mass emissions of the trial POHCs;
and
C)
A computation of
(DRE),
in accordance with the DRE
formula specified in 35 Ill.
Adni.
Code 726.204—(a).
3)
When a trial burn for chlorinated dioxins and furans
is
required under
35
Ill.
Adm. Coda
726.204—(e),
a quantitative
analysis of the stack gas for the concentration and mass
emission rate of the 2-,-~3,—7,—8—chlorinatedtetra—octa
congeners of chlorinated dibenzo—p—dioxins and furans, and a
computation showing conformance with the emission standard.
4)
When a trial burn for PM,
metals, or HC1/Chlorine gas is
required under 35
Ill. Adm. Code 726.205,
726.206—(c) or
(d)
or 726.207—(b)—(2)
or
(c),
a quantitative analysis of the
stack gas
for the concentrations and mass emissions of PM,
metals,
or HC.
and chlorine gas and computations showing
conformance with the applicable emission performance
standards;
5)
When a trial burn for DRE, metals, and Rd/Chlorine gas is
required under 35
Ill.
Adm. Code 726.204—(a),
726.206—(c)
or
(d), or 726.207—(b)—(2)
or
(c),
a quantitative analysis of
the scrubber water (if any),
ash residues,
other residues,
and products for the purpose of estimating the fate of the
trial POliCe, metals, and chlorine/chloride;
6)
An identification of sources of fugitive emissions and their
means of control;
7)
A continuous measurement of carbon monoxide
(do),
oxygen,
and where required,
hydrocarbons
(lid),
in the stack gas; and
16
8)
Such other information
as the Agency specifies
as
necessary
to ensure that the trial burn will determine compliance with
the performance standards
35 Ill. Adm. Code 726.204 through
726.207 and to establish the operating conditions required
by 35
Ill. Adm.
Code 726.204 through 726.207 and of
determining adequate operating conditions under 35 Ill. Adm.
Code 726.203, and to establish the operating conditions
required by 35 Ill. Adm. Code 726.202(e)
as necessary to
meet those performance standards.
g).
Interim status boilers and industrial furnaces,
for the purpose
of determining feasibility
of compliance with the performance
standards of
35 Ill. Adm. Code 726.204 through 726.207 and of
determining adequate operating conditions under 35 Ill. Adni. Code
726.203, applicants owning or operating existing boilers or
industrial
furnaces operated under the interim statue standards of
35
Ill. Mm.
Code 726.203 shall either prepare and submit a trial
burn plan and perform a trial burn
in accordance with the
requirements of the Section or submit other information as
specified in Section 703.208(a)(6).
Applicants w~ethatsubmit
a
trial burn plan and receive approval before submission of the part
B permit application shall complete the trial burn and submit the
results specified in subsection
(f).,-
above-,- with the part B permit
application.
If completion of this process conflicts with the
date set for submission of the part B application, the applicant
shall contact the Agency to establish
a later date for submission
of the part B application or the trial burn results.
If the
applicant submits
a trial burn plan with part B of the permit
application, the trial burn must be conducted and the results
submitted within a time period prior to permit issuance to be
specified by the Agency.
BOARD NOTE:
Derived
from 40 CFR 270.66
(1992).
as amended at
58
Fed. Req.
46051
(Aug.
31,
1993).
(Source:
Amended at 18
Ill. Reg.
_________,
effective
________________
TITLE 35:
ENVIRONMENTAL PROTECTION
SUBTITLE G:
WASTE DISPOSAL
CHAPTER
I:
POLLUTION CONTROL BOARD
SUBCHAPTER
C:
HAZARDOUS WASTE OPERATING REQUIREMENTS
PART 720
HAZARDOUS WASTE MANAGEMENT SYSTEM:
GENERAL
SUBPART A:
GENERAL PROVISIONS
Section
720.101
Purpose, Scope and Applicability
720.102
Availability of Information; Confidentiality of Information
720.103
Use
of
Number
and
Gender
SUBPART
B:
DEFINITIONS
Section
720. 110
Definitions
720.111
References
SUBPART C:
RULEMAKING PETITIONS AND OTHER PROCEDURES
Section
720. 120
Rulemaking
720.121
Alternative Equivalent Testing Methods
720.122
Waste Delisting
17
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 ease—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
(Ill. Rev. Stat.
1991,
eh. 111½,
pars.
1022.4 and
1027
(415 ILCS 5/22.4 and 27)).
SOURCE:
Adopted in R81-22,
43 PCB 427, at 5
Ill. Reg.
9781, effective as
noted in 35 Ill. Adm.
Code 700.106;
amended and codified in R82.-22,
45 PCB
317, at
6 Ill. Req.
4828,
effective as noted in
35 Ill. Adm. Code 700.106;
amended in R82—l9 at
7
Ill. Req.
14015, effective October 12,
1983;
amended in
R84—9,
53
PCB 131 at 9 Ill. Req.
11819, effective July 24,
1985;
amended in
R85—22 at 10
Il..
Reg. 968, effective January 2,
1986; amended in R86—1 at
10
Ill. Req.
13998, effective August
12,
1986;
amended in R86—19 at 10 Ill. Reg.
20630, effective December
2,
1986;
amended in R86—28 at
12. Ill. Reg.
6017,
effective March 24,
1987; amended in R86—46 at
11
Ill.
Reg.
13435, effective
August
4,
1987; amended in R87—5 at
12.
Ill.
Req.
19280, effective November
12,
1987;
amended in R87—26 at 12
Ill. Reg.
2450, effective January 15,
1988;
amended in R87—39 at 12
Ill. Reg.
12999, effective July 29,
1988;
amended in
R88—16 at
13
Ill.
Reg.
362, effective December 27,
1988; amended in R89—1 at
13
Ill. Reg.
18278, effective November 13,
1989;
amended in R89—2 at
14 Ill.
Req.
3075,
effective February 20,
1990;
amended in R89—9 at 14 Ill.
Req. 6225,
effective April
16,
1990;
amended in R90—10 at
14
Ill.
Reg.
16450, effective
September 25,
1990;
amended in R90—17 at 15
Ill. Reg.
7934,
effective May
9,
1991;
amended in R90-11 at 15
Ill. Req.
9323, effective June 17,
1991; amended
in R91—1 at 15
Ill.
Req.
14446, effective September 30,
1991; amended in R9l—
13 at 16 Ill. Reg. 9489,
effective June
9,
1992;
amended in R92—2. at 16 Ill.
Req.
17636, effective November 6,
1992;
amended in R92—10 at
17
Ill. Req.
5625, effective March 26,
1993; amended in R93—4 at 17
Ill. Req.
20545,
effective November 22, 1993;
amended in R93—16 at
18
Ill.
Req.
6720, effective
April 26,
1994;
amended in R94—7 at
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 B31.3 and B31.4.
See ASME/ANSI B31.3 and B31.4
ACI.
Available from the American Concrete Institute,
Box
19150,
Redford
Station,
Detroit,
Michigan
48219:
ACI
318-83:
“Building Code Requirements for
Reinforced
Concrete”,
adopted
September,
1983.
API.
Available
from
the American Petroleum
Institute,
1220
L
Street,
N.W.,
Washington,
D.C.
20005,
(202)
682—8000:
18
“Guide for Inspection of Refinery Equipment, Chapter
XIII,
Atmospheric and Low Pressure Storage Tanks,” 4th
Edition,
1981,
reaffirmed December,
1987.
“Cathodic Protection of Underground Petroleum Storage
Tanks and Piping Systems,” API Recommended Practice
1632,
Second Edition, December,
1987.
“Installation of Underground Petroleum Storage
Systems,” API Recommended Practice 1615, Fourth
Edition,
November,
1987.
APTI.
Available from the Air and Waste Management
Association, Box 2861,
Pittsburgh,
PA
15230,
(412)
232—
3444:
A.PTI Course 415:
Control of Gaseous Emissions, U.S~
EPA Publication EPA-450/2—Bl—005,
December,
1981.
ASME.
Available from the American Society of Mechanical
Engineers,
345 East 47th Street,
New York,
NY
10017,
(212)
705—7722:
“Chemical Plant and Petroleum Refinery Piping”,
ASME/
ANSI B31.3—1987,
as supplemented by B3l.3a—l988 and
B31.3b—1988.
Also available from ANSI.
“Liquid Transportation Systems for Hydrocarbons,
Liquid Petroleum Gas, Anhydrous Ammonia, and
Alcohols”,
ASME/ANSI B31.4—1986,
as supplemented by
B31.4a—1987.
Also available from ANSI.
ASTM.
Available from American Society for Testing and
Materials,
1916 Race Street,
Philadelphia,
PA 19103,
(215)
299—5400:
ASTM C94—90, Standard Specification for Ready—Mixed
Concrete,
approved
March
30,
1990.
ASTM D88-87, Standard Test Method for Saybolt
Viscosity,
April 24, 1981, reapproved January,
1987.
ASTM D93-85, Standard Test Methods for Flash Point by
Pensky—Martens Closed Tester,
approved October 25,
1985.
ASTM D1946—90,
Standard Practice for Analysis of
Reformed Gas by Gas Chromatoqraphy, Approved March 30,
1990.
ASTM D216l—87,
Standard Practice for Conversion of
Kinematic Viscosity to Saybolt Universal or to Saybolt
Furol Viscosity, March 27,
1987.
ASTM D2267—88,
Standard Test Method for Aromatics
in
Light Naphthas and Aviation Gasolines by Gas
Chromatography, approved November
17,
1988.
ASTM D2382—88,
Standard Test Method for Heat of
Combustion of Hydrocarbon Fuels by Bomb Calorimeter
(High Precision Method), approved October 31,
1988.
19
ASTM D2879-86,
Standard Test Method for Vapor
Pressure—Temperature Relationship and Initial
Decomposition Temperature of Liquids by Isoteniscope,
approved October 31,
1986.
ASTN D3828-87, Standard Test Methods for Flash Point
of Liquids by Setaflash Closed Tester, approved
December 14,
1988.
ASTM E168—88, Standard Practices for General
Techniques of Infrared Quantitative Analysis,
approved
May 27,
1988.
ASTN E169-87,
Standard Practices for General
Techniques of Ultraviolet—Visible Quantitative
Analysis, approved February
1,
1987.
ASTM E260—85, Standard Practice for Packed Column Gas
Chromatography,
approved June 28,
1985.
ASTM E926-88
C.
Standard Test Methods for Pre~arina
Refuse—Derived Fuel
(RDFI
Sanrnles for Analysie of
Metals.
Bomb-Acid Digestion Method, ar~rovedMarch 25,
1988.
ASTM Method G21—70
(2984a)
——
Standard Practice for
Determining Resistance of Synthetic Polymer Materials
to Fungi
ASTM Method G22—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.
20401j,
(202-)-
—783—3238j:
Standard Industrial Classification Manual
(1972), and
1977 Supplement,
republished in 1983
“Test Methods for Evaluatinc Solid Waste. Physical!
Chemical Methods,” U.S. EPA Publication number SW—846
(Third Edition. September 1986),
as amended bY Update
I
(July 1992)
(Document Number 955—001—00000—1).
NACE.
Available from the National Association of Corrosion
Engineers,
1400 South Creek Dr.,
Houston, TX
77084,
(713)
492—0535:
“Control of External Corrosion on Metallic Buried,
Partially Buried, or Submerged Liquid Storage
Systems”,
NACE Recommended Practice 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 Port Royal
20
Road,
Springfield, VA
22161,
(703)
487—4600:
“Generic Quality Assurance Project Plan for Land
Disposal Restrictions Program”,
EPA/530-SW—87—011,
March 15,
1987.
(Document number PB 88-170766.)
“Guidance on Air Quality Models”, Revised 1986.
(Document number PB86—245-248
(Guideline)
and PaSS-
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—l20—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 B4—l74820).
“Screening Procedures for Estimating the Air Quality
Impact of Stationary Sources”,
AuguotOctober, 19~~L.
(Dosumorit
nPublication
Number
PD99-169396EPA—450/R-
92—019.
“Toot Hothodo for Evaluating Solid Wapto, rhyoieal/
Chemioal Methods,” E~APublioatien number £N-~46
(Seeend Edition, 198~as amended by Update
I
(r~pril,
1984) and Update
II
(Z~pril, 1985))
(Document numbcr PB
87—120~91).
“Toot Hothoda
for
Evaluating Lolid Waste, Physical!
Ohemieul Mathodo,” ~I’Z~.
rublieation number OW 846
(Third Edition, September 1985
(Dooutnont number
i’R8S-
339223)
as ainondod by Rovigion I
(Doombor 1987)
and
Firat Update, January,
1983)
(Document Number FB89
148076)).
STI.
Available from the Steel Tank Institute,
728 Anthony
Trail, Northbrook,
IL
60062,
(312) 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,
WR
550
E,
Washington,
D.C.
20460:
“Technical
Assistance
Document:
Corrosion,
Its
Detection and Control in Injection Wells”, EPA 570/9-
87—002,
August,
1987.
~
Available from U..S~.EPA,Number F—90—WPWF-FFFFF,
Room 142427,
401
M Street SW, Washington, D.C.
20460,
(202)
475—9327:
“Test Method 8290:
Procedures for
the
Detection
and
21
Measurement of PCDDs and PCDFs”, EPA/530—SW-91—019
(January,
1991)
U.S.
EPA.
Available from Receptor Analysis Branch.
U.S. EPA
IMD-14).
Research
Triangle
Park.
NC
27711:
“Screenino
Procedures for Estimatina the Air Oualitv
Impact
of
Stationary
Sources.
Revised”. October.
1992,
Publication
Number
EPA—4501R—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
(1992)
40
CFR
51.100(u)
(1992)
40
CFR
51,
Subpart
W,
as
added
at
58
Fed.
Rea.
38822
(July
20,
1993)
40
CFR
60
(1992-i)
40
CFR
61,
Subpart
V
(199~)
40
CFR
136
(199~1)
40
CFR
142
(199~)
40
CFR
220
(1992)
40
CFR
260.20
(1992)
40
CFR
264
(1992)
40 CFR 268.Appendix IX
(1992)
40
CFR
302.4,
302.5
and
302.6
(1992)
40
CFR
761
(199&~)
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
18
111.
Req.
_________,
effective
______________________
SUBPART
C:
RULEMAKING
PETITIONS
AND
OTHER
PROCEDURES
Section
720.122
Waste
Delisting
a)
Any
person
seeking
to
exclude
a
waste
from a particular generating
facility
from
the
lists
in
35
Ill.
Adm.
Code
721.Subpart
D
may
file
a petition,
as specified
in subsection
(n)
below.
The Board
will grant the petition if:
1)
The
petitioner
demonstrates
that
the
waste
produced
by
a
particular
generating
facility
does
not
meet
any of the
22
criteria under which the waste was listed as a hazardous or
acute hazardous waste; and
2)
If the Board determines that there
is
a reasonable basis to
believe that factors (including additional constituents)
other than those for which the waste was listed could cause
the waste to be a hazardous waste,
that such factors do not
warrant retaining the waste as a hazardous waste.
A Board
determination under the preceding sentence must be made by
reliance on, and in a manner consistent with,
“Petitions to
Delict——A Guidance Manual”, incorporated by reference in
Section 720.111.
A waste ~hiohthat
is so excluded, however,
still may be a hazardous waste by operation of 35 Ill. Adm.
Code 72l.Subpart
C.
b)
Listed wastes and mixtures.
A person may also petition the Board
to exclude from 35
Ill. Adm. Code 721.103(a)(2)(B) or
(a) (21(C),
a
waste whiahthat is described in these Sections and is either a
waste listed in 35
Ill. Adm. Code 721.Subpart D,
or
is derived
from
a
waste listed in that Subpart.
This exclusion may only be
granted
for
a
particular
generating,
storage, treatment or
disposal facility.
The petitioner shall make the same
demonstration as required by subsection
(a)
above.
Where the
waste
is a mixture of a solid waste and one or more listed
hazardous wastes or is derived from one or more listed hazardous
wastes,
the demonstration must be made with respect to the waste
mixture as a whole; analyses must be conducted for not only those
constituents for which the listed waste contained
in the mixture
was listed as hazardous, but also for factors
(including
additional constituents) that could cause the waste mixture to be
a hazardous waste.
A waste vhiohthat is so excluded may still be
a hazardous waste by operation of
35 Ill. Adm. Code 72lSubpart
C.
C)
Ignitable, corrosive, reactive and toxicity characteristic wastes.
If the waste
is listed in codes
“I”,
“C”,
“R” or “E” in 35
Ill.
Adm. Code 721.Subpart D:
1)
The
petitioner
shall
demonstrate
that
the
waste does not
exhibit
the
relevant
characteristic
for
which
the waste was
listed,
as
defined
in
35
Ill.
Mm.
Code 721.121,
721.122,
721.123
or
721.124,
using
any
applicable
methods
prescribed
in those Sections.
The petitioner shall also show that the
waste does not exhibit any of the other characteristics,
defined in those Sections,
using any applicable methods
prescribed in those Sections;
2)
Based on a complete petition, the Board will determine,
if
it has a reasonable basis to believe that factors (including
additional constituents) other than those for which the
waste was listed could cause the waste to be hazardous
waste, that such factors do not warrant retaining the waste
as
a hazardous waste.
A Board determination under the
preceding sentence must be made by reliance on, and in a
manner consistent with, “Petitions to Delist——A Guidance
Manual”, incorporated by reference in Section 720.111.
A
waste whiohthat
is so excluded,
however, may still be a
hazardous waste by operation of
35 Ill. Adm. Code
721.Subpart
C.
d)
Toxic waste.
If the waste is listed in code “T” in
35 Ill. Adm.
Code
721.Subpart
D:
23
1)
The
petitioner
shall
demonstrate
that
the
waste:
A)
Does
not
contain
the
constituent
or constituents (as
defined in 35
Ill.
Adm.
Coda
721.Appendix
G)
that
caused U~S.EPA to list the waste,
using the
appropriate test methods prescribed in 35 Ill. Mm
Code
731.Appondix C”Test Methods for Evaluatina Solid
Waste~, Physical/Chemical Methods”.
U.S. EPA
Publication SW—846,
as
incoroorated by reference
iii
Section 720.111 or
B)
Although containing one or more of the hazardous
constituents
(as defined in 35 Ill. Adm. Code
721.Appendix G) that caused U~SJ.EPAto list the
waste,
does
not
meet
the criterion of
35
Ill.
Adm.
Code 721.111(a) (3) when considering the factors used
in 35 Ill. Adm. Code 721.111(a)(3)(A) through
(K)
under which the waste was listed as hazardous;
and
2)
Based on a complete petition, the Board will determine,
if
it has
a reasonable basis to believe that factors
(including
additional constituents) other than those for which the
waste was listed could cause the waste to be hazardous
waste,
that such factors do not warrant retaining the waste
as a hazardous waste.
3)
The petitioner shall demonstrate that the waste does not
exhibit any of the characteristics, defined in 35
Ill. Adm.
Code 721.121, 721.122,
721.123 or 721.124, using any
applicable methods prescribed in those Sections.
4)
A waste ~~hiahthatis
so excluded,
however, may still be a
hazardous waste by operation of
35
Ill. Adm. Code
721.Subpart
C.
e)
Acute hazardous waste.
If the waste is
listed with the code “H”
in 35
Ill. Adm. Code 721.Subpart D:
1)
The petitioner shall demonstrate that the waste does not
meet
the
criterion
of
35
Ill.
Adm.
Code
721.111(a)
(2);
and
2)
Based on
a
complete
petition,
the
Board will determine,
if
it has
a reasonable basis to believe that factors
(including
additional constituents)
other than those for which the
waste was listed could cause the waste to be hazardous
waste,
that such factors do not warrant retaining the waste
as a hazardous waste.
A Board determination under the
preceding sentence must be made by reliance on,
and
in a
manner consistent with,
“Petitions to Delict——A Guidance
Manual”, incorporated by reference in Section 720.111.
3)
The petitioner shall demonstrate that the waste does not
exhibit any of the characteristics, defined
in 35 Ill. Adm.
Code 721.121, 721.122,
721.123 or 721.124, using any
applicable methods prescribed in those Sections.
4)
A waste
,ihichthat is so excluded,
however, may still be a
hazardous waste by operation of 35
Ill. Adm. Code
721.Subpart
C.
h)
Demonstration samples must consist of enough representative
samples,
but in no case less than four samples, taken over
a
24
period of time sufficient to represent the variability or the
uniformity of the waste.
i)
Each petition must include,
in addition to the
information
required by subsection
(n) below:
1)
The name and address of the laboratory facility performing
the sampling or teats of the waste;
2)
The names and qualifications of the persona sampling and
testing the waste;
3)
The dates of sampling and testing;
4)
The location of the generating facility;
5)
A description of the manufacturing processes or other
operations and feed materials producing the waste and an
assessment of whether such processes,
operations or feed
materials can or might produce a waste ~hiohthat
is not
covered by the demonstration;
6)
A description of the waste and an estimate of the average
and
maximum
monthly and annual quantities of waste covered
by the demonstration;
7)
Pertinent data on and discussion of the factors delineated
in the respective criterion for listing a hazardous waste,
where the demonstration is based on the factors in 35 Ill.
Adm. Code 721.111(a) (3);
8)
A description of the methodologies and equipment used to
obtain the representative samples;
9)
A description of the sample handling and preparation
techniques,
including
techniquea
used
for
extraction,
containerization and preservation of the samples;
10)
A description of the tests performed
(including results);
11)
The names and model numbers of the instruments used in
performing
the
tests;
and
12)
The following statement signed by the generator or the
generator’ a authorized representative:
I certify under penalty of law that
I have personally
examined and am familiar with the information
submitted in this demonstration and all attached
documents,
and that, based on my inquiry of those
individuals immediately responsible for obtaining the
information,
I
believe
that
the
submitted
information
is
true,
accurate
and
complete.
I
am
aware
that
there
are significant penalties for submitting false
information,
including the possibility of fine and
imprisonment.
j)
After receiving a petition, the Board may request any additional
information
~hiohthat
the
Board
needs
to
evaluate
the
petition.
k)
An
exclusion
will
only apply to the waste generated at the
individual
facility
covered
by the demonstration and will not
25
apply to waste from any other facility.
1)
The Board will exclude only part of the waste for which the
demonstration
is submitted if the Board determines that
variability
of the waste
justifies a partial exclusion.
BOARD NOTE:
See “Petitions to Deliat Hazardous Wastes
—-
A
Guidance Manual”,
incorporated by reference in Section 720.111.
m)
Delisting of specific wastes from specific sources uhioh~~thave
been adopted by UJS~EPAmay be proposed as State regulations
uhiphthat are identical in substance pursuant to Section
720.120(a).
n)
Delistings uhishthat have not been adopted by UJ.S~EPAmay be
proposed to the Board pursuant to a petition for adjusted standard
pursuant to 35 Ill. Adm. Code 106.Subpart G.
The justification
for the adjusted standard is as specified in subsections
(a) et~
cog..throuah
(a)
above, as applicable to the waste in question.
The petition must be clearly labeled as a RCRA delisting adjusted
standard petition.
1)
In accordance with 35
Ill. Adm. Code 106.710, the petitioner
shall serve copies of the petition,
and any other documents
filed with the Board, on U~S.Z...EPAat the following
addresses:
U.S. EPA
Office of Solid Waste and Emergency Response
Washington,
D.C.
20460
U.~S.~EPA,Region
V
230
5.
Dearborn
Street
Chicago,
IL
60604
2)
The Board will mail copies of all opinions and orders to
U.~S.~.EPAat the above addresses.
3)
In
conjunction
with
the
normal
updating
of
the
RCRA
regulations,
the Board will maintain, in 35
Ill.
Adzn.
Code
721.Appendix
I,
a listing of all adjusted standards granted
by the Board.
0)
The
Agency
may
determine
in
a
permit or
a letter directed to
a
generator
that,
based
on
35
Ill.
Adm.
Code
721,
a waste from a
particular
source
is
not
subject to these regulations.
Such a
finding
is
evidence
against
the
Agency
in
any
subsequent
proceedings
but
shall
not
be conclusive with reference to other
persona
or
the
Board.
p)
Any
petition
to
delist
directed
to
the
Board
or
request
for
determination
directed
to
the
Agency
must
include
a
showing
that
the waste will
be
generated or managed in Illinois.
q~
The Board will not grant any petition ~.thiohthatwould render the
Illinois RCRA program less stringent than if the decision were
made by U.~S.~EPA.
r)
Delistings apply only within Illinois.
Generators shall comply
with
35
Ill.
Mm.
Code
722
for
waste
whiohthat
iB
hazardous in any
state
to
which
it is to be transported.
26
TITLE 35:
ENVIRONMENTAL PROTECTION
SUBTITLE G:
WASTE DISPOSAL
CHAPTER
I:
POLLUTION
CONTROL
BOARD
SUBCHAPTER
c:
HAZARDOUS WASTE
OPERATING
REQUIREMENTS
PART 721
IDENTIFICATION AND LISTING OF HAZARDOUS WASTE
SUBPART
A:
GENERAL PROVISIONS
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 WasteB
721.Appendix A
721.Appendix B
721.Appendix C
Table
A
Table
B
Table
C
721.Appendix G
721.Appendix B
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 ChemicalB
(Repealed)
Analytical Characteristics of Inorganic Species
(Repealed)
Sample Preparation/Sample Introduction Techniques (Repealed)
Basis
for
Listing
Hazardous
Wastes
Hazardous
Constituents
Wastes
Excluded
under Section
720.120
and
720.122
Wastes Excluded from Non—Specific Sources
Wastes Excluded from Specific Sources
Wastes Excluded From Commercial Chemical Products,
Off-
Specification
Species,
Container
Residues,
and
Soil
Residues
Thereof
Wastes
Excluded
by
Adjusted
Standard
(Source:
Amended at
18 Ill. Reg.
_________,
effective
_____________________)
Section
721.101
721.102
721. 103
721. 104
721.105
721. 106
721. 107
721. 108
Sect ion
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
27
721.Appendix
J
Method
of
Analysis
for
Chlorinated
Dibenzo—p—Dioxins and
Dibenzofurans
(Repealed)
721.Appendix
Z
Table to Section 721.102
AUTHORITY:
Implementing Section 22.4 and authorized by Section 27 of the
Environmental Protection Act
(Ill.
Rev. Stat.
1991,
ch. 111½,
pars.
1022.4 and
1027
(415 ILCS 5/22.4 and 27)).
SOURcE:
Adopted in R81—22, 43 PCB 427, ~t
5 Ill. Req.
9781, effective
as
noted in 35
Ill.
Adm. Code 700.106; amended and codified in R81-22,
45 PCB
317,
at
6
Ill.
Reg.
482a,
effective
as noted in
35
Ill.
Adm. Code 700.106;
amended in Rb2—18,
51 PCB 31,
at
7
Ill.
Rag.
2518,
effective February 22,
1983; amended
in R82—19,
53 PCB 131,
at
7
Ill. Req.
13999, affective October
12,
1983; amended in R84—34,
61 PCB 247,
at 8 Ill. Rag.
24562, effective
December 11,
1984;
amended in R84—9, at 9
Ill. Rag.
11834, affective July 24,
1985; amended in R85—22 at 10 Ill.
Req.
998, affective January 2,
1986;
amended in R85—2 at 10
Ill. Reg. 8112,
effective May
2,
1986;
amended in R86—1
at
10 Ill. Req.
14002,
effective August 12,
1986; amended in R86—3.9 at 10 Ill.
Req.
20647,
effective December
2,
1986; amended in R86-28 at
11
Ill.
Req.
6035, affective March 24,
1987;
amended in R86—46 at
11
Ill.
Req.
13466,
affective August
4,
1987; amended in R87-32 at
1.
Ill.
Req.
16698, effective
September 30,
1987;
amended in R87—5 at 11 Ill. Req.
19303, effective November
12,
1987;
amended in R87—26 at 12
Ill.
Req. 2456, affective January
15,
1988;
amended in R87—30 at 12
Ill.
Req. 12070,
effective
July
12,
1988;
amended
in
R87—39 at
12
Ill. Beg.
13006, effective July 29,
1988;
amended in R88—16 at
13
Ill. Rag.
382, effective December 27, 1988;
amended
in R89—1 at
13 Ill. Req.
18300, effective November
13,
1989;
amended in R90—2 at
14
Ill.
Req.
14401,
effective August 22,
1990;
amended in R90—10 at 14 Ill.
Req.
16472, effective
September 25, 1990; amended in R90—17 at 15
Ill. Req.
7950, effective May 9,
1991;
amended in R90-13. at
15
Ill. Req.
9332, affective June 17,
1991;
amended
in R91—1
at
15
Ill.
Req.
14473, effective September 30,
1991;
amended in R91—
12
at 16
Ill. Req. 2155,
effective January 27,
1992; amended in R91—26 at 16
Ill. Rag.
2600,
effective February
3,
1992;
amended in R91—13 at 16 Ill.
Rag.
9519,
affective June 9,
1992;
amended in
R92—2. at
16 Ill. Rag.
17666,
effective November
6,
1992;
amended in R92—10 at
17
Ill. Req.
5650, effective
March 26,
1993; amended
in R93—4 at
17
Ill.
Req.
20568, effective November 22,
1993;
amended in R93—16 at
18
Ill.
Req.
6741,
effective
April
26,
l994L
amended
in
R94—7
at
Ill.
Req.
•
effective
SUBPART
C:
CHARACTERISTICS OF HAZARDOUS
WASTE
Section
721.122
Characteristic of
Corrosivity
a)
A
solid
waste
exhibits
the
characteristic
of
corrosivity
if
a
representative sample of the waste has either of the following
properties:
1)
It
is aqueous and has
a pH less than or equal to 2 or
greater than or equal to
12.5,
as
determined
by
a
pH
meter
using
either
an
EPA teat methed
er
an
equivalent
test
methed
(35
Ill.
Adin.
Code 720.131).
The EPA toot methodo for pH
arc
opccificd
as
Methods
9040,
9041 or 9045 in “Test Methods
for the Evaluation of Solid Waste, Physical/Chemical
Methods”,
incorporated by reference in 35 Ill.
Adm. Code
720. 111.
2)
It is
a liquid and corrodes steel
(ShE 1020)
at
a rate
greater
than
6.35
mm
(0.250
inch)
per year at a test
temperature
of
550
C
(130°
F) as determined by the test
method
specified
in
MACE (National Association of Corrosion
Engineers) Standard TM-01—69 as standardized
in “Test
28
Methods for the Evaluation of Solid Waste,
Physical/Chemical
Methods”,
incorporated by reference in
35
Ill.
Adm. Code
720.111,
er an
equivalent test aethed
(35
Ill.
3Ld.
Cede
730.121).
BOARD NOTE:
The corrosivity characteristic determination
currently does not apply to non—liquid wastes,
as discussed
by U~.S~EPAat 45 Fed.
Req. 33109, May 19,
1980 and at
55
Fed. Req.
22549, June
1,
1990.
b)
A solid waste that exhibits the characteristic of corrosivity has
the US. EPA Hazardous Waste Number of D002.
(Source:
Amended at 18 Ill. Req.
_________,
effective
______________________)
Section 721.124
Toxicity Characteristic
a)
A solid waste exhibits the characteristic of toxicity if, using
the toot methedo described in Appendix
B or equivalent toot
methods approved by the Agenoy under the prooedurea
sot forth in
Seetions
7~0.130
and
720.l2lToxicity
Characteristic
Leachina
Procedure
(TCLP). test Method
1311
in “Teat Methods for Evaluatina
Solid Waste, Physical/Chemical Methods”. U.S. EPA Publication
SW—
846,
as incorporated by reference
in 35
Ill.
Adm. Code 720.111,
the extract from a representative sample of the waste contains any
of the contaminants listed in the table in subsection
(b) below at
a
concentration
equal
to
or
greater
than
the
respective
value
given
in
that
table.
Where
the
waste
contains
lass
than
0.5
percent
filterable
solids,
the
waste
itself,
after filtering using
the methodology outlined in Appendix OMethod
1311,
is
considered
to
be
the
extract
for
the
purpose
of
this
Section.
BOARD NOTE:
Generators are required to use the TOLP teat for ehe
hasardous i.~aotodetcrmination under 35
Ill.
Adzn.
Code 722.120 as
of September 25,
1990.
Provided,
ho.rnvor,
that,
ao cpooifiod at
ES Fed.
Bog.
11850, March
29,
1990,
omall
quantity
gonoratoro -el
IGO to 1000 kg/ month, ao defined in 35 Ill. Mm.
Code 721.10E,
may continue to use the EP toxicity test until March 29,
1991.
The EP toxioity toot
La Method 1310 in SW 84?,
“Toot Methods for
Evaluating Solid Wastes, Phyoieal/Ohomieal Methoda”- ineor~erated
hi,
rr~Erir~~nn~In
~S
Til
‘~m
fln,ir
7~CL1h1
T””
—~
______--
--_--
-
-
reference
to
the
“EP
toxicity
test”
in
35
Ill. Adm. Code 808.410(b)(4)
is to be
understood as referencing the test required by this Section.
b)
A solid waste that exhibits the characteristic of toxicity has the
U.~.S. EPA Hazardous Waste Number specified in the following table
vhiohthat corresponds to the toxic contaminant causing it to be
hazardous.
MAXIMUM
CONCENTRATION OF CONTAMINANTS
FOR THE TOXICITY CHARACTERISTIC
U~S.~EPA
Regulatory
Hazardous
CAS
Level (mg/L)
Waste No.
Contaminant
Number
Note
D004
Arsenic
7440—38—2
5.0
D005
Barium
7440—39—3
100.0
D018
Benzene
71—43—2
0.5
D006
Cadmium
7440—43—9
1.0
D019
Carbon tetra—
56—23—5
0.5
chloride
29
1)020
Chlordane
57—74—9
0.03
D021
Chlorobenzene
108—90—7
100.0
D022
Chloroform
67—66—3
6.0
1)007
Chromium
7440—47-3
5.0
1)023
o—Cresol
95—48—7
4
200.0
1)024
m—Creaol
108—39—4
4
200.0
D025
p—Creaol
106—44—5
4
200.0
D026
Crasol
4
200.0
1)016
2,4—D
94—75—7
10.0
D027
1,4—Dichlorobenzene
106—46—7
7.5
1)028
1,2—Dichioroethane
107—06—2
0.5
1)029
1,1—Dichloro—
75—35—4
0.7
ethylene
1)030
2,4—Dinitrotoluene
121—14—2
3
0.13
D012
Endrin
72—20—8
0.02
1)031
Heptachlor (and its
76—44—8
0.008
epoxide)
D032
Hexachlorobenzene
118—74—1
3
0.13
D033
Hexachlorobutadiene
87—68—3
0.5
1)034
Hexachloroethane
67—72—1
3.0
1)008
Lead
7439—92—1
5.0
1)013
Lindane
58—89—9
0.4
1)009
Mercury
7439—97—6
0.2
D014
Methoxychlor
72—43—5
10.0
D035
Methyl ethyl ketone
78—93—3
200.0
D036
Nitrobenzene
98—95—3
2.0
1)037
Pentachlorophenol
87—86—5
100.0
1)038
Pyridine
110—86—1
3
5.0
1)010
Selenium
7782—49—2
1.0
DOll
Silver
7440—22—4
5.0
D039
Tetrachloroethylene
127—18—4
0.7
1)015
Toxaphene
8001—35—2
0.5
1)040
Trichloroethylene
79—01—6
0.5
D041
2,4,5—Trichloro—
95—95—4
400.0
phenol
D042
2,4,6—Trichloro—
88—06—2
2.0
phenol
DQ17
2,4,5—TP
(Silvex)
93—72—1
1.0
D043
Vinyl
chloride
75—01—4
0.2
Notes to Table:
3
Quantitation limit
is greater than the calculated regulatory
level.
The quantitation limit therefore becomes the
regulatory level.
4
If o—,
at-,
p—cresol concentrations cannot be differentiated,
the total cresol
(D026) concentration is used.
The
regulatory level
of
total
cresol
is 200.0 mg/L.
(Source:
Amended at 18 Ill.
Req.
_________,
effective
___________________
Section
721.Appendix
Bi.
Method 1311 Toxicity Characteristic Leaching
Procedure
(TCLP)
The Beard ineerperatas by reference 40 GFB 261, Appendix II,
as amended at
Fed. Req.
55114
ineersertea no
5S117,
future
Nevember
editions
24, 1992 and ES
or stadifie.ationo.
Fed.
Beg.
6854.
This Coetj~
NOTE:
The
TCLP
(Method
1311)
is
published
in
“Test
Methods
for
Evaluatir~g
Solid
Waste,
Physical/Chemical
Methods”.
U.S.
EPA
publication
SW-846,
as
incorporated
by
reference
in
35
111.
Adxn.
Code
720.111.
30
(Source:
Amended
at 18 Ill. Req.
_________,
effective
_____________________)
Section 721.Appendix C÷
Chemical Analysis Test Methods
aand•d at
65
Fed
flee.
60483, December
8,
1900.
ThL•SseCienineerperatee
ne
future aditiena
at
a.diiieatiens.
NOTE:
Ao~ropriateanalytical orocedures to determine whether a
sample
contains
a aiven toxic
constituent are .~ecifLed in Charter Two, “Choosina the
Correct Procedure”,
found in “Test Methods for Evaluatina Solid Waste.
Physical/Chemical Methods”.
U.S.
EPA
Publication
SW—846,
as
incor~orated
by
reference
in
35
Ill.
Adm. Code
720. 111.
Prior
to
final
sampling
and
analysis
method selection, the individual should consult the specific section or
method
described in SW-846 for additional auidance on which of the a~~rovedmethods
should be em~lovedfor a specific aam~leanalysis situation.
(Source:
Amended at 18 Ill. Rag.
effective
Section 721.Appendix J+
Method of Analysis for Chlorinated
Dibenzo—p—Dioxins and Dibenzofurans (Re~ealed~
The Beard inserperatee by refarenas 40 OrB 261, Appendix X
(1985).
This Part
Lnseaparatas ne future
revipiens or editions.
(Source:
Repealed at 18 Ill. Req.
_________,
effective
________________
TITLE
35:
ENVIRONMENTAL
PROTECTION
SUBTITLE G:
WASTE DISPOSAL
CHAPTER
I:
POLLUTION
CONTROL
BOARD
SUBCHAPTER
c:
HAZARDOUS
WASTE
OPERATING
REQUIREMENTS
PART
724
STANDARDS
FOR
OWNERS
AND
OPERATORS
OF
HAZARDOUS
WASTE
TREATMENT,
STORAGE
MiD
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
Traininq
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
Sect ion
724.130
Applicability
724.131
Design
and
Operation
of
Facility
724.132
Required
Equipment
724.133
Testing
and
Maintenance
of
Equipment
31
724.134
Access to Communications or Alarm System
724.135
Required Aisle Space
724.137
Arrangements with Local Authorities
SUBPART D:
CONTINGENCY PLAN AND EMERGENCY PROCEDURES
Section
724.150
Applicability
724.151
Purpose and
Implementation
of
Contingency
Plan
724.152
Content
of
Contingency
Plan
724.153
Copies of Contingency Plan
724.154
Amendment of Contingency Plan
724.155
Emergency Coordinator
724.156
Emergency Procedures
SUBPART
E:
MANIFEST
SYSTEM,
RECORDKEEPING
AND
REPORTING
Section
724.170
Applicability
724. 171
Use of Manifest System
724.172
Manifest
Discrepancies
724.173
Operating Record
724.174
Availability, Retention and Disposition of Records
724.175
Annual Report
724.176
Unmanifested Waste Report
724.177
Additional
Reports
SUBPART
F:
RELEASES
FROM
SOLID
WASTE
MANAGEMENT
UNITS
Section
724.190
Applicability
724.191
Required
Programs
724.192
Groundwater
Protection
Standard
724.193
Hazardous Constituents
724.194
Concentration Limits
724.195
Point
of
Compliance
724.196
Compliance
Period
724.197
General Groundwater Monitoring Requirements
724.198
Detection
Monitoring
Program
724.199
Compliance Monitoring Program
724.200
Corrective Action Proqram
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
32
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
SUBPART J:
TANK
SYSTEMS
Section
724.290
Applicability
724.291
Assessment of Existing Tank System’s Integrity
724.292
Design and Installation of New Tank Systems or Components
724.293
Containment and Detection of Releases
724.294
General Operating Requirements
724.295
Inspections
724.296
Response to Leaks or Spills and Disposition of Leaking or unfit-
for—use Tank Systems
724.297
Closure and Post-Closure Care
724.298
Special
Requirements for Ignitable or Reactive Waste
724.299
Special Requirements for Incompatible Wastes
724.300
Special Requirements for Hazardous Wastes P020,
P021,
F022,
F023,
F026 and F027
SUBPART
K:
SURFACE
IMPOUNDMENTS
Section
724.320
Applicability
724.321
Design
and
Operating
Requirements
724.322
Action Leakage Rate
724.324,a
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, P021,
P022,
F023,
P026 and F027
SUBPART L:
WASTE PILES
Section
-
724.350
Applicability
724.351
Design and Operatinq 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, P021,
P022,
P023,
F026 and P027
33
SUBPART
M:
LAND
TREATMENT
Sect ion
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 P020, F021, P022,
P023,
P026
and
P027
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 P020, P021,
P022,
P023,
P026 and P027
SUBPART 0:
INCINERATORS
Section
724.440
Applicability
724.441
Waste Analysis
724.442
Principal Organic Hazardous Constituents
(POHC5)
724.443
Performance
Standards
724.444
Hazardous Waste Incinerator Permits
724.445
Operating Requirements
724.447
Monitoring and Inspections
724.451
Closure
SUBPART 5:
CORRECTIVE ACTION FOR SOLID WASTE MANAGEMENT UNITS
Section
724.652
Corrective Action Management Units
724.653
Temporary Units
SUBPART
W:
DRIP
PADS
Section
724. 670
Applicability
724.671
Assessment of existing
drip
pad
integrity
724.672
Design and installation of new drip pads
724.673
Design and operating requirements
724.674
Inspections
724.675
Closure
SUBPART X:
MISCELLANEOUS UNITS
Section
724. 700
Applicability
724.701
Environmental Performance Standards
34
Monitoring, Analysis,
Inspection,
Response, Reporting and
Corrective Action
Poet—closure Care
SUBPART AR:
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
SB:
AIR
EMISSION
STANDARDS
FOR
EQUIPMENT
LEAKS
Applicability
Definitions
Standards:
Standards:
Standards:
Standards:
Standards:
Standards:
Standards:
Connectors
Standards:
Delay of Repair
Standards:
Closed—vent Systems and Control Devices
Alternative Percentage Standard for Valves
Skip Period Alternative for Valves
Test
Methods
and
Procedures
Recordkeeping Requirements
Reporting Requirements
Applicability
Design and operating standards
Closure
and
post—closure
care
724.Appendix A
Recordkeeping
Instructions
724.Appendix B
EPA Report Form and Instructions
(Repealed)
724.Appendix
1)
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
(Ill.
Rev.
Stat.
1991,
ch.
111½,pare.
1022.4
and
1027
415
ILCS
5/22.4
and
27).
SOURCE:
Adopted in R82—19,
53
PCB
131,
at
7
Ill.
Req.
14059,
effective
October 12,
1983;
amended in R84—9 at
9 Ill. Req.
11964, effective July 24,
1985;
amended in R85—22
at
10 Ill. Reg.
1136, effective January
2,
1986;
amended in R86—1 at 10
Ill. Req.
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. Req.
8684, effective April
21,
1987; amended in R86—46 at
11
Ill.
Reg.
13577,
effective August
4,
1987;
amended in R87—S
at
11
Ill. Req. 19397,
effective November 12,
1987;
amended
in R87—39 at
12
Ill. Req.
13135,
effective July 29,
1988;
amended
in R88—16 at
13
Ill.
Reg.
458, effective
December 28,
1988;
amended in R89—1 at
13 Ill. Reg.
18527,
effective November
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
724.964
724. 965
Section
724.1100
724.1101
724. 1102
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
SUBPART
DD:
CONTAINMENT BUILDINGS
35
13,
1989; amended in R90—2 at
14 Ill.
Req. 14511,
effective August
22,
1990;
amended in R90—10 at 14
Ill. Req.
16658, effective September 25,
1990;
amended
in R90—11 at
15
Ill. Req. 9654,
effective June
17,
1991;
amended in R91—l at
15 Ill. Rag.
14572, effective October
1,
1991;
amended in R91—13 at
16
Ill.
Req.
9833, effective June
9,
1992;
amended in R92—1 at
16 Ill. Req. 17666,
effective November
6,
1992; amended in R92-10 at
17
Ill. Req.
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. Req.
6973,
effective April
26,
1994j.
amended in R94-7
at
Ill.
Req.
,
effective
SUBPART
J:
TANK
SYSTEMS
Section
724.290
Applicability
The requirements of this Subpart apply to owners and operators of facilities
that use tank systems for storing or treating hazardous waste, except as
otherwise provided in subsections
(a),
(b)
or
(c) below or in Section 724.101.
a)
Tank systems that are used to store or treat hazardous waste
whichthat contains no free liquids and are situated inside
a
building with an impermeable floor are exempted from the
requirements in Section 724.293.
To demonstrate the absence or
presence
of
free
liquids
in
the
stored
or
treated
waste,
~j~g
following test must be used:
U.S. EPA Method
9095
(Paint Filter
Liquids Test)~as described in “Test Methods for Evaluating Solid
Wastes Physical/Chemical Methods”
U.S.
EPA
Publication
No.
SW—846),
incorporated by reference in 35
Ill. Adm. Code 720.111—,-
must
bct uocd.
b)
Tank systems,
including Bumps, are defined in 35 Ill. Adm. Code
720.110,
that serve as part of a secondary containment system to
collect or contain releases of hazardous wastes are exempted from
the requirements in Section 724.293(a).
c)
Tanks,
sumps and other such collection devices or systems used in
conjunction with drip pads, as defined
in
35
Ill.
Adm. Code
720.110 and regulated under Subpart W of this Part, must meet the
requirements of this Subpart.
(Source:
Amended at
18
Ill.
Req.
_________,
effective
______________________
SUBPART N:
LANDFILLS
Section 724.414
Special Requirements for Bulk and Containerized Liquids
a)
This subsection corresponds with 40 CFR 264.314(a), which pertains
to pre May
8,
1985 actions,
a date long since passed.
This
statement maintains structural consistency with U~.S.~EPArules.
b)
The placement of bulk or non-containerized liquid hazardous waste
or
hazardous
waste
containing
free
liquids
(whether
or
not
sorbents
have
been
added)
in any landfill
is prohibited.
c)
To
demonstrate
the
absence
or
presence
of
free
liquids
in
either
a
containerized
or
a bulk waste,
the following test must be used:
Method 9095
(Paint Filter Liquids Test) as described in “Test
Methods
for Evaluating Solid Wastes, Physical/Chemical Methods-,-”~
+U.S.
EPA Publication
No. SW-846,
incorporated by reference in 35
Ill. Adm.
Code 724~O.l11.
36
d)
Containers holding free liquids must not be placed in
a landfill
unless;
1)
All
free—standing
liquid:
A)
has
been
removed
by
decanting
or
other
methods;
B)
has been mixed with sorbent or solidified so that
free—standing liquid is no longer observed; or
C)
has been otherwise eliminated; or
2)
The
container
is
very
small,
such
as
an
ampule;
or
3)
The
container
is designed to hold free liquids for use other
than storage, such
as
a battery or capacitor; or
4)
The container
is
a lab pack as defined in Section 724.416
and is disposed of in accordance with Section 724.416.
a)
Sorbents used to treat
free liquids to be disposed of in landfills
must be nonbiodegradable.
Nonbiodegradable sorbents are:
materials listed or described in subsection (e)(1)
below;
materials that pass one of the tests in subsection (e)(2)
below;
or materials that are determined by the Board to be
nonbiodegradable through the 35
Ill. Adm. Code 106 adjusted
standard process.
1)
Nonbiodegradable sorbents are:
A)
Inorganic minerals,
other inorganic materials, and
elemental carbon (e.g., aluminosilicates,
clays,
smectites, Fuller’s earth, bentonite,
calcium
bentonite,
montmorillonite, calcined montmorillonite,
kaolinite, micas (illite),
vermiculites,
zeolites;
calcium carbonate (organic free limestone); oxides/
hydroxides, alumina,
lime,
silica
(sand), diatomaceous
earth; perlite
(volcanic glass); expanded volcanic
rock;
volcanic ash;
cement kiln dust;
fly ash; rice
hull ash; activated charcoal
(activated carbon));
or
B)
High molecular weight synthetic polymers
(e.g.,
polyethylene, high density polyethylene (HDPE),
polypropylene,
polystrene,
poly urethane, polycrylate,
polynorborene, polyisobutylene, ground synthetic
rubber,
cross-linked allylstrene and tertiary butyl
copolymers).
This
does
not
include
polymers
derived
from biological material or polymers specifically
designed to be degradable;
or
C)
Mixtures of these nonbiodegradable materials.
2)
Tests for nonbiodegradable sorbents:
A)
The sorbent material
is determined to be
nonbiodeqradable under ASTM Method G21-70
(1984a)-.-
Standard Practice for Determining Resistance of
Synthetic Polymer Materials to Fungi”. incoroorateQ~
reference in
35 Ill. Adm. Code 720.111
or
B)
The
sorbent
material
is
determined
to
be
nonbiodegradable under ASTM Method G22-76 (1984b)--
37
Standard Practice for Determining Resistance of
Plastics to Bacteria”, incorporated by reference in ~35
Ill.
Adm. Code 720.111.
f)
The placement of any liquid. ~hichthat is not
a hazardous waste in
a landfill
is prohibited
(35
Ill. Adm. Code 729.311).
(Source:
Amended at 18 Ill.
Req.
________,
effective
________________
TITLE 35:
ENVIRONMENTAL PROTECTION
SUBTITLE G:
WASTE DISPOSAL
CHAPTER
I:
POLLUTION CONTROL BOARD
SUBCHAPTER
c:
HAZARDOUS WASTE OPERATING REQUIREMENTS
PART
725
INTERIM
STATUS
STANDARDS
FOR
OWNERS
AND
OPERATORS
OF
HAZARDOUS
WASTE
TREATMENT, STORAGE AND DISPOSAL FACILITIES
SUBPART A:
GENERAL PROVISIONS
Section
725.101
Purpose,
Scope
and
Applicability
725.104
Imminent Hazard Action
SUBPART
B:
GENERAL
FACILITY
STANDARDS
Section
725.110
Applicability
725.111
USEPA Identification Number
725.112
Required
Notices
725.113
General Waste Analysis
725.114
Security
725.115
General Inspection Requirements
725.116
Personnel Training
725.117
General Requirements for Ignitable,
Reactive or Incompatible
Wastes
725.118
Location Standards
725.119
Construction Quality Assurance Program
SUBPART
C:
PREPAREDNESS
AND
PREVENTION
Sect ion
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
38
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
hampling and Analysis
725.193
Preparation, Evaluation and Response
725.194
Recordkeeping and Reporting
SUBPART G:
CLOSURE AND POST-CLOSURE
Section
725.210
Applicability
725.211
Closure Performance Standard
725.212
Closure Plan; Amendment of Plan
725.213
Closure; Time Allowed for Closure
725.214
Disposal
or
Decontamination
of
Equipment,
Structures
and
Soils
725.215
Certification of Closure
725.216
Survey
Plat
725.217
Post-closure Care and Use of Property
725.218
Post—closure Plan; Amendment of Plan
725.219
Post-Closure Notices
725.220
Certification of Completion of Post—Closure Care
SUBPART H:
FINANCIAL REQUIREMENTS
Sect ion
725.240
Applicability
725.241
Definitions of Terms as Used in this Subpart
725.242
Cost Estimate for Closure
725.243
Financial Assurance for Closure
725.244
Cost
Estimate
for
Post—closure
Care
725.245
Financial Assurance for Post—closure Monitoring and Maintenance
725.246
Use of a Mechanism for Financial Assurance of Both Closure and
Post—closure Care
725.247
Liability
Requirements
725.248
Incapacity
of
Owners
or
Operators,
Guarantors or Financial
Institutions
725.251
Promulgation of Forms
(Repealed)
SUBPART
I:
USE AND MANAGEMENT OF CONTAINERS
Section
725.270
Applicability
725.271
Condition of Containers
725.272
Compatibility of Waste with Container
725.273
Management of Containers
725.274
Inspections
725.276
Special Requirements for Ignitable or Reactive Waste
725.277
Special Requirements for Incompatible Wastes
SUBPART J:
TANK
SYSTEMS
Section
725.290
Applicability
725.291
Assessment
of
Existing
Tank System’s Integrity
725.292
Design and Installation of New Tank Systems or Components
725.293
Containment and Detection of Releases
725.294
General Operating Requirements
725.295
Inspections
39
725.296
Response to leaks or spills and disposition
of Tank Systems
725.297
Closure
and
Post—Closure
Care
725.298
Special Requirements for Ignitable or Reactive Waste
725.299
Special Requirements for Incompatible Wastes
725.300
Waste Analysis and Trial Tests
725.301
Generators of 100 to 1000 kg/mo.
SUBPART K:
SURFACE IMPOUNDMENTS
Section
725.320
Applicability
725.321
Design and Operating Requirements
725.322
action Leakage Rate
725.323
Response Actions
725.324
Containment System
725.325
Waste Analysis and Trial Tests
725.326
Monitoring and Inspections
725.328
Closure and Post—Closure Care
725.329
Special
Requirements
for
Ignitable or Reactive Waste
725.330
Special Requirements for Incompatible Wastes
SUBPART
L:
WASTE PILES
Section
725.350
Applicability
725.351
Protection from Wind
725.352
Waste Analysis
725.353
Containment
725.354
Design and Operating Requirements
725.355
Action Leakage Rates
725.356
Special Requirements for Ignitable or Reactive Waste
725.357
Special Requirements for Incompatible Wastes
725.358
Closure and Post—Closure Care
725.359
Response Actions
725.360
Monitoring
and
Inspection
SUBPART
14:
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)
40
SUBPART 0:
INCINERATORS
Sect
ion
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
Sect ion
725.470
Other Thermal Treatment
725.473
General
Operating
Requirements
725.475
Waste Analysis
725.477
Monitoring and Inspections
725.481
Closure
725.482
Open Burning; Waste Explosives
725.483
Interim Status Thermal Treatment Devices Burning Particular
Hazardous Waste
SUBPART Q:
CHEMICAL, PHYSICAL AND BIOLOGICAL TREATMENT
Section
725
•
500
Applicability
725.501
General Operating Requirements
725.502
Waste Analysis and Trial Tests
725.503
Inspections
725.504
Closure
725.505
Special Requirements for Ignitable or Reactive Waste
725.506
Special Requirements for Incompatible Wastes
SUBPART R:
UNDERGROUND INJECTION
Section
725.530
Applicability
SUBPART W:
DRIP PADS
Section
725.540
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 AR:
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
SB:
AIR
EMISSION
STANDARDS
FOR
EQUIPMENT
LEANS
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
41
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 DD:
CONTAINMENT BUILDINGS
Section
725.1100
Applicability
725.1101
Design and operating standards
725.1102
Closure and post—closure care
725.Appendix A
Recordkeepinq Instructions
725.Appendix
B
EPA Report Form and Instructions
(Repealed)
725Appendix
C
EPA
Interim
Primary
Drinking Water Standards
725.Appendix D
Tests for Significance
725.Appendix E
Examples of Potentially Incompatible Waste
AUTHORITY:
Implementing Section 22.4 and authorized by Section 27 of the
Environmental Protection Act
(Ill.
Rev. Stat.
1991,
ch.
111½, pars.
1022.4 and
1027
(415 ILCS 5/22.4 and 27)).
SOURCE:
Adopted in R81—22,
43 PCB 427, at
5
Ill. Req.
9781, effective as
noted in 35
Ill.
Adm. Code 700.106; amended and codified in R81-22,
45 PCB
317, at
6 Ill.
Req.
4828, effective as noted in 35
Ill. Adm. Code 700.106;
amended in R82—18,
51 PCB 831, at
7 Ill.
Req. 2518,
effective February 22,
1983; amended in R82—19,
53
PCB
131,
at 7
Ill. Req.
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.
Req.
1085,
effective
January
2,
1986;
amended in
R86—1 at
10
Ill. Req.
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. Rag.
19338,
effective November 10,
1987;
amended in R87—26 at 12
Ill.
Req.
2485,
effective
January
15,
1988;
amended in R87—39 at 12
Ill. Req.
13027, effective July 29,
1988; amended
in R88—16 at
13
Ill. Reg.
437, effective December 28,
1988;
amended in R89—1 at
13
Ill.
Req.
18354, effective November
13,
1989;
amended
in R90—2
at
14
Ill. Req.
14447, effective August 22,
1990; amended in R90—lO
at 14
Ill. Req. 16498,
effective September 25,
1990; amended in R90—1l
at
15
Ill. Reg.
9398,
effective June 17,
1991; amended in R91—1 at
15 Ill. Req.
14534, effective October
1,
1991; amended
in R91—13 at
16 Ill. Reg.
9578,
effective
June
9,
1992;
amended
in
R92—1
at
16
Ill.
Req.
17672,
effective
November
6,
1992; amended in R92—10 at
17
Ill.
Req.
5681, effective March 26,
1993; amended in R93—4 at
17
Ill.
Req. 20620,
effective November 22,
1993;
amended in R93—16 at 18
Ill.
Req.
6773., effective April 26,
1994:
amended in
R94—7
at
Ill.
Req.
•
effective
SUBPART J:
TANK SYSTEMS
Section 725.290
Applicability
The regulations of this Subpart apply to owners and operators of facilities
that use tank
systems
for
storing
or treating hazardous waste,
except as
otherwise provided
in subsections
(a),
(b)
or
(C)
below,
or in Section
725.101.
a)
Tank systems that are used to store or treat hazardous waste
whiohthat contains no free liquids and that are situated inside
a
42
building
with
an
impermeable floor are exempted from
the
requirements
in Section 725.293.
To demonstrate the absence or
presence of free
liquids
in
the
stored~
or
treated
waste,
~
followina test muat be used:
U~S3~..EPAMethod 9095
(Paint Filter
Liquids Test)3, as described in “Test Methods for Evaluating Solid
Wastes, Physical/chemical Methods”3, fU.S. EPA Publication No.
SW—846), incorporated by reference in 35
Ill.
Adm. Code 720.111,r
ust be
usod.
b)
Tank systems, including sumpa,
as defined in 35
Ill. Adm. Code
720.110, that serve as part of
a secondary containment system to
collect or contain releases of hazardous wastes are exempted from
the requirements in Section 725.293(a).
C)
Tanks,
sumpa and other collection devices used in conjunction with
drip pads, as defined in 35 Iii.
Adxn.
Code 720.110 and regulated
under Subpart W of this Part, must meet the requirements of this
Subpart.
(Source:
Amended at 18 Ill.
Req.
_________,
effective
______________________
SUBPART N:
LANDFILLS
Section 725.414
Special Requirements for Liquid Wastes
a)
This subsection corresponds with 40 CFR 265.314(a), which pertains
to the placement of bulk or non—containerized liquid waate or
waste containing free liquids in a landfill prior to May
8,
1985.
This statement maintains structural
consistency with U3,S~EPA
rules.
b)
The placement of bulk or non-containerized liquid hazardous waste
or
hazardous
waste
containing
free
liquids
(whether
or
not
sorbents have been added)
in any landfill
is prohibited.
C)
Containers holding free liquids must not be placed in a landfill
unless;
1)
All
free—standing
liquid:
A)
has
been
removed
by
decanting
or
other
methods;
B)
has been mixed with sorbent or solidified so that
free—standing liquid is no longer observed;
or
C)
has been otherwise eliminated;
or
2)
The
container
is very small,
such as an ampule;
or
3)
The container is designed to hold free liquids for use other
than storage,
such as a battery or capacitor; or
4)
The container is a
lab
pack as defined
in Section 724.416
and is disposed of in accordance with Section 724.416.
d)
To demonstrate the absence or presence of free liquids in either a
containerized or a bulk waste, the following test must be used:
Method 9095
(Paint Filter Liquids Test)3, as described in “Test
Methods for Evaluating Solid Wastes, Physical/Chemical Methods.,.”3,
.f-U.S. EPA Publication No.
SW-846,
incorporated by reference in
35
Ill.
Adm. Code 724~O.111.
43
e)
The placement of any liquids whiohthat is not a hazardous waste in
a landfill
is prohibited
(35
Ill.
Adm. Code 729.311).
f)
Sorbents used to treat free liquids to be disposed of in landfills
must be nonbiodegradable.
Nonbiodegradable sorbents are:
materials listed or described in subsection
(f)(1)
below;
materials that pass one of the tests in subsection
(f)(2) below;
or materials that are determined by Board to be nonbiodegradable
through the
35
Ill. Adm. Code 106 adjusted standard process.
1)
Nonbiodegradable sorbents
are:
A)
Inorganic minerals,
other inorganic materials,
and
elemental carbon
(e.g.,
aluminosilicates, clays,
smectites,
Fuller’s earth, bentonite, calcium
bentonite, montmorillonite, calcined montmorillonite,
kaolinite,
micas (illite), vermiculites,
zeolites;
calcium carbonate
(organic free limestone); oxides!
hydroxides,
alumina,
lime,
silica
(sand),
diatomaceous
earth; perlite
(volcanic glass); expanded volcanic
rock; volcanic ash;
cement kiln dust;
fly ash; rice
hull ash; activated charcoal/activated carbon); or
B)
High molecular weight synthetic polymers (e.g.,
polyethylene,
high density polyethylene (HDPE),
polypropylene, polystyrene, polyurethane,
polyacrylate,
polynorborene, polysobutylene, ground
synthetic rubber, cross-linked allylstyrene and
tertiary butyl copolymers).
This does not include
polymers derived from biological material or polymers
specifically designed to be degradable;
or
C)
Mixtures of these nonbiodegradable materials.
2)
Tests
for nonbiodegradable sorbents.
A)
The sorbent material is determined to be
nonbiodegradable under ASTM Method G2l-70 (1984a)~-
Standard Practice for Determining Resistance of
Synthetic Polymer Materials to Fungi”~ incorporated by
reference
in
35
Ill.
Adm.
Code 720.111 or
B)
The sorbent material is determined to be
nonbiodegradable under ASTM Method G22-76 (l984b)~—
~Standard
Practice
for
Determining Resistance of
Plastics to Bacteria”.
incorDorated by reference
in 35
Ill. Adm. Code 720.113.
(Source:
Amended at
18
Ill. Req.
_________,
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
44
Section
726.120
Applicability
726.121
Standards applicable to generators and transporters of materials
used in a manner that constitutes disposal
726.122
Standards applicable to storers, who are not the ultimate users,
of materials that are to be used in a manner that constitutes
disposal
726.123
Standards applicable to users of materials that are used in a
manner that constitutes disposal
SUBPART
D:
HAZARDOUS
WASTE
BURNED
FOR
ENERGY
RECOVERY
Section
726.130
Applicability (Repealed)
726.131
Prohibitions (Repealed)
726.132
Standards applicable to generators of hazardous waste fuel
(Repealed)
726.133
Standards applicable to transporters of hazardous waste fuel
(Repealed)
726.134
Standards applicable to marketers of hazardous waste fuel
(Repealed)
726.135
Standards applicable to burners of
hazardous waste fuel
(Repealed)
726.136
Conditional exemption for spent materials and by—products
exhibiting a characteristic of hazardous waste
(Repealed)
SUBPART E:
USED OIL BURNED FOR ENERGY RECOVERY
(Repealed)
Section
726.140
Applicability
(Repealed)
726.141
Prohibitions
(Repealed)
726.142
Standards applicable to generators of used oil burned for energy
recovery
(Repealed)
726.143
Standards applicable to marketers of used oil burned for energy
recovery
(Repealed)
726.144
Standards applicable to burners of used oil burned for energy
recovery
(Repealed)
SUBPART
F:
RECYCLABLE
MATERIALS
UTILIZED
FOR
PRECIOUS
METAL
RECOVERY
Section
726.170
Applicability and requirements
SUBPART G:
SPENT LEAD-ACID BATTERIES BEING RECLAIMED
Section
726.180
Applicability and requirements
SUBPART H:
HAZARDOUS WASTE BURNED
IN BOILERS
AND INDUSTRIAL FURNACES
Section
726.200
Applicability
726.201
Management prior to Burning
726.202
Permit standards for Burners
726.203
Interim e~tatuse~tandardsfor Burners
726.204
Standards to .Qontrol Organic Emissions
726.205
Standards to control PM
726.206
Standards to e~ontrolMetals Emissions
726.207
Standards to control HC1 and Chlorine Gas Emissions
726.208
Small quantity On—site Burner Exemption
726.209
Low risk waste Exemption
726.210
Waiver of DRE trial burn for Boilers
726.211
Standards for direct Transfer
726.212
Regulation of Residues
726.219
Extensions of Time
45
726.Appendix A
Tier
I and Tier II Feed Rate and Emissions Screening Limits
for Metals
726.Appendix B
Tier
I Feed Rate Screening Limits for Total Chlorine
726.Appendix C
Tier
II Emission Rate Screening Limits for Free Chlorine and
Hydrogen Chloride
726.Appendix D
Reference Air Concentrations
726.Appeadix E
Risk Specific Doses
726.Appendix F
Stack Plume Rise
726.Appendix G
Health—Based Limits for Exclusion of Waste—Derived Residues
726.Appendix H
Potential PICs for Determination of Exclusion of Waste—
Derived Residues
726.Appendix
I
Methods Manual for Compliance with BIF Regulations
726.Appendix J
Guideline on Air Quality Models
726 Appendix K
Lead-Bearing Materials That May be Processed in Exempt Lead
Smelters
726.Appendix L
Nickel or Chromium-Bearing Materials that may be processed
in Exempt Nickel—Chromium Recovery Furnaces
726.Table A
Exempt Quantities
for Small Quantity Burner Exemption
AUTHORITY:
Implementing Section 22.4 and authorized by Section
27 of the
Environmental Protection Act
(Ill. Rev.
Stat.
1991,
ch. 111½,
pars.
1022.4 and
1027
(415 ILCS 5/22.4 and 27)).
SOURCE:
Adopted in R85—22
at
10
Ill. Req.
1162,
effective January 2,
1986;
amended in R86—1 at 10 Ill. Req.
14156, effective August 12,
1986;
amended in
R87—26 at
12
Ill.
Req. 2900,
effective January
15,
1988;
amended in R89—1 at
13 Ill. Req.
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. Req.
9727,
effective June 17,
1991;
amended in R91—13 at 16 Ill. Req.
9858, effective
June 9,
1992;
amended in R92—10 at
17 Ill. Req. 5865,
effective March 26,
1993;
amended in R93—4 at 17 Ill. Req. 20904,
effective November 22, 1993k
amended in R94—7
at
Ill. Req.
•
effective
SUBPART H:
HAZARDOUS WASTE BURNED IN BOILERS
AND INDUSTRIAL FURNACES
Section 726.203
Interim e~tatusestandards for Burners
a)
Purpose,
scope,
applicability.
1)
General.
A)
The purpose of this Section is to establish minimum
national standards for owners and operators of
“existing” BIF5 that burn hazardous waste where such
standards define the acceptable management of
hazardous waste during the period of interim status.
The standards of this Section apply to owners and
operators of existing facilities until either a permit
is issued under Section 726.202(d) or until closure
responsibilities identified in this Section are
fulfilled.
B)
“Existing” or “in existence” means
a BIF for which the
owner or operator filed a certification of
precompliance with U3,S.~.EPApursuant to 40 CFR
266.103(b), incorporated by reference in subsection
(b),. below;
provided,
however, that U3,S~EPAhas not
determined that the certification is invalid.
C)
If
a BIF is
located at a facility that already has a
46
RCRA permit or interim status,
then the owner or
operator shall comply with the applicable regulations
dealing with permit modifications in 35 Ill.
Adm. Code
703.280 or changes in interim status in 35
Ill.
Adm.
Code 703.155.
2)
Exemptions.
The requirements of this Section do not apply
to hazardous waste and facilities exempt under Sections
726.200(b) or 726.208.
3)
Prohibition on burning dioxin-listed wastes.
The following
hazardous waste listed for dioxin and hazardous waste
derived from any of these wastes must not be burned in a BIF
operating under interim status:
U3,S~EPAHhazardous W~aste
N~umbersF020, P021, P022,
P023,
P026 and P027.
4)
Applicability of 35
Ill. Adm. Code 725 standards.
Owners
and operators of BIFs that burn hazardous waste and are
operating under interim status are subject to the following
provisions of 35 Ill. Adm.
Code 725, except as provided
otherwise by this Section:
A)
In Subpart A of this Part
(General),
35
Ill. Adm. Code
725.104;
B)
In Subpart B of this Part (General facility
standards),
35 Ill.
Adm.
Code 725.111 through 725.117;
C)
In Subpart C of this Part (Preparedness and
prevention), 35 Ill.
Adm.
Code 725.131 through
725.137;
D)
In Subpart D of this Part
(Contingency plan and
emergency procedures),
35 Ill.
Adm. Code 725.151
through 725.156;
E)
In Subpart
E of this Part
(Manifest system,
recordkeeping and reporting),
35 Ill.
Adm. Code
725.171 through 725.177, except that
35
Ill.
Adm.
Code
725.171, 725.172 and 725.176 do not apply to owners
and operators of on—site facilities that do not
receive any hazardous waste from off—site sources;
F)
In Subpart G of this Part
(Closure and post—closure),
35 Ill.
Adm.
Code 725.211 through 725.215;
G)
In Subpart
H of this Part
(Financial requirements),
35
Ill.
Adxn. Code 725.241,
725.242,
725.243
and 725.247
through 725.251, except that the State of Illinois and
the Federal government are exempt
from the
requirements of 35
Ill.
Adxu. Code 725.Subpart
H; and
H)
~~Subpart
BB of this Part
(Air emission standards for
equipment leaks), except
35 Ill. Adm. Code 725.950(a).
5)
Special requirements for furnaces.
The following controls
apply during interim status to industrial
furnaces (e.g.,
kilns,
cupolas) that feed hazardous waste for a purpose
other than solely as an ingredient
(see subsection
(a)(5)(B)-,. above) at any location other than the hot end
where products
are normally discharged or where fuels are
normally fired:
47
A)
Controls.
i)
The hazardous waste must be fed at
a location
where combustion gas temperatures are at least
1800—°_F;
ii)
The owner or operator shall determine
that
adequate oxygen is present
in combustion gases
to combust organic constituents in the waste and
retain documentation of such determination in
the facility record;
iii)
For cement kiln systems, the hazardous waste
must be fed into the kiln;
and
iv)
The MC controls of Section 726.204(f)
or
subsection (c)(5)r below, apply upon
certification of compliance under subsection
(c), below,
irrespective of the CO level
achieved during the compliance test.
B)
Burning hazardous waste solely as an ingredient.
A
hazardous waste is burned for
a purpose other than
“solely as an ingredient”
if
it meets either of these
criteria:
i)
The hazardous waste has
a total concentration of
nonmetal compounds listed in 35
Ill. Adm. Coda
721.Appendix H, exceeding 500 ppm by weight,
as
fired and so is considered to be burned for
destruction.
The concentration of nonmetal
compounds in a waste as—generated may be reduced
to the 500 ppm limit by bona fide treatment that
removes or destroyB nonmetal constituents.
Blending for dilution to meet the 500 ppm limit
is prohibited and documentation that the waste
has not been impermissibly diluted must be
retained in the facility record; or
ii)
The hazardous waste has
a heating value of 5,000
Btu/lb or more, as~fired,
and so
is considered
to be burned as fuel.
The heating value of a
waste as—generated may be reduced to below the
5,000 Btu/lb limit by bona fide treatment that
removes or destroys organic constituents.
The
heating value of
a waste as—generated may be
reduced to below the 5,000 Btu/lb limit by bona
fide treatment that removes or destroys organic
constituents.
Blending to augment the heating
value to meet the 5,000 Etu/ib limit
is
prohibited and documentation that the waste has
not been irnpermissibly blended must be retained
in the facility record.
6)
Restrictions on burning hazardous waste that is not
a fuel.
Prior to certification of compliance under subsection
(C),-
below,
owners and operators shall not feed hazardous waste
that has
a heating value less than 5000 Btu/lb,
as
generated,
(except that the heating value of a waste as—
generated may be increased to above the 5,000 Btu/lb limit
by bone fide treatment; however blending to augment the
heating value to meet the 5,000 Btu/lb limit
is prohibited
48
and records must be kept to document that impermisaible
blending has not occurred)
in a BIF, except that:
A)
Hazardous waste may be burned solely as an ingredient;
or
B)
Hazardous waste may be burned for purposes of
compliance testing (or testing prior to compliance
tasting)
for a total period of time not to exceed 720
hours; or
C)
Such waste may be burned
if the Agency has
documentation to show that,
prior to August 21,
1991:
i)
The BIT was operating under the interim status
standards
for
incinerators
or
thermal
treatment
units,
35
Ill.
Adm. Code 725.Subparts 0 or P;
and
ii)
The
BIF
met the interim status eligibility
requirements under 35 Ill.
Adm.
Code 703.153 for
35 Ill.
Adm.
Code 725.Subparts 0 or P;
and
iii)
Hazardous
waste
with
a
heating
value
less
than
5,000 Btu/lb was burned prior to that date;
or
D)
Such waste may be burned in a halogen acid furnace if
the waste was burned as
an excluded ingredient under
35 Ill. Adm. Code 721.102(e) prior to February 21,
1991,
and documentation is kept on file supporting
this claim.
7)
Direct transfer to the burner.
If hazardous waste is
directly transferred from a transport vehicle to a BIT
without the use of
a storage unit,
the owner or operator
shall comply with Section 726.211.
b)
Certification of precompliance.
1)
The Board incorporates by reference 40 CFR 266.103(b)(1992)
;
amended
at
57
Fed.
Req.
38564, August 25,
1992.
This
Section
incorporates
no
later
editions
or
amendments.
2)
Certain
owners
and
operators were required to file a
certification of precompliance with U3,S~.EPAby August 21,
1991,
pursuant to 40 CFR 266.103(b).
No separate filing
is
required with the Agency.
c)
Certification of compliance.
The owner or operator shall conduct
emissions testing to document compliance with the emissions
standards of Sections 726.204(b)
through
(e),
726.205,
726.206,
726.207, and subsection
(a) (5) (A) (iv),- above,- under the procedures
prescribed by this subsection, except under extensions of time
provided by subsection
(c)(7),- below.
Based on the compliance
test,
the owner or operator shall submit to the Agency, on or
before August 21,
1992,
a complete and accurate “certification of
compliance”
(under subsection
(c)(4),- below)
with those emission
standards establishing limits on the operating parameters
specified in subsection
(c)(1),- below.
1)
Limits on operating conditions.
The owner or operator shall
establish
limits
on
the
following
parameters
based on
49
operations
during
the
compliance
test
(under
procedures
prescribed
in Bubsection
(c)(4)(D),- below)
or as otherwise
specified and include these limits
with
the
certification
of
compliance.
The BIF must be operated
in accordance with
these operating limits and the applicable emissions
standards of Section 726.204(b) through
(a),
726.205,
726.206,
726.207 and subsection (a)(S)(A)(iv),-
above,
at all
times when there
is
hazardous
waste
in
the
unit.
A)
Feed rate
of total hazardous waste and
(unless
complying
the
Tier
I or adjusted Tier
I metals feed
rate
screening
limits
under
Section
726.206(b)
or
(e)), pumpable hazardous waste;
B)
Feed rate of each metal in the following feedstreams:
i)
Total feedstreams, except that industrial
furnaces that must comply with the alternative
metals implementation approach under subsection
(c)(3)(B), below, must specify limits on the
concentration
of
each metal in collected PM in
lieu of feed rate limits for total feedstreams;
and facilities that comply with Tier I or
Adjusted Tier
I metals feed rate screening
limits
may
8et
their
operating
limits
at
the
metal
feed
rate
screening
limits
determined
under subsection
726.206(b)
or
(e).
BOARD
NOTE:
Federal subsections
266.103(c)(1)(ii)(A)(1) and (c~(1)(iiI(A)(2) are
condensed into the above subsection.
ii)
Total hazardous waste feed (unless complying
with
the
Tier
I
or
adjusted
Tier
I
metals
feed
rate screening limits under Section 726.206(b)
or
(e)); and
iii)
Total
pumpable
hazardous
waste
feed
(unless
complying
with
Tier
I
or
Adjusted
Tier
I
metals
feed
rate
screening
limits
under
subsection
726.206
(b)
or
(e)).
C)
Total
feed
rate
of
total
chlorine
and chloride in
total
feed
streams,
except
that
facilities
that
comply
with
Tier
I
or
Adjusted
Tier
I
feed
rate
screening
limits may
set their operating limits at the total
chlorine
and chloride feed rate screening limits
determined under subsection 726.207(b)(1)
or
(e);
D)
Total
feed
rate
of
ash
in
total
feed streams, except
that
the
ash
feed
rate
for
cement
kilns
and
light-
weight aggregate kilne is
not
limited;
E)
CO concentration,
and where required,
MC concentration
in stack gas.
When complying with the CO controls oc
Section
726.204(b),
the
CO
limit
is
100
ppmv,
and
when
complying
with
the
HC
controls
of Section 726.204(0),
the
HC
limit
is
20
ppmv.
When
complying
with
the
co
controls
of
Section
726.204(c),
the
CO
limit
is
established
based
on
the
compliance
test;
F)
Maximum
production
rate
of
the
device
in
appropriate
50
unita when producing normal product unless complying
with
Tier
I or Adjusted Tier
I feed rate
screening
limits for chlorine under subsection 726.207(b)(1)
or
(e)
and
for
all
metals under subsection 726.207(b)
or
(e),
and
the
uncontrolled
particulate
emissions
do
not
exceed the standard under subsection 726.205;
G)
Maximum
combustion
chamber temperature where the
temperature measurement
is as close to the combustion
zone as possible and is upstream of any quench water
injection,
(unless complying with the Tier
I adjusted
Tier
I metals feed rate screening limits under Section
726.206(b)
or
(e));
H)
Maximum
flue gas temperature entering a PM control
device (unless complying with Tier
I or adjusted Tier
I metals feed rate screening limits under Section
726.206(b) or
(e));
I)
For systems using wet scrubbers, including wet
ionizing scrubbers
(unless complying with the Tier
I
or
adjusted
Tier
I metals feed rate screening limits
under
Section
726.206(b)
or
(e)
and the total chlorine
and
chloride
feed
rate
screening
limits
under
Section
726.207(b)(1) or
(e)):
i)
Minimum liquid to flue gas ratio;
ii)
Minimum scrubber blowdown from the system or
maximum suspended solids content of scrubber
water; and
iii)
Minimum pH level of the scrubber water;
J)
For systems using venturi scrubbers, the minimum
differential gas pressure across the venturi
(unless
complying
the
Tier
I
or
adjusted
Tier
I
metals
feed
rate
screening
limits
under
Section
726.206(b)
or
(e)
and
the
total
chlorine
and
chloride
feed
rate
screening
limits
under
Section
726.207(b)(l)
or
(e));
K)
For
systems
using dry scrubbers (unless complying with
the
Tier
I
or
adjusted
Tier
I
metals
feed
rate
screening
limits
under
Section
726.206(b)
or
(e)
and
the total chlorine and chloride feed rate screening
limits under Section 726.207(b)(1) or
(e)):
i)
Minimum caustic feed rate; and
ii)
Maximum
flue gas flow rate:
L)
For systems using wet ionizing scrubbers or
electrostatic
precipitators
(unless
complying
with
the
Tier
I
or adjusted Tier
I
metals feed rate screening
limits
under
Section
726.206(b)
or
(e)
and
the
total
chlorine and chloride feed rate screening limits under
Section 726.207(b)(1) or
(e)):
i)
Minimum
electrical
power
in
kVA
to
the
precipitator
plates;
and
ii)
Maximum
flue
gas
flow
rater
51
M)
For systems using fabric filters (baghouses),
the
minimum pressure drop (unless complying with the Tier
I or adjusted Tier
I metals feed rate screening limits
under Section 726.206(b) or
(e)
and the total chlorine
and chloride feed rate screening limits under Section
726.207(b) (1) or
(e)).
2)
Prior notice of compliance testing.
At least 30 days prior
to the compliance testing required by subsection
(c)(3),-
below,
the owner or operator shall notify the Agency and
submit the following information:
A)
General facility information including:
i)
U~S.~EPAfacility ID number;
ii)
Facility name, contact person, telephone number
and address;
iii)
Person responsible for conducting compliance
test,
including company name,
address and
telephone number, and a statement of
qualifications;
iv)
Planned date of the compliance test;
B)
Specific information on each device to be tested
including:
i)
~Description
of BIT;
ii)
A scaled plot plan showing the entire facility
and location of the SIP;
iii)
A description of the
APCS;
iv)
Identification of the continuous emission
monitors
that
are
installed,
including:
CO
monitor; Oxygen monitor; NC monitor,
specifying
the minimum temperature
of the system
and,
if
the temperature is
less than 150—°_C,an
explanation of why a heated system is not used
(see subsection
(c)(5)-,-
below)
and a brief
description
of
the
sample
gas
conditioning
system;
v)
Indication
of
whether
the
stack is
shared with
another device that will be in
operation
during
the compliance test;
vi)
Other information useful to an understanding of
the system design or operation.
C)
Information
on the testing planned,
including a
complete copy of the test protocol and QA/QC plan,
and
a su~ary description for each test providing the
following information at
a minimum:
i)
Purpose of the test
(e.g., demonstrate
compliance with emissions of PM); and
ii)
Planned
operating
conditions,
including
levels
52
for each pertinent parameter specified in
subsection
(C)(1)-j-
above.
3)
Compliance testing.
A)
General.
Compliance testing must be conducted under
conditions
for which the
owner
or
operator
has
submitted a certification of precompliance under
subsection
(b),-
above,-
and under conditions
established in the notification of compliance testing
required by subsection
(c)(2)-,- above.
The owner or
operator
may
seek
approval on
a case-by—case basis to
use compliance test data from one unit in lieu of
testing a similar on-site unit.
To support the
request, the owner or operator shall provide a
comparison of the hazardous waste burned and other
feedstreams,
and the design, operation,
and
maintenance of both the tested unit and the similar
unit.
The Agency shall provide
a written approval to
use compliance test data in lieu of testing a similar
unit if the Agency finds that the hazardous wastes,
devices and the operating conditions are sufficiently
similar, and the data from the other compliance test
is adequate to meet the requirements of this
subsection
(c).
B)
Special requirements far industrial furnaces that
recycle collected PM.
Owners
and operators of
industrial furnaces that recycle back into the furnace
PM from the APCS shall comply with one of the
following procedures for testing to determine
compliance with the metals standards of Section
726.206(c)
or
(d):
i)
The special testing requirements prescribed
in
“Alternative Method for Implementing Metals
Controls”
in
Section
726.Appendix
I
(“aye”)
or
ii)
Stack emissions testing for a minimum of
6
hours
each day while hazardous waste is burned during
interim status.
The testing must be conducted
when burning normal hazardous waste for that day
at normal feed rates for that day and when the
APCS is operated under normal conditionB.
During interim status, hazardous waste analysis
for metals content must be sufficient for the
owner or operator to determine if changes in
metals
content
affect
the
ability
of
the
unit
to
meet the metals emissions standards established
under Section 726.206(c)
or
(d).
Under this
option, operating limits
(under subsection
(c)(1),- above)
must be established during
compliance testing under this subsection (c)(3)
only on the following parameters: Feed rate of
total hazardous waste;
Total feed rate of total
chlorine and chloride in total feed streams;
Total feed rate of ash
in total feed streams,
except that the ash feed rate for cement kilns
and light—weight aggregate kilns
is not limited;
CO concentration, and where required,
MC
concentration
in stack gas; Maximum production
rate of the device in appropriate units when
53
producing normal product; or
iii)
Conduct compliance testing to determine
compliance with the metals standards to
establish limits on the operating parameters of
subsection
(c)(1)-r above-,- only after the kiln
system has bean conditioned
to enable it to
reach equilibrium with respect to metals fed
into the system and metals emissions.
During
conditioning,
hazardous waste and raw materials
having the same metals content as will be fed
during the compliance test must be
fad at the
feed rates that will be fed during the
compliance test.
C)
Conduct of compliance testing.
i)
If compliance with all applicable emissions
standards of Sections 726.204 through 726.207
is
not demonstrated simultaneously during a set of
test runs,
the operating conditions of
additional test runs required to demonstrate
compliance with remaining emissions standards
must be as close as
possible
to
the
original
operating conditions.
ii)
Prior
to
obtaining
test
data for purposes of
demonstrating compliance with the applicable
emissions standards of Sections 726.204 through
726.207 or establishing limits on operating
parameters under this Section, the facility must
operate under compliance test conditions for a
sufficient period to reach steady—state
operations.
Industrial furnaces that recycle
collected PM back into the furnace and that
comply with subsections
(c)(3)(B)(i)
or
(c~(3(B~(ii),-above,
however, need not reach
steady
state
conditions
with
respect
to
the
flow
of metals in the system prior to beginning
compliance testing for metals.
iii)
Compliance test data
on
the
level
of
an
operating parameter
for
which a limit must be
established in the certification of compliance
must be obtained during emissions sampling for
the pollutant(s)
(i.e.,
metals,
PM, HCl/chlorine
gas,
organic
compounds)
for
which
the
parameter
must be established as specified by subsection
(c)(1),- above.
4)
Certification of compliance.
Within 90 days of completing
compliance tasting,
the owner or operator shall certify to
the Agency compliance with the emissions standards of
Sections 726.204(b),
(C)
and
(e),
726.205,
726.206,
726.207,
and subsection
(a)(5).(A)(iv)-,- above.
The certification of
compliance must include the following information:
A)
General facility and testing information including:
i)
U~S~EPAfacility ID number;
ii)
Facility
name,
contact
person,
telephone
number
54
and address;
iii)
Person responsible for conducting compliance
testing,
including company name,
addreBs and
telephone number,
and a statement of
qualifications;
iv)
Date(s) of each compliance test;
v)
Description of BIT tested;
vi)
Parson responsible for QA/QC, title and
telephone number,
and statement that procedures
prescribed in the QA/QC plan submitted under
Section 726.203(c)(2)(C) have been followed, or
a description of any changes and an explanation
of why changes were necessary.
vii)
Description of any changes in the unit
configuration prior to or during testing that
would alter any of the information
submitted in
the prior notice of compliance testing under
subsection
(c)(2)-,- above, and an explanation of
why the changes were necessary;
viii) Description of any changes in the planned test
conditions
prior
to
or
during
the
testing
that
alter any of the information submitted in the
prior notice of compliance testing under
subsection
(c)(2)-y- above, and an explanation of
why the changes were necessary;
and
ix)
The complete report on results of emissions
testing.
B)
Specific
information
on
each
test
including:
i)
Purpose(s)
of
test
(e.g.,
demonstrate
conformance with the emissions
limits
for PM,
metals,
Nd,
chlorine gas and dO)
ii)
Suxmnary
of
test
results
for
each
run
and
for
each test including the following information:
Date of run; Duration of run; Time-weighted
average
and
highest
hourly
rolling
average
Co
level
for each run and for the test;
Highest
hourly rolling average MC level,
if HC
monitoring is required
for
each run and for
the
test;
If dioxin and furan testing is required
under Section 726.204(e), time—weighted average
emissions for each run and for the test of
chlorinated dioxin and furan emissions, and the
predicted maximum annual average ground level
concentration of the toxicity equivalency factor
(defined in Section 726.200(g)); Time—weighted
average
PM emissions for each run and for the
test;
Time-weighted average Nd
and chlorine gas
emissions for each run and for the test; Time-
weighted average emissions for the metals
subject to regulation under Section 726.206 for
each run and for the test; and QA/QC results.
55
C)
Comparison of the actual emissions during each test
with the emissions limits prescribed by Sections
726.204(b),
(c)
and
(e),
726.205,
726.206 and 726.207
and established for the facility in the certification
of precompliance under subsection
(b),- above.
D)
Determination of operating limits based on all valid
runs
of the compliance test for each applicable
parameter listed in subsection
(c)(1),- above, using
either of the following procedures:
i)
Instantaneous limits.
A parameter must be
measured
and
recorded
on an instantaneous
basis
(i.e., the value that occurs at any time)
and
the operating limit specified as the time-
weighted average during all runs of the
compliance test; or
ii)
Hourly rolling average basis.
The limit for a
parameter must be established and continuously
monitored on an hourly rolling average basis, as
defined in Section 726.200(g).
The operating
limit for the parameter must be established
based on compliance test data as the average
over
all
test runs of the highest hourly rolling
average value for each run.
iii)
Rolling average limits for carcinogenic metals
and lead.
Feed rate limits for the carcinogenic
metals and lead must be established either on an
hourly rolling average basis as prescribed by
subsection
(C)
(4)(D) (ii), above,, or on (up to)
a
24 hour rolling average basis.
If the owner or
operator elects to use an averaging period from
2 to 24 hours: The feed rate of each metal must
be limited at any time
to
ten times the feed
rate that would be allowed on a hourly rolling
average basis; The continuous monitor
is as
defined in Section 726.200(g).
And the
operating limit for the feed rate of each metal
must be established based on compliance test
data as the average over all test runs of the
highest hourly rolling average feed rate for
each
run.
iv)
Peed rate limits for metals, total chlorine and
chloride and ash.
Feed rate limits for metals,
total chlorine and chloride and ash are
established and monitored by knowing the
concentration of the substance
(i.e., metals,
chloride/chlorine and ash)
in each feadstream
and the flow rate of the feedstream.
To monitor
the feed rate of these substances, the flow rate
of each feedetream must be monitored under the
continuous monitoring requirements of
subsections
(c)(4)(D)(i) through (c~(4)(D~(iii),-
above.
E)
Certification of compliance statement.
The following
statement must
accompany
the certification of
compliance:
56
“I certify under penalty of law that this
information was prepared under my direction or
supervision in accordance with a system designed
to ensure that qualified personnel properly
gathered and evaluated the information and
supporting documentation.
Copies of all
emissions
tests,
dispersion
modeling
results
and
other information used to determine conformance
with
the
requirements
of
35
Ill.
Mm.
Code
726.203(c)
are available at the facility and can
be obtained from the facility contact person
listed above.
Based on my inquiry of the person
or persons who manage. the facility, or those
persona
directly
responsible
for
gathering
the
information, the information submitted is, to
the best of my knowledge and belief,
true,
accurate and complete.
I am aware that there
are
significant penalties for submitting false
information, including the possibility of fine
and imprisonment for knowing violations.
I
also
acknowledge
that
the
operating
limits
established pursuant to 35 Ill. Adm. Code
726.203(c) (4) (D) are enforceable limits at which
the facility can legally operate during interim
status until a revised certification of
compliance is submitted.”
5)
Special
requirements
for
NC
monitoring
systems.
When
an
owner
or
operator
is
required to comply with the HC controls
provided by Sections 726.204(c)
or
subsection
(a) (5)
(A)(iv)-,-
above,
a conditioned gas monitoring system may be used in
conformance with specifications provided in Section
726.Appendix
I
(“cyc”)- provided
that
the
owner
or
operator
submits a certification of compliance without using
extensions of time provided by subBection
(c)(7),- below.
However, owners or operators of facilities electing to
comply
with the alternative hydrocarbon provision of Section
726.204(f) and requesting a time extension under Section
726.219(b)
may
establish the baseline HC level and comply
with the interim
MC
limit
established
by
the
time
extension
using
a conditioned gaa monitoring system if the Board
determines that the owner or operator has also demonstrated
a
good
faith
effort
to
operate
a
heated
monitoring
system
but
found
it
to
be
impracticable.
6)
Special operating requirements for industrial
furnaces that
recycle collected PM.
Owners and operators of industrial
furnaces that recycle back into the furnace PM from the APCs
must:
A)
When complying with the requirements of subsection
(c)(3)(B)(i),- above, comply with the operating
requirements
prescribed
in
“Alternative
Method
to
Implement the Metals Controls” in Section 726.Appendix
I
(“aye”)
and
B)
When complying with the requirements of subsection
(c) (3) (B) (ii), above,
comply with the operating
requirements
prescribed
by
that
subsection.
7)
Extensions
of
time.
57
A)
If the owner or operator does not submit
a complete
certification of compliance for all of the applicable
emissions
standards
of
Sections
726.204,
726.205,
726.206 and 726.207
by
August
21,
1992,
the owner or
operator shall either:
i)
Stop burning hazardous waste and begin closure
activities under subsection
(1)-,- below,
for the
hazardous waste portion of the facility; or
ii)
Limit hazardous waste burning only for purposes
of compliance testing
(and pretesting to prepare
for compliance testing)
a total period of 720
hours for the period of time beginning August
21,
1992,
submit
a notification to the Agency by
August
21,
1992
stating that the facility is
operating
under
restricted interim status and
intends
to
resume
burning
hazardous waste,
and
submit
a
complete
certification
of
compliance
by
August 23,
1993;
or
iii)
Obtain a case—by—case extension of time under
subsection
(c)(7)(B).,- below.
B)
Case—by—case extensions of time.
See Section 726.219.
8)
Revised certification of compliance.
The owner or operator
may submit at any time a revised certification of compliance
(recertification of compliance) under the following
procedures:
A)
Prior to submittal of
a revised certification of
compliance, hazardous waste must not be burned for
more than a total of 720 hours under operating
conditions that exceed those established under
a
current
certification
of
compliance,
and
such
burning
must be conducted only for purposes of determining
whether
the
facility
can
operate
under
revised
conditions
and
continue
to
meet
the
applicable
emissions standards of Sections 726.204,
726.205,
726.206
and
726.207;
B)
At
least 30 days prior to
first burning hazardous
waste under operating conditions that exceed those
established
under
a
current
certification
of
compliance, the owner or operator shall notify the
Agency and submit the following information:
i)
U~,S~EPAfacility
ID
number,
and facility name,
contact person, telephone number and address;
ii)
Operating conditions that the owner or operator
is seeking to revise and description of the
changes in facility design or operation that
prompted the need to seek to revise the
operating
conditions;
iii)
A
determination
that,
when
operating
under
the
revised
operating
conditions,
the
applicable
emissions
standard8
of
Sections
726.204,
726.205,
726.206 and 726.207 are not likely to
be
exceeded.
To
document
this
determination,
58
the owner or operator shall submit the
applicable information required under subsection
(b)(2).,. above;
and
iv)
Complete emissions testing protocol for any
pretesting and for a new compliance test to
determine compliance with the applicable
emissions standards of Sections 726.204,
726.205,
726.206 and 726.207 when operating
under revised operating conditions.
The
protocol shall include a schedule of pre~tast3.ng
and compliance testing.
If the owner or
operator revises the scheduled date for the
compliance test,
the owner or operator shall
notify the Agency in writing at least 30 days
prior to the revised date of the compliance
test;
C)
Conduct a compliance test under the revised operating
conditions and the protocol submitted to the Agency to
determine compliance with the applicable emissions
standards of Sections 726.204,
726.205,
726.206 and
726.207;
and
D)
Submit
a revised certification of compliance under
subsection
(c)(4)’,- above.
d)
Periodic Recertifications.
The owner or operator shall conduct
compliance testing and submit to the Agency a recertification of
compliance under provisions of subsection
(c),. above,- within three
years from submitting the previous certification or
recertification.
If the owner or operator seeks to racertify
compliance under new operating conditions, the owner or operator
shall comply with the requirements of subsection
(c)(8),- above.
e)
Noncompliance with certification schedule.
If the owner or
operator
does
not
comply
with
the
interim
status
compliance
schedule provided by subsections
(b),
(C)
and (d)r above,
hazardous waste burning must terminate on the date that the
deadline is missed, closure activities must begin under subsection
(1)’,, below, and hazardous waste burning must not resume except
under an operating permit issued under 35 Ill.
Adm.
Code 703.232.
For purposes of compliance with the closure provisions of
subsection
(1),- below-, and 35 Ill. Mm. Code 725.212(d) (2) and
725.2l3~,the BIT has received “the known final volume of hazardous
waste” on the date the deadline
is missed.
f)
Start-up and shut—down.
Hazardous waste
(except waste fed solely
as an ingredient under the Tier
I
(or adjusted Tier
I)
feed rate
screening limits for metals and chloride/chlorine) must not be
fed
into the device during start-up and shut—down of the BIT, unless
the
device
is
operating
within
the
conditions
of
operation
specified in the certification of compliance.
9)
Automatic waste feed cutoff.
During the compliance teat required
by subsection
(c)(3),-
above,-
and upon certification of compliance
under subsection
(C),- above,
a BIT must be operated with a
functioning system that automatically cuts
off
the
hazardous
waste
feed when the applicable operating conditions specified in
subsections
(c)(l)(A) and (c~(11’(E)through (c~(11(M)rabove.,-
deviate from those established
in the certification of compliance.
In
addition:
59
1)
To
minimize
emissions
of
organic
compounds,
the
minimum
combustion chamber
temperature
(or
the
indicator
of
combustion
chamber
temperature)
that
occurred
during
the
compliance
test
must be maintained while hazardous waste or
hazardous waste residues remain in the combustion chamber,
with
the
minimum temperature during the compliance test
defined as either:
A)
If compliance with the combustion chamber temperature
limit
is based on a hourly rolling average, the
minimum temperature during the compliance test is
considered to be the average over all runs of the
lowest hourly rolling average for each run; or
B)
If compliance with the combustion chamber temperature
limit is based on an instantaneous temperature
measurement, the minimum temperature during the
compliance test is considered to be the time-weighted
average temperature during all runs of the test; and
2)
Operating parameters limited by the certification of
compliance must continue to be monitored during the cutoff,
and the hazardous waste feed must not be restarted until the
levels of those parameters comply with the limits
established in the certification of compliance.
h)
Fugitive emissions.
Fugitive emissions must be controlled by:
1)
Keeping the combustion zone totally sealed against fugitive
emissions;
or
2)
Maintaining the combustion zone pressure lower than
atmospheric pressure;
or
3)
An alternate means of control that the owner or operator
demonstrates provides fugitive emissions control equivalent
to maintenance of combustion
zone pressure lower than
atmospheric pressure.
Support for such demonstration must
be included in the operating record.
i)
Changes.
A BIT must cease burning hazardous waste when combustion
properties,
or feed rates of the hazardous waste, other fuels or
industrial furnace feedstocks,
or the BIT design or operating
conditions
deviate
from
the
limits specified in the certification
of compliance.
j)
Monitoring
and
Inspections.
1)
The owner or operator shall monitor and record the
following,
at
a
minimum,
while burning hazardous waate:
A)
Feed
rates
and
composition
of
hazardous
waste,
other
fuels and industrial furnace feed stocks,
and feed
rates of ash, metals, and total chlorine and chloride
as
necessary
to
ensure
conformance
with
the
certification
of precompliance or certification of
compliance;
B)
CO, oxygen and,
if applicable,
Hd, on a continuous
basis at
a common point
in the BIF downstream of the
combustion zone and prior to release of stack gases to
the
atmosphere
in
accordance
with
the
operating
limits
60
specified in the certification of compliance.
CO, MC
and oxygen monitors must be installed,
operated and
maintained in accordance with methods specified in
Section 726.Appendix
I (“eye”).
C)
Upon the request of the Agency, sampling and analysis
of the hazardous waste
(and other fuels and industrial
furnace feed stocks
as
appropriate) and th. stack gas
emissions
must be conducted to verify that the
operating conditions established
in the certification
of precompliance or certification of compliance
achieve the applicable standards of Sections 726.204,
726.205, 726.206 and 726.207.
2)
The BIT and associated equipment (pumps,
valves, pipes,
fuel
storage tanks,
etc.) must be subjected to thorough visual
inspection when they contain hazardous waste, at least daily
for leaks, spills,
fugitive emissions and signs of
tampering.
3)
The automatic hazardous waste feed cutoff system and
associated
alarms
must be tested at least once every
7 days
when hazardous waste is burned to verify operability, unless
the owner or operator can demonstrate that weekly
inspections will unduly restrict or upset operations and
that less frequent inspections will be adequate.
Support
for such demonstration must be included in the operating
record.
At a minimum, operational testing must be conducted
at least once every 30 days.
4)
These monitoring and
inspection
data
must
be
recorded
and
the records must be placed in the operating log.
k)
Recordkeeping.
The owner or operator shall keep in the operating
record of the facility all information and data required by this
Section until closure of the BIT unit.
1)
Closure.
At closure, the owner or operator shall remove all
hazardous waste and hazardous waste residues
(including, but not
limited to, ash, scrubber waters and scrubber sludges)
from the
BIT and shall comply with 35 Ill. Adm. Code 725.211 through
725.215.
(Source:
Amended at
ia
Ill.
Reg.
_________,
effective
_____________________
Section
726.204
Standards
to
e~ontrol
Organic
Emissions
a)
DRE standard.
1)
General.
Except
as
provided
in
subsection
(a)(3)r
below,
a
BIT
burning
hazardous
waste
must
achieve
a
DRE
of
99.99
for
all organic hazardous constituents
in the waste feed.
To
demonstrate conformance with this requirement, 99.99
DR.E
must be demonstrated during a trial burn for each principal
organic hazardous constituent
(POHC) designated
(under
subsection
(a)(2),- below)
in its permit for each waste feed.
DRE is determined for each PONC from the following equation:
DRE
100(1
—
0)/I
where:
61
I
=
Mass feed rate of one POHC in the hazardous waste fired
to
the
BIF;
and
0
Mass emission rate of the same POHC present in stack gas
prior to release to the atmosphere.
2)
Designation of POHCs.
POHCs are those compounds for which
compliance with the DRE requirements of this Section must be
demonstrated in a trial burn in conformance with procedures
prescribed
in
35
Ill.
Adm.
Code
703.232.
One
or
more POHCs
must
be
designated
by
the
Agency
for
each
waste
feed
to
be
burned.
POEC5
must
be
designated
based
on
the
degree
of
difficulty of destruction of the organic constituents in the
waste and on their concentrations or mass in the waste feed
considering the results of waste analyses submitted with
Part B of the permit application.
PONds are most likely to
be selected from among those compounds listed in 35
Ill.
Adm.
Code 721.Appendix H that are also present in the normal
waste
feed.
However,
if
the
applicant
demonstrates
to
the
Agency that a compound not listed in 35 Ill. Adm. Code
72l.Appendix
H
or
not
present in the normal waste feed is a
suitable
indicator
of
compliance
with
the
DRE
requirements
of
this
Section,
that
compound
must
be
designated
as
a
POHC.
Such PONds need not be toxic or organic compounds.
3)
Dioxin-listed waste.
A BIT burning hazardous waste
containing
(or derived from)
U.~S,~,EPAHazardous Wastes Nos.
P020,
P021,
P022,
F023,
P026 or
P027
must achieve a
destruction and removal efficiency
(DRE) of 99.9999
for
each POHC designated
(under subsection
(a)(2),- above)
in its
permit.
This
performance must be demonstrated on POHC5 that
are
more
difficult
to
burn than tetra-, penta- and
hexachlorodibenzo—p—dioxina and dibenzofurans.
DRE
is
determined
for
each
POHC
from
the
equation
in
subsection
(a)(l),
above.
In
addition,
the
owner
or
operator
of
the
BIT
shall
notify
the
Agency of intent to burn U~,S~EPA
Hazardous
Waste
Nos.
P020,
F021,
P022,
P023,
P026
or
F027.
4)
Automatic
waiver
of
DRE
trial
burn.
Owners
and
operators
of
boilers
operated
under
the
special
operating
requirements
provided
by
Section
726.210
are
considered
to
be
in
compliance
with
the
DRE
standard
of
subsection
(a)(l),
above,
and
are
exempt from the DRE
trial
burn.
5)
Low
risk
waste.
Owners
and
operators
of
BITs
that
burn
hazardous
waste
in
compliance
with
the
requirements
of
Section 726.209(a) are considered to be in compliance with
the
DRE
standard
of
subsection
(a)(1)-,-
above,
and
are
exempt
from
the
DRE
trial
burn.
b)
CO
standard.
1)
Except
as provided in subsection
(c)-r below, the stack gas
concentration
of
CO
from
a
BIT
burning
hazardous
waste
cannot
exceed
100
ppmv
on
an
hourly rolling average basis
(i.e.,
over
any
60
minute period), continuously corrected to
7 percent oxygen,
dry gas basis.
2)
CO
and
oxygen
must
be
continuously
monitored
in
conformance
with
“Performance
Specifications
for
Continuous
Emission
Monitoring
of
Carbon
Monoxide and Oxygen for Incinerators,
Boilers,
and
Industrial
Furnaces
Burning
Hazardous
Waste”
in
62
Section 726.Appendix I (“cyc”).
3)
Compliance with the 100 ppmv CO
limit
must be demonstrated
during
the
trial
burn
(for
new
facilities
or
an
interim
status
facility applying for
a permit)
or
the
compliance
teat (for interim status facilities).
To demonstrate
compliance, the highest hourly rolling average CO level
during
any valid run of the trial burn or compliance test
must
not
exceed
100
ppcnv.
C)
Alternative CO standard.
1)
The
stack
gas
concentration
of
CO
from
a
BIT
burning
hazardous
waste
may
exceed
the
100
ppcnv
limit
provided
that
stack gas concentrations of HCs do not exceed 20 ppmv,
except as provided by subsection
(f), below, for certain
industrial furnaces.
2)
MC limits must be established under this Section on an
hourly rolling average basis (i.e., over any 60 minute
period),
reported
as
propane,
and
continuously
corrected
to
7 percent oxygen,
dry gas basis.
3)
MC
must
be
continuously
monitored
in conformance with
“Performance Specifications for Continuous Emission
Monitoring of Hydrocarbons
for
Incinerators,
Boilers, and
Industrial Furnaces Burning Hazardous Waste” in Section
726.Appendix
I
(“oyo”).
CO
and
oxygen must be continuously
monitored
in
conformance
with
subsection
(b)(2),
above.
4)
The alternative CO standard is established based on CO data
during
the
trial
burn
(for
a
new
facility)
and
the
compliance
test
(for
an
interim
status
facility).
The
alternative Co standard is the average over all valid runs
of the highest hourly average CO level for each run.
The dO
limit
is
implemented
on
an
hourly
rolling
average
basis,
and
continuously
corrected
to
7
percent
oxygen,
dry
gas
basis.
d)
Special requirements for furnaces.
Owners and operators of
industrial furnaces
(e.g.,
kilns,
cupolas) that feed hazardous
waste for a purpose other than solely as an ingredient
(see
Section
726.203(a)(5)(B))
at any location other than the end where
products
are
normally
discharged
and
where
fuels are normally
fired must comply with the HC limits
provided
by
subsections
(c),
above,
or
(f), below, irrespective of whether stack gas CO
concentrations
meet
the
100
ppmv limit of subsection
(b)-,- above.
e)
Controls for dioxins and furanB.
Owners and operators of BIFs
that are equipped with a dry PM control device that operates
within
the
temperature
range
of
450
through 750—°_F,
and
industrial
furnaces
operating
under
an
alternative
NC
limit
established under subsection
(f),-
below,
shall
conduct
a site-
specific risk assessment as follows to demonstrate that emissions
of chlorinated dibenzo—p—dioxins and dibenzofurans do not result
in an increased lifetime cancer risk to the hrothetical maximum
exposed
individual
(MEl)
exceeding
1E-0~1X10
(1
in
100,000):
1)
During
the
trial
burn
(for
new
facilities
or
an
interim
status
facility
applying
for
a
permit)
or
compliance
test
(for interim status
facilities), determine emission rates of
the
tetra—octa
congeners
of
chlorinated
dibenzo—p—dioxins
63
(PCDD5)
and dibenzofurans (CDDs/CDFB) using Method 23,
“Determination of Polychlorinated Dibenzo—p-Dioxins and
Polychlorinated Dibenzofurans
(PCDFa) from Stationary
Sources”,
in Section 726.Appendix I (“oyo”)
2)
Estimate the 2,3,7,8-TCDD toxicity equivalence of the tetra-
octa CDD5/CDF5 congeners using “Procedures
for
Estimating
the Toxicity Equivalence of Chlorinated Dibenzo-p—Dioxin and
Dibenzofuran Congeners” in Section 726.Appendix I
(“cyc”).
Multiply
the
emission
rates of CDD/CDF congeners with a
toxicity equivalence greater than zero (see the procedure)
by
the
calculated
toxicity
equivalence
factor
to
estimate
the
equivalent
emission
rate
of
2,3,7,8—TCDD;
3)
Conduct dispersion modeling using methods recommended in
~Q
CPR
51,
Appendix
W,
as incornorated by reference at 35
Ill.
Adm. Code 720.111 (“Guideline
on
Air
Quality
Models
(Revised)”
11986~ and its sup~lementsL.e*the “Hazardous
Waste Combustion Air Quality Screening Procedure”,
whioh-aI’e
provided
in
Appendieee~ I
and
.7,
roapootivoly,
or
“EPZ~
SCREEN
Lorooning
I’r000dufe”
as
dosoribod
in
Screening
Procedures
for
Estimating
Air Quality Impact of Stationary
Sources, Revised”
(incorporated by reference in 35
Ill.
Adm.
Code 720.111) to predict the maximum annual average off—site
ground
level
concentration
of
2,3,7,8-TCDD
equivalents
determined under subsection (e)(2), above.
The maximum
annual average on—site concentration must be used when a
person resides on—site;
and
4)
The
ratio
of
the
predicted
maximum annual average ground
level concentration of 2,3,7,8—TCDD equivalents to the risk—
specific
dose
(RED)
for
2,3,7,8—TdDD
provided
in
Section
726.Appendix
E
(2.2E-07X10~’)
must
not
exceed
1.0.
f)
Alternative
MC
limit
for
furnaces
with
organic
matter
in
raw
material.
For industrial furnaces that cannot meet the 20 ppmv
HC
limit
because
of
organic matter in normal raw material, the Agency
shall
establish
an
alternative
NC
limit
on
a
case—by-case
basis
(under
a
Part
B
permit
proceeding)
at
a
level
that
ensures
that
flue
gas
HC
(and
CO)
concentrations
when
burning
hazardous
waste
are not greater than when not burning hazardous waste
(the
baseline Nd level) provided that the owner or operator complies
with
the following requirements.
However, cement kilns equipped
with
a
by-pass
duct meeting the requirements of BubBection (g),
below,
are
not
eligible
for an alternative NC limit.
1)
The
owner
or
operator
shall demonstrate that the facility is
designed and operated to minimize MC emissions from fuels
and raw materials, and that the facility is producing normal
products
under
normal
operating
conditionB
feeding
normal
feedstocks
and
fuels
when
the
baseline
HC
(and
CO)
level
is
determined.
The baseline
NC
level
is
defined
as
the
average
over all valid test runs of the highest hourly rolling
average value for each run when the facility does not burn
hazardous waste,
adjusted as appropriate to consider the
variability
of
hydrocarbon
levels
under
good combustion
operating conditions.
The baseline CO
level
is
determined
based on the test runs used to establish the baseline MC
level and is defined as the average over all test runs of
the highest hourly rolling average
CO
value
for
each
run.
More than one baseline level must be determined
if
the
facility
operates
under
different
modes
that
generate
64
significantly different
MC
(and
CO)
levels;
2)
The owner or operator shall develop an approach to monitor
over time changes in the operation of the facility that
could reduce the baseline NC level;
3)
The
owner
or operator shall conduct emissions testing during
the trial burn to:
A)
Determine the baseline HC (and CO)
level;
B)
Demonstrate
that,
when
hazardous
waste
is
burned,
MC
(and
CO)
levels
do
not
exceed
the
baseline
level;
and
C)
Identify the types
and
concentrations
of
organic
compounds listed in 35
Ill. Adm. Code 721.Appendix H,
that are emitted and conduct dispersion modeling to
predict the maximum annual average ground level
concentration
of
each
organic compound.
On—site
ground
level
concentrations
must
be
considered
for
this evaluation if
a person resides on site.
i)
Sampling and analysis of organic emissions must
be
conducted
using
procedures
prescribed
by
the
Agency
pursuant
to
35
Ill.
Adm.
Code
703.208(a).
ii)
Dispersion modeling must be conducted according
to procedures provided by subsection (e)(2),
above;
and
D)
Demonstrate
that
maximum annual average ground level
concentrations of the organic compounds identified in
subsection (f)(3)(C),- above,
do
not
exceed
the
following
levels:
i)
For
the
noncarcinogenic
compounds
listed
in
Section 726.Appendix D,
the levels established
in
that
Section
726.1~ppcndix D
ii)
For
the carcinogenic compounds listed in Section
726.Appendix E,
the sum for all compounds of the
ratios of the actual ground level concentration
to the level established
in that Section
736.Appondix
E
cannot
exceed
1.0.
To estimate
the health risk from chlorinated dibenzo—p-
dioxins and dibenzofuran congeners, use the
procedures prescribed by subsection
(e)(3),
above,
to
estimate
the 2,3,7,8-TCDD toxicity
equivalence
of
the
congeners.
iii)
For
compounds
not
listed
in
Section 726.Appendix
D
or
726.Appendix
E,
0.1
~g/ei*—rn3
(microarams
~er
cubic
meter~.
4)
All
MC
levels
specified
under
this
subsection
are
to
be
monitored and reported
as
specified
in
subsections
(c)(1)
and ~~j(2), above.
g)
Monitoring CO and NC
in
the
by—pass
duct
of
a
cement
kiln.
Cement
kilne may comply with the CO
and
NC limits provided by subsections
(b),
(c)
and
(d),
above,
by
monitoring
in
the
by—pass
duct
provided
that:
65
1)
Hazardous waste
is fired only into the kiln and
not
at
any
location downstream from the kiln exit relative to the
direction
of
gas
flow;
and
2)
The
by—pass
duct
diverts
a
minimum
of
10
of
kiln
off—gas
into
the
duct.
h)
Use of emissions test data to demonstrate compliance and establish
operating limits.
Compliance with the requirements of this
Section must be demonstrated simultaneously by emissions testing
or during separate runs under identical operating conditions.
I~urther,data to demonstrate compliance with the 00 and MC limits
of
this
Section
or
to
establish alternative CO or NC limits under
this
Section
must be obtained during the time that DRE testing,
and where applicable,
CDD/CDF testing under
subsection
(a)-,- above,
and comprehensive organic emissions testing under subsection
(f).r
above, is conducted.
i)
Enforcement.
For the purposes of permit enforcement, compliance
with the operating requirements specified in the permit (under
Section 726.202) will be regarded as compliance with this Section.
However, evidence that compliance with those permit conditions
is
insufficient to ensure compliance with the requirements of this
Section
is
“information” justifying modification or revocation and
re—issuance of a permit under
35
Ill.
Adm.
Code
703.270
et
seq.
(Source:
Amended
at
18
Ill.
Reg.
,
effective
______________________
Section
726.206
Standards
to
e~ontrol
Metals
Emissions
a)
General.
The owner or operator shall comply with the metals
standards provided by subsections
(b),
(c),
(d),
(e)
or
(f)-,-
below,
for
each
metal
listed
in
subsection
(b),
below,
that
is
present in the hazardous waste at detectable levels using
analytical
procedures
specified
in
Test
Methods
for
Evaluating
Solid Waste, Physical/Chemical Methods.L +SW—846+, incorporated by
reference
in
35
Ill.
Adm. Code 720.111.
b)
Tier
I feed rate screening limits.
Teed rate screening limits
for
metals are specified in Section 726.Appendix A as
a function of
terrain-adjusted effective stack height
(TESN) and terrain and
land use in the vicinity of the facility.
Criteria for facilities
that are not eligible to comply with the screening limits are
provided
in
subsection
(b)(7),
below.
1)
Noncarcinogenic metals.
The feed rates of the
noncarcinogenic metals in all feed streama, including
hazardous waste,
fuels and industrial furnace
feed stocks
must
not
exceed
the
screening
limits specified in Section
726.Appendix A.
A)
The
feed
rate
screening
limits
for
antimony,
barium,
mercury, thallium and silver are based on either:
i)
An hourly rolling average as defined
in Sections
726.200(g)
and
726.202(e)
(6) (A)(ii);
or
ii)
An
instantaneous
limit
not
to
be exceeded at any
time.
B)
The
feed
rate
screening
limit
for
lead
is
based on one
of
the
following:
66
i)
An hourly rolling average as defined in Sections
726.200(g) and 726.202(e) (6) (A)(ii);
ii)
An averaging period of 2
to
24
hours as defined
in Section 726.202(e) (6) (B) with an
instantaneous feed rate limit not to exceed 10
times the feed rate that would be allowed on an
hourly rolling average baBis; or
iii)
An instantaneous limit not to be exceeded at any
time.
2)
Carcinogenic metals.
A)
The
feed
rates
of
carcinogenic
metals
in
all
feed
streams,
including hazardous waste,
fuels and
industrial furnace feed stocks must not exceed values
derived from the screening limits specified in Section
726.Appendix
A.
The
feed
rate of each of these metals
is
limited
to
a
level
such
that
the
sum
of
the
ratios
of the actual feed rate to the feed rate screening
limit specified in Section 726.Appendix A must not
exceed
1.0,
as provided by the following equation:
0
SUH(1~.i/Fi) ~ 1.0
where:
CUM(Xi)E
A../F~means
the
sum
of
the
values
of
X~Jj
for
each metal
“i”,
from i
=
1
to
n.
n
=
number of carcinogenic metals
=
the
actual
feed
rate
to
the
device
for
metal
“i”
F~
=
the
feed
rate
screening
limit
provided by Section 726.Appendix A for
metal
“i”.
B)
The feed rate screening limits for the carcinogenic
metals are based on either:
i)
An hourly rolling average; or
ii)
An averaging period of
2 to 24 hours, as defined
in Section 726.202(e) (6) (B),
with an
instantaneous feed rate limit not to exceed 10
times the feed rate that would be allowed on an
hourly rolling average basis.
3)
TESH
(terrain adjusted effective stack height).
A)
The TESH is determined according to the following
equation:
67
TESH
=
H
+
P
-
T
where:
H
=
Actual
physical
stack
height
(m)
P
=
Plume
rise
(in
m)
as
determined
from
Section 726.Appendix
P
as
a
function
of
stack flow rate and stack gas exhaust
temperature.
T
=
Terrain rise
(in m)
within five
kilometers of the stack.
B)
The stack height
(N) must not exceed good engineering
practice
stack
height,
as
defined
in
Section
726.200(g).
C)
If the TESN calculated pursuant to subsection
(b)(3)(A),
above,
is
not
listed
in
Sections
726.Appendieee~
A
through
726.Anoendix
C,
the values
for
the
nearest
lower
TESH
listed
in
the
table must be
used.
If
the
TESH
is
four
meters or less,
a value
based
on
four
meters
must
be
used.
4)
Terrain
type.
The
screening
limits
are
a
function
of
whether the facility is located in noncomplex or complex
terrain.
A device located where any part of the surrounding
terrain within 5 kilometers of the stack equals or exceeds
the
elevation
of
the
physical
stack
height
(N)
is
considered
to be in complex terrain and the screening limits
for
complex terrain apply.
Terrain measurements are to be made
from
U.S.
Geological
Survey
7.5—minute topographic maps of
the area surrounding the facility.
5)
Land
use.
The
screening
limits
are
a
function
of
whether
the
facility
is
located
in an area where the land use is
urban
or
rural.
To
determine
whether
land
use
in
the
vicinity
of
the
facility
is
urban or rural, procedures
provided
in
Section
726.Appendieee~
I
(“cyc”)
or Section
726.Appendix
J
shall
be
used.
6)
Multiple
stacks.
Owners
and
operators
of
facilities
with
more
than
one
on-site
stack
from
a
BIT,
incinerator
or
other
thermal
treatment
unit
subject
to
controls
of
metals
emissions
under
a
RCRA
permit
or
interim
status
controls
shall comply with the screening limits for all such units
assuming
all
hazardous
waste
is
fed
into
the
device
with
the
worst—case
stack
based
on
dispersion
characteristics.
The
stack
with
the
lowest
value
of
K
is
the
worst—case
stack.
K
is
determined
from
the
following
equation
as
applied
to
each
stack:
K
=
N~ X V~ X
T
Where:
K
=
a
parameter
accounting
for
relative
influence
of
stack
height
and
plume
rise;
H
=
physical
stack
height
(meters);
68
V
=
stack
gas
flow rate (eQ—m~/sec(cubic mete~SL
~er second) and
T
=
exhaust temperature
(degrees K).
7)
Criteria for facilities not eligible for screening limits.
If any criteria below are met, the Tier
I
(and Tier II)
screening limits do not apply.
Owners and operators of such
facilities shall comply with either the Tier III standards
provided by subsection
(d),- below or with the adjusted Tier
I feed rate screening limits provided by subsection
(e)
below.
A)
The device
is
located in a narrow valley less than one
kilometer wide;
B)
The device has a stack taller than 20 meters and is
located such that the terrain rises to the physical
height
within
one
kilometer
of
the
facility;
C)
The device has a stack taller than 20 meters and is
located within five kilometers of
a shoreline of
a
large body of water such as an ocean or large lake;
D)
The physical stack height of any stack is less than
2.5 times the height of any building within five
building heights or five projected building widths of
the stack and the distance from the stack to the
closest boundary is within five building heights or
five projected building widths of the associated
building;
or
8)
Implementation.
The feed rate of metals in each feedatream
must be monitored to ensure that the feed rate screening
limits are not exceeded.
C)
Tier II emission rate screening limits.
Emission rate screening
limits are specified in Section 726.Appendix A as
a function of
TESH and terrain and land use in the vicinity of the facility.
Criteria
for
facilities
that
are
not eligible to comply with the
screening
limits
are
provided
in
subsection
(b)(7),
above.
1)
Noncarcinogenic metals.
The emisBion rates of
noncarcinogenic
metals
must
not
exceed
the
screening
limits
specified in Section 726.Appendix A.
2)
Carcinogenic metals.
The emission rates of carcinogenic
metals
must
not
exceed
values
derived
from
the
screening
limits specified in Section 726.Appendix A.
The emission
rate of each of these metals is limited to
a level such that
the sum of the ratios of the actual emission rate to the
emission rate screening limit specified
in Section
726.Appendix A must not exceed 1.0,
as
provided by the
following
equation:
“A.
~
~Ufl(Ai/Ei)
69
where:
CU~f(Xi)E
A~/E~
means the sum of the values of
~
for each metal “i”,
from i
=
1 to
n.
n
=
number
of carcinogenic metals
=
the actual emission rate to the device for
metal
“i”
=
the emission rate screening limit provided
by Section 726.Appendix A for metal
“i”.
3)
Implementation.
The emission rate limits must be
implemented
by
limiting
feed
rates
of
the
individual
metals
to levels during the trial burn (for new facilities or an
interim status facility applying for a permit) or the
compliance test (for interim status facilities).
The feed
rate averaging periods are the same as provided by
subsections
(b)(1)(A)~
a*~4(b)(1~(B)~and
(b)(2)(B),
above.
The
feed
rate
of
metals
in
each
feedstream
must
be
monitored
to
ensure
that
the
feed
rate
limits
for
the
feedstreams
specified
under
Sections
726.202
or
726.203 are not
exceeded.
4)
Definitions
and
limitations.
The
definitions
and
limitations provided by subsection
(b), above, and
726.200(g)
for the following terms also apply to the Tier II
emission rate screening limits provided by this subsection
(c):
TESH,
good engineering practice stack height,
terrain
type,
land
use
and
criteria
for
facilities
not
eligible
to
use
the
screening
limits.
5)
Multiple
stacks.
A)
Owners
and
operators
of
facilities
with
more
than
one
on—site
stack
from
a
BIT,
incinerator
or
other
thermal
treatment
unit
subject
to
controls
on
metals
emissions
under
a RCRA permit or interim status controls shall
comply
with
the
emissions
screening
limits
for
any
such
stacks
assuming
all
hazardous
waste
is
fed
into
the
device
with
the
worst—case
stack
based
on
dispersion
characteristics.
B)
The worst—case stack is determined by procedures
provided in subsection
(b)(6), above.
C)
For each metal,
the total emissions of the metal from
those
stacks
must
not
exceed
the
screening
limit
for
the
worst—case
stack.
d)
Tier III site—specific risk assessment.
The requirements of this
subsection apply to facilities complying with either the Tier III
or Adjusted Tier
I except where specified otherwise.
1)
General.
Conformance with the Tier III metals controls must
be
demonstrated
by
emissions
testing
to
determine
the
emission
rate
for
each
metal.
In
addition,
conformance
with
either Tier III or Adjusted Tier I metals controls must be
demonstrated
by
air
dispersion
modeling
to
predict
the
maximum annual average off—site ground level concentration
70
for each metal and a demonstration that acceptable ambient
levels are not exceeded.
2)
Acceptable ambient levels.
Sections 726.Appendieee~D and
726.A~tendixE list the acceptable ambient levels for
purposes of this Subpart.
Reference air concentrations
(RAC5)
are listed
for
the noncarcinogenic metals and 1B—
Q&X1O5RSDs are listed
for the carcinogenic metals.
The RSD
for
a metal
is
the
acceptable ambient level for that metal
provided that only one of the four carcinogenic metals
is
emitted.
If more than one carcinogenic metal
is emitted,
the
acceptable ambient level
for
the
carcinogenic metals is
a fraction of the RSD as described in subsection (d)(3),
below.
3)
Carcinogenic metals.
For the carcinogenic metals the sum of
the
ratios
of
the
predicted
maximum annual average off—site
ground
level
concentrations
(except that on—site
concentrations
must
be
considered
if a person resides on
Bite) to the RSD for all carcinogenic metals emitted must
not exceed 1.0 as determined by the following equation:
ftp.
SU14(Pi/Ri) ?l.0
where:
£UH(Xi)E
P~/P.~
means the sum of the values of
~
for each metal
“i”, from
i
=
1
to
n.
n
=
number of carcinogenic metals
=
the pPredicted ambient concentration for
metal
i.
=
the RSD for metal
i.
4)
Noncarcinogenic metals.
For the noncarcinogenic metals, the
predicted maximum annual average off—site ground
level
concentration for each metal must not exceed the RAC.
5)
Multiple stacks.
Owners and operators of facilities with
more than one on—site Btack from a BIF, incinerator or other
thermal treatment unit subject to controls on metals
emissions under a RCRA permit or interim status controls
shall conduct emissions testing (except that facilities
complying with Adjusted Tier I controls need not conduct
emissions testing)
and dispersion modeling to demonstrate
that
the
aggregate emissions from all such on—site stacks do
not result in an exceedance of the acceptable ambient
level8.
6)
Implementation.
Under
Tier
III,
the
metals
controls
must
be
implemented
by
limiting feed rates of the individual metals
to
levels
during
the
trial
burn
(for
new
facilities or an
interim
status
facility
applying
for
a permit) or the
71
compliance
test
(for
interim
status
facilities).
The
feed
rate
averaging
periods
are
the
same
as
provided
by
subsections
(b)(1)(A)~
and
(b~(1~(B).,..and
(b)(2)(B),
above.
The feed rate of metals in each feedstream must be monitored
to
ensure
that
the
feed
rate
limits
for
the
feedatreams
specified
under Sections 726.202 or 726.203 are not
exceeded.
e)
Adjusted Tier
I feed rate screening limits.
The owner or operator
may
adjust
the
feed
rate screening limits provided by Section
726.Appendix
A
to
account
for
site—specific
dispersion
modeling.
Under
this
approach,
the
adjusted feed rate
screening
limit
for
a
metal
is determined by back-calculating from the acceptable
ambient levels provided by Sections 726.Appendieee~D and
726.Anoendix E using dispersion modeling to determine the maximum
allowable emission rate.
This emission rate becomes the adjusted
Tier
I feed rate screening limit.
The feed rate screening limits
for
carcinogenic
metals
are
implemented
as
prescribed
in
subsection
(b)(2),
above.
f)
Alternative implementation approaches.
1)
Pursuant
to
subsection
(f)(2),
below,
the
Agency
shall
approve on a case—by—case basis approaches to implement the
Tier
II or Tier III metals emission limits provided by
subsectione
(c)
or
(d),
above,
alternative to monitoring the
feed rate of metals in each feedstream.
2)
The emission limits provided by subsection
(d), above, must
be determined as follows:
A)
For each noncarcinogenic metal, by back—calculating
from the RAC provided in Section 726.Appendix D to
determine the allowable emission rate for each metal
using the dilution factor for the maximum annual
average ground level concentration predicted by
dispersion
modeling
in
conformance
with
subsection
(h),
below;
and
B)
For
each
carcinogenic metal by:
i)
Back—calculating
from
the
RSD
provided
in
Section 726.Appendix E to determine the
allowable
emission
rate
for
each
metal
if
that
metal were the only carcinogenic metal emitted
using the dilution factor for
the
maximum
annual
average ground level concentration predicted by
dispersion modeling in conformance with
subsection
(h), below; and
ii)
If more than one carcinogenic metal is emitted,
selecting an emission limit for each
carcinogenic metal not to exceed the emission
rate determined by subsection
(f)(2)(B)(i),
above,
such that the sum for all carcinogenic
metals of the ratios of the selected emission
limit to the emission rate determined by that
subsection does not exceed 1.0.
g)
Emission testing.
1)
General.
Emission testing for metals must be conducted
72
using the Multiple Metals Train as described in Section
726.Appendix
I
(“cyc”).
2)
Hexavalent chromium.
Emissions of chromium are assumed to
be hexavalent chromium unless the owner or operator conducts
emissions testing to determine hexavalent chromium emissions
using procedures prescribed in Section 726.Appendix
I
(“aye”).
h)
Dispersion modeling.
Dispersion modeling required under this
Section must be conducted according to methods recommended in
~ootion 726.Appondix 340 CFR 51, a~nendixW (“Guideline on Air
Quality
Models
(Revised)”
(19861
and
its
supplements),
the
“Hazardous Waste Combustion Air Quality Screening Procedure”
described
in Section 726.Appendix
I
(“eye”), or j~~.”EPASCREEN
Lorooning E~roooduro”as described in
Screening
Procedures
for
Estimating the Air Quality Impact of Stationary Sources.
Revised’t
(the latter document is incorporated by reference, eeejj~35
Ill.
Adm. Code 720.111) to predict the maximum annual average off-site
ground level concentration.
However, on—site concentrations must
be considered when a person resides on—site.
i)
Enforcement.
For
the purposes of permit enforcement, compliance
with
the
operating
requirements
specified
in
the
permit
(under
Section 726.202) will be regarded as compliance with this Section.
However, evidence that compliance with those permit conditions
is
insufficient to ensure compliance with the requirements of this
Section is “information” justifying modification
or revocation and
re—issuance of
a permit under 35
Ill. Adm. Code 703.270 et seq.
(Source:
Amended at
18 Ill. Reg.
_________,
effective
_____________________
Section
726.212
Regulation
of
Residues
A
residue
derived
from
the
burning
or
processing
of
hazardous
waste
in
a
BIT
is
not
excluded
from
the
definition
of
a
hazardous
waste
under
35
Ill.
Adin.
Code
721.104(b)
(4),
j.~~(7)~
or
(b)(8)
unless
the
device
and
the
owner
or
operator meet the following requirements:
a)
The device meets the following criteria:
1)
Boilers.
Boilers must burn at least 50
coal on a total
heat input or mass basis, whichever results in the greater
mass feed rate of coal;
2)
Ore or mineral
furnaces.
Industrial furnaces subject to 35
Ill. Adm. Code 721.104(b) (7) must process at least 50
by
weight normal,
nonhazardous raw materials;
3)
Cement kilns.
Cement kilns must process at
least 50
by
weight
normal cement—production raw materials;
b)
The
owner
or
operator
demonstrates that the hazardous waste does
not significantly affect the residue by demonstrating conformance
with
either
of
the
following
criteria:
1)
Comparison
of
waste—derived
residue
with
normal
residue.
The waste-derived residue must not contain 35
Ill.
Adm. Code
721.Appendix H constituents (toxic constituents)
that could
reasonably
be
attributable
to
the
hazardous
waste
at
concentrations significantly higher than in residue
generated without burning or processing of hazardous waste,
73
using
the
following
procedure.
Toxic
compounds
that
could
reasonably be attributable to burning or processing the
hazardous waste (constituents of concern)
include toxic
constituents
in
the
hazardous
waste, and the organic
compounds listed in 35
Ill.
Adm.
Code 721.Appendix H that
may be PICa.
Sampling and analyses must be in conformance
with procedures prescribed 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(a).
A)
Normal
residue.
Concentrations
of
toxic
constituents
of
concern
in
normal
residue
must
be
determined
based
on
analyses
of
a
minimum
of
10
samples
representing
a
minimum
of
10
days
of
operation.
Composite
samples
may
be
used
to
develop
a
sample
for
analysis provided
that the compositing period does not exceed 24 hours.
The
upper
tolerance
limit
(at
95
confidence with a
95
proportion of the sample distribution)
of the
concentration in the normal residue shall be
conBidered the statistically—derived concentration in
the normal residue.
If changes
in
raw materials or
fuels
reduce
the
statistically-derived
concentrations
of
the
toxic constituentB of concern in the normal
residue,
the
statistically—derived
concentrations
must
be
revised
or
statistically—derived concentrations of
toxic constituents in normal residue must be
established for a new mode of operation with the new
raw material or fuel.
To determine the upper
tolerance limit
in the normal residue, the owner or
operator shall use statistical procedures prescribed
in
“Statistical
Methodology
for
Bevill
Residue
Determinations”
in
Section
726.Appendix
I
(“eye”).
B)
Waste—derived residue.
Waste derived residue must be
sampled and analyzed as often as necessary to
determine
whether
the
residue
generated
during
each
24—hour
period
has
concentrations
of
toxic
constituents that are higher than the concentrations
established for the normal residue under subsection
(b)(1)(A), above.
If
so,
hazardous waste burning has
significantly affected the residue and the residue
is
not excluded from the definition of “hazardous waste”.
Concentrations of toxic constituents in waste—derived
residue must be determined based on analysis of one or
more samples obtained over
a 24—hour period.
Multiple
samples may be analyzed,
and multiple samples may be
taken to form a composite sample for analysis provided
that
the
sampling
period
does not exceed 24 hours.
If
more
than
one
sample
is
analyzed
to
characterize
waste—derived residues generated over
a 24—hour
period,
the concentration of each toxic constituent
must be the arithmetic mean of the concentrations in
the samples.
No results can be disregarded; or
2)
Comparison of waste—derived residue concentrations with
health-based
limits.
A)
Nonmetal
constituents.
The
concentratione of each
nonmetal toxic constituente of concern
(specified in
subsection
(b)(1),
above)
in
the waste—derived residue
must
not
exceed
the
health—based
levele
specified
in
74
Section 726.Appendix
G,
or the level of detection
(using analytical procedures prescribed in “Test
Methods for Evaluating Solid Waste, Physical/Chemical
Methods”,
U.S. EPA Publication SW—846~incorporated by
reference in 35 Ill.
Adxn.
Code 720.111),
whichever is
higher.
If a health-based limit for
a constituent of
concern
is not listed in Section 726.Appendix G, then
a limit of 0.002
ieijg/kg or the level of detection
(using analytical procedures prescribed 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), whichever
is
higher,
must
be
used.
The
levels
snecified
in
Section
726.Ap~endix
G
(and
the
default level of 0.002
ua/ka
or
the
level
of
detection
for
constituents,
as
identified
in
Note
1
of
Section
726.Appendix GI
are
administratively
staved
under
the
condition,
for
those
constituents specified in subsection
(b)(1) above,
that the owner or operator complies with alternative
levels defined as the land disnosal restriction limits
specified
in
35
Ill.
Adm.
Code
728.143
and
728.Table
B
for
P039
nonwastewaters.
In complying with those
alternative
levels,
if
an
owner
or
operator
is
unable
to
detect
a
constituent
despite
documenting
use
of
the
beet
good-faith
efforts,
as
defined
by
applicable
U.S.
EPA
guidance
and
standards,
the
owner
or
operator
is
deemed
to
be
in
compliance
for
that
constituent.
Until U.S. EPA develops new guidance or standards, the
owner
or
operator
may
demonstrate
such
good—faith
efforts
by
achieving
a
detection
limit
for
the
constituent
that
does
not
exceed
an
order
of
magnitude
above
(ten times~the level provided by 35
Ill.
Adxn.
Code 728.143 and 728.Table B
for P039 nonwastewaters.
The stay will remain in effect until further rule-
making action
is taken and
B)
Metal constituents.
The concentration of metals in an
extract obtained using the TCLP test muBt
not
exceed
the levels specified in Section 726.Appendix G; and
C)
Sampling and analysis.
Wastewater—derived residue
must be sampled and analyzed as often as necessary to
determine whether the residue generated during each 24
hour period has concentrations of toxic conBtituents
~.shichthatare higher than the health—based levels.
Concentrations of concern in the wastewater—derived
residue must be determined based on analysis of one or
more samples obtained over a 24—hour period.
Multiple
samples may be analyzed,
and multiple samples may be
taken to form a composite for analysis provided that
the sampling period does not exceed 24 hourB.
If more
than one sample is
analyzed to characterize waste—
derived residues generated over a 24 hour period, the
concentration of each toxic constituent
is the
arithmetic mean of the concentrations of the samples.
No results can be disregarded; and
c)
Records sufficient to document compliance with the provisions of
this Section must be retained until closure of the BIF unit.
At
a
minimum, the following must be recorded:
75
1)
Levels of constituents
in 35
Ill. Adm.
Code 721..Appendix
H
that are present in waste—derived residues;
2)
If the waste—derived residue
is compared with normal residue
under subsection (b)(l), above:
A)
The levels of constituents in 35
Ill.
Adm. Code
721.Appendix H that are present in normal residues;
and
B)
Data and information,
including analyses of samples as
necessary,
obtained to determine if
changes
in
raw
materials or fuels would reduce the concentration of
toxic constituents of concern in the normal residue.
(Source:
Amended at
18
Ill. Reg.
_________,
effective
______________________
Section 726.Appendix G
Health—Based Limits for Exclusion of Waste—Derived
Residues
BOAflD NOTE.j~: PUnder Section 726.212(bl(2UA),
the health-based concentration
limits for
35
Ill.
Adni. Code 72l.Appendix
H constituents for which a health—
based concentration is not provided below is 0.002 ua/ka
(O.000002E-06 mg/kgj.
NOTE 2:
The levels specified in this Section and the default level of 0.002
uc/kc
(0.000002 mo/ka) or the level of detection for constituents,
as
identified in Note 1,
are administratively staved under the condition, for
those constituents specified in Section 726.212 (b) (1), that the owner or
operator complies with alternative levels defined as the land disposal
restriction limits specified in
35
Ill.
Adni.
Code 728.143 and 728.Table B for
F039 nonwastewaters.
See Section 726.212(bl(2)(A).
Metals-TCLP Extract Concentration Limits
Constituent
CAS No.
Concentration
limits
(mg/L)
Antimony
7440-36—0
1.~E+00
Arsenic
7440—38—2
5.E+00
Barium
7440—39—3
lOO.E+02
Beryllium
7440—41—7
0.007E 03
Cadmium
7440-43—9
1~E+0O
Chromium
7440—47-3
Lead
7439—92—1
5~Ef00
Mercury
7439—97—6
Q~2E01.
Nickel
7440-02—0
70.E-i-01
Selenium
7782—49—2
1.~E+00
Silver
7440—22—4
5~E-F00
Thallium
7440-28-0
7.~E1-O0
Nonmetals—Residue Concentration Limits
Constituent
CAS
No.
Concentration
limits for
residues
(mg/kg)
Acetonitrile
75—05—8
Q~2E—01
Acetophenone
98—86—2
4~E+00
Acrolein
107-02—8
Q~5E01
76
Acrylamide
Acrylonitrile
Aldrin
79—06—1
107—13—1
309—00—2
0.0002E 04
0.0007g 04
0.00002B—
Allyl alcohol
Aluminum
phosphide
Aniline
Barium cyanide
Benz (a)anthracene
Benzene
Benzidine
Bis (2—chloroethyl) ether
Bis(chloromethyl) ether
107—18—6
20859—73—8
62—53—3
542—62—1
56—55—3
71—43—2
92—87—5
111—44—4
542—88—1
46
0.2E—-01
0.01E—02
Q.~6E02
l.~E~*
00
o.000lz: 04
0.005E 03
0.0000015—
0.00035 04
0.0000025—
Bis(2—ethylhexyl) phthalate
Bromoform
Calcium cyanide
117—81—7
75—25—2
592—01—8
30.5+01
0.7E 01
0.0000015—
Carbon
disulfide
Carbon
tetrachloride
Chlordane
Chlorobenzene
Chloroform
Copper cyanide
Cresols
(Cresylic acid)
Cyanogen
DDT
Dibenz (a,
h)—anthracene
75—15—0
56—23—5
57—74—9
108—90—7
67—66—3
544—92 —3
1319—77—3
460—19—5
50—29—3
53—70—3
4~E+00
0.005E 03
0.0003E 04
1~E+00
0.06E—02
0.25
01
2~E*00
1~E+0O
0.0015—03
0.0000075-
1,2—Dibromo—3—chloropropane
96—12—8
0.000025-
p-Dichlorobenzene
Dichlorodifluoromethane
1,1-Dichloroethylene
2, 4-Dichlorophenol
1,3-Dichloropropene
Dieldrin
Diethyl phthalate
Diethylstilbestrol
Dimethoate
2,4-Dinitrotoluene
Diphenylamine
1,2—Diphenylhydrazine
Endosulfan
Endrin
Epichlorohydrin
Ethylene dibromide
Ethylene oxide
Fluorine
Formic acid
Heptachlor
106—46—7
75—71—8
75—35—4
120—83—2
542—75—6
60—57—1
84—66—2
56—53—1
60—51—5
12 1—14—2
122—39—4
122—66—7
115—29—7
72—20—8
106—89—8
106—93—4
75—21—8
7782—41—4
64—18—6
76—44—8
46
0.07.55 02
7~E+00
0.0055-03
0.15—01
0.0015 03
0.000025—
30.E~+01
0.00000075 07
0.035—02
0.00055—04
0.95
01
0.0005E—0d
0.0025—03
0.00025—04
0.045—02
0.00000045-07
0.00035—04
4~B±00
70.5+01
0.000085—
Heptachlor
epoxide
Hexachlorobenzene
Hexachlorobutadiene
Hexachlorocyclopentadiene
Hexachlorodibenzo—p—dioxins
1024—57—3
118—74—1
87—68—3
77—47—4
19408—74—3
0.000045-
0. 00025—04
0.0055—03
Q.~2E—0-1
77
0.000000065—
46
Hexachloroethane
67-72-1
Hydrazine
302-01—1
0.0001E—04
Hydrogen cyanide
74—90-8
0.000075—
44
Hydrogen
sulfide
7783—06—4
0.0000015—
4’
Isobutyl alcohol
78—83—1
1Q.~E*0l
Methomyl
16752—77—5
1~E400
Methoxychlor
72—43-5
3—Methylcholanthrene
5 6-49—5
0.000045-
45
4,4’—Methylenebis
(2—chloroaniline)
101—14—4
0.0025-03
Methylene chloride
75-09-2
Q~Q5E-02
Methyl ethyl ketone
(MEK)
78—93—3
2.~E4.0O
Methyl hydrazine
60-34—4
0.0003~04
Methyl parathion
298—00-0
Q~Q25--O2
Naphthalene
91-20-3
1Q~E-l-G1
Nickel cyanide
557—19—7
75 01
Nitric
oxide
10102—43—9
4~E~t00
Nitrobenzene
98-95-3
Q~Q2E-0~
N—Nitrosodi—n-butylamine
924—16-3
0.000065—
44
N-Nitrosodiethylamine
55—18—5
0.0000025—
46
N-Nitroao—N—methylurea
684-93-5
0.00000015-07
N—Nitroaopyrrolidine
930-55—2
0.00025
04
Pentachlorobenzene
608-93—5
Q~3E 02
Pentachloronitrobenzene
(PCNB)
82—68—8
~lE
01
Pentachiorophenol
87—86—5
1~E+00
Phenol
108—95—2
1~E+00
Phenylmercury acetate
62—38—4
0.0035 03
Phosphine
7803—51—2
Q~QlE02
Polychlorinated biphenyls,
N.O.S
1336—36—3
0.000055-
44
Potassium cyanide
151—50—8
2 StOp
Potassium silver cyanide
506—61-6
7.5+00
Pronamide
23950—58—5
3.5+00
Pyridine
110—86—1
Q~Q4E
02
Reserpine
50—55—5
0.00003S—
4’
Selenourea
630-10—4
~2E-01
Silver cyanide
506—64—9
4.5+00
Sodium cyanide
143—33—9
l~.5t00
Strychnine
57—24—9
~QlE—02
1,2,4,5—Tetrachlorobenzene
95—94—3
Q~Q1E—02
1,1,2,2—tetrachloroethane
79—34—5
0.0025-03
Tetrachloroethylene
127—18-4
Q~7E01
2,3,4, 6—Tetrachiorophenol
58—90—2
0.015—02
Tetraethyl lead
78—00—2
0.0000045—
46
Thiourea
62—56—6
0.00025
04
Toluene
108—88—3
10.5+01
Toxaphene
8001—35—2
0.0055—03
1,1,2—Trichloroethane
79—00—5
0.0065 03
Trichloroethylene
79—01—6
O.cos~p~
Trichloromonofluoromethane
75—69—4
1Q~E+0l
2,4,5—Trichlorophenol
95—95—4
4~E+00
2,4,6—Trichlorophenol
88—06—2
4~E+00
Vanadium pentoxide
1314—62—1
~75
Cl
78
Vinyl chloride
75—01—4
0.0025
03
(Source:
Amended at 18 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
Sect ion
728.110
First Third
728.111
Second Third
728.112
Third Third
728.113
Newly Listed Wastes
728.114
Surface Impoundment exemptions
SUBPART C:
PROHIBITION ON
LAND
DISPOSAL
Section
728.130
Waste Specific Prohibitions
-—
Solvent Wastes
728.131
Waste Specific Prohibitions
-—
Dioxin—Containing Wastes
728.132
Waste Specific Prohibitions
——
California List Wastes
728.133
Waste Specific Prohibitions
——
First Third Wastes
728.134
Waste Specific Prohibitions
——
Second Third WasteB
728.135
Waste Specific Prohibitions
——
Third Third Wastes
728.136
Waste Specific Prohibitions
——
Newly Listed Wastes
728.137
Waste Specific Prohibitions
——
Ignitable and Corrosive
Characteristic Wastes Whose Treatment Standards Were Vacated
728.139
Statutory Prohibitions
SUBPART
D:
TREATMENT
STANDARDS
Section
728.140
Applicability of Treatment Standards
728.141
Treatment Standards Expressed as Concentrations in Waste Extract
728.142
Treatment Standards Expressed as Specified Technologies
728.143
Treatment Standards expressed as Waste Concentrations
728.144
Adjustment of Treatment Standard
728.145
Treatment Standards for Hazardous Debris
728.146
Alternative Treatment Standards Based on
HTMR
SUBPART E:
PROHIBITIONS ON STORAGE
Section
728.150
Prohibitions on Storage of Restricted Wastes
79
728.Appendix A
728.Appendix B
728.Appendix C
728.Appendix
D
728.Appendix E
728.Appendix P
728.Appendix G
728.Appendix H
728.Appendix I
728.Table A
728.Table
B
728.Table C
728.Table
D
728.Table E
728.Table P
728.Table G
728.Table
H
Toxicity Characteristic Leaching Procedure
(TCLP)
Treatment Standards
(As concentrations in the Treatment
Residual Extract)
List of Halogenated Organic Compounds
Organometallic Lab Packs
Organic Lab Packs
Technologies to Achieve Deactivation of Characteristics
Federal Effective Dates
National Capacity LDR Variances for UIC Wastes
EP
Toxicity Test Method and Structural Integrity Test
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
AUTHORITY:
Implementing Section 22.4 and authorized by Section 27 of the
Environmental Protection Act
(Ill.
Rev. Stat.
1991,
ch.
111½, pars.
1022.4 and
1027
(415 ILCS 5/22.4 and 27).
SOURCE:
Adopted in R87-5 at
11 Ill. Reg. 19354, effective November 12,
1987;
amended in R87—39 at
12
Ill.
Reg. 13046, effective July 29,
1988;
amended in
R89—1 at
13
Ill.
Reg.
18403, effective November 13, 1989; amended in R89—9 at
14
Ill.
Reg.
6232,
effective April
16,
1990;
amended in R90—2 at 14 Ill. Reg.
14470, effective August 22,
1990;
amended in R90—10 at 14 Ill. Reg.
16508,
effective September 25,
1990;
amended
in R90—ll at 15 Ill.
Reg. 9462,
effective June 17,
1991;
amended in R92—10 at
17
Ill.
Reg.
5727, effective
March 26,
1993; amended in R93—4 at
17
Ill. Reg.
20692, effective November 22,
1993; amended in R93—16 at
18
Ill.
Reg. 6799,
effective April
26, l994~
amended
in R94—7 at
Ill.
Rea.
,
effective
SUBPART A:
GENERAL
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, the generator shall
test its waste,
or test an extract using the toot method doocribod
in 35
Ill. 1~dm. Code 72l.2’~ppcndixSToxicity Characteristic
Leaching Procedure, Method 1311,
in “Test Methods for Evaluating
Solid Waste,
Physical/Chemical Methods”.
U.S. EPA Publication SW—
846.
as incorporated by reference in 35 Ill.
Adni. Code 720.111, or
use knowledge of the waste,
to determine
if the waste is
restricted from land disposal under this Part.
Except as
specified in Section 728.132,
if
a generator’s waste exhibits one
or more of the characteristics set out at 35 Ill. Adm. Code
721.Subpart
C, the generator shall test an extract using the toot
method described
in Loation 72S.l~.ppcndiuISP Toxicity Test, Method
1310,
in “Test Methods for Evaluating Solid Waste,
Phvsical/
Chemical Methods”, U.S. EPA Publication SW—846. 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, PSUBS,
or RORGS of Section 728.Table C of this Part),
or
80
the characteristic or corrosivity
(D002),
and is prohibited under
Section 728.137,
the generator shall determine what underlying
hazardous constituents
(as defined in Section 728.102 of this
Part),
are reasonably expected to be present
in the D001 or D002
waste.
1)
If a generator determines that the generator is managing a
restricted waste under this Part and determines that the
waste does not meet the applicable treatment standards set
forth in 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 this Part and
any applicable prohibition
levels set forth in Section
728.132 or 728.139.
The notice must include the following
information:
A)
U.S. EPA hazardous waste number;
B)
The corresponding treatment standards for wastes POOl
through F005,
P039,
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 the applicable
wastewater (as defined in Section 728.102(f)) or
nonwastewater
(as defined
in Section 728.102(d))
category,
the applicable subcatogory made within
a
waste code based on waste—specific criteria
(such as
D003 reactive cyanides), and the Sections and
subsections where 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.
C)
The manifest number associated with the shipment of
waste;
and
D)
For
hazardous debris, the contaminants subject to
treatment as provided by Section 728.145(b) and the
following statement:
“This hazardous debris is
subject
to
the
alternative
treatment
standards
of
35
Ill.
Adm.
Code
728.145;
and
E)
Waste analysis data,
where available.
2)
If
a
generator determines that the generator 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,
storage or land disposal facility,
a notice and
a
certification Btating that the waste meets the applicable
treatment standards set forth in Subpart D of this Part and
the applicable prohibition levels
Bet
forth in Section
728.132 or 728.139.
Generators of hazardous debris that
is
excluded
from
the
definition
of
hazardous waste under 35
Ill. Adm. Code 721.103(c),
35
Ill. Adm.
Code 728.103(f)(2)
and 35
Ill.
Adm. Code 720.122
(i.e. debris that is
81
delisted),
however are 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 standards for wastes
FOOl through P005,
F039 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 referenced by including on
the notification the applicable wastewater or
nonwastewater
(as defined in Section 728.102)
category,
the applicable subdivisions made
within a waste code based on waste—specific
criteria (such as 0003,
reactive cyanides), and
the Section and subsection where the applicable
treatment Btandard 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.
iii)
The manifest number associated with the shipment
of waste;
iv)
Waste analysis data, where available
B)
The certification must be signed by an authorized
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 0 and all applicable
prohibitions set forth in 35
Ill. Adm. Code
728.132,
728.139 or Section 3004(d)
of the
Resource Conservation and Recovery Act.
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 posBibility
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 728.101(c) (3) or a
nationwide capacity variance under 40 CFR 268.Subpart C
(19492), with each shipment of waste,
the generator shall
submit a notice with 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:
82
A)
US
EPA hazardous waste number:
B)
The corresponding treatment standards for wastes FOOl
through P005, P039 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 the
,
and the Section
and subsection where 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.
C)
The manifest number associated with the shipment
of
waste;
0)
Waste analysis data,
where available;
E)
For hazardous debris,
the contamineneta subject to
treatment as provided by Section 728.145(b)
and the
following statement:
“This hazardous debris is
subject to the alternative treatment standards of
35
Ill.
Adm. Code 728.145”;
and
F)
The date the waste is subject to the prohibitions.
4)
If
a generator is managing a prohibited waste in tanks or
containers regulated under 35
Ill. Adm. Code 722.134,
and is
treating such waste in such tanks,
containers or containment
buildings to meet applicable treatment standards under
Subpart 0 of this Part,
the generator shall develop and
follow
a written waste analysis plan ~thiohthatdescribes the
procedures the generator will carry out to comply with the
treatment standards.
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
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 Bhall 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
83
shall retain all waste analysis data on site in the
generator’s
files.
6)
If
a generator determines,
subsequent to the time of
generation,
that the generator is managing a restricted
waste whichthat
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,
subsequent exclusion from
the definition of hazardous or solid waste or exemption from
regulation as
a RCRA hazardous waste,
and the disposition of
the waste.
7)
Generators shall retain on—site a copy of all notices,
certifications, demonstrations, waste analysis data 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 treatment storage or disposal.
The five year
record retention period
is automatically extended during the
course of any unresolved enforcement action regarding the
regulated activity 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,
or when the waste is excluded from the definition
of hazardous or solid waste under 35
Ill.
Adin. Code 721.102
through 721.106,
or 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 728.142, with
each shipment of waste the generator shall submit a notice
to the treatment facility in accordance with subsection
(a)(1) above.
The generator shall also comply with the
requirements in subsections
(a)(5) and
(a)(6)
above-7- 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
contains
only
the
wastes
specified
in
35
Ill.
Adm.
Code
728.Appendix
D
or
solid
wastes
not
subject
to regulation under 35 Ill.
Adm. Code 721.
I 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 contains organic
wastes specified in Section 728.Appendix E and wishes to use
the alternate treatment standards under Section 728.142,
with each shipment of waste the generator shall submit a
notice to the treatment facility in accordance with
subsection
(a)(1) above.
The generator also shall comply
with the requirements in subsections
(a)(5) and (a)(6)
above-
and shall submit the following certification
whichthat must be signed by an authorized representative:
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
84
and that the lab pack contains only organic waste
specified in 35
Ill. Adm.
Code 728.Appendix
E or solid
wastes not subject to regulation under 35
Ill.
Adm.
Code
721.
I am aware that there are significant
penalties for submitting a false certification,
including the possibility of
fine or imprisonment.
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, until either any subsequent enforcement
action is resolved, or the Agency notifies the generator
documents need no be retained.
b)
Treatment facilities shall test their wastes according to the
frequency specified in their waste analysis plans
as required by
35
Ill. Adm. Code 724.113 or 725.113.
Such testing must be
performed as provided in subsections
(b)(1),
(b)(2) 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
whichthat are not subject to any treatment standards under
Subpart
0 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 residueB meet the applicable treatment
standards.
4)
A notice must be Bent with each waste shipment to the land
disposal facility whichthat includes the following
information, except that debris excluded from the definition
of the hazardous waste under Section 728.103(f)(2)
(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
requirmenta of subsection
(d) below rather than these
notification requirments:
A)
U.S. EPA hazardous waste number;
85
B)
The corresponding treatment standards for wastes FOOl
through FOOS,
P039, wastes prohibited pursuant to
Section 728.132 or 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 0001 and
D002 wastes
if those wastes are prohibited under
Section 728.137 of this Part.
Treatment standards
for
all other restricted wastes must either be included,
or be referenced by including on the notification the
applicable wastewater
(as defined in Section
728.102(f))
or nonwastewater
(as defined in Section
728.102(d))
category, the applicable subdivisions made
within a waste code based on waste—specific criteria
(such as 0003 reactive cyanides), and the Sections and
subsections where 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.
C)
The manifest number associated with the shipment of
waste; and
0)
Waste analysis data,
where available.
5)
The treatment facility 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 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 Section 728.1O3(f)(2)
(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 requirments of
subsection
(d) below rather than the certification
requirements of 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 whichthat
are not subject to any treatment standards under
Subpart
0 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
sin 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
86
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
Subpart
D 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. 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 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,
storage 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.
Mm.
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
87
the recycling facility shall submit a certification
described in subsection
(b)(5)
above-i- and
a notice whichth3t
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-i- and the certification specified
in Section 728.108 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 wasteB or
treatment residues are in compliance with the applicable
treatment standards set forth in Subpart D of this 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 dispoBal
is in accordance with the requirements of Section
728.105(h)(2).
The same requirement applies to any waste
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)(l)
through
j~J(3)
above
with
respect
to
such
waste.
d)
Generators or treaters w~ethatfirst claim that hazardous debris
is excluded from the definition of hazardous waste under 35 Ill.
Adni.
Code 728.103(f)(2)
(i.e.,
debris treated by an extraction or
destruction
technology
provided
by
Section 728.Table F,
and debris
that
has
been
delisted)
are
Bubject
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
D
facility
receiving
the
treated
debris;
88
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. Mm.
Code
728.103(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)(1),
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 728.103(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.”
(Source:
Amended
at
18
Ill.
Reg.
_________,
effective
______________________
SUBPART
0:
TREATMENT
STANDARDS
Section
728.140
Applicability of Treatment Standards
a)
A restricted waste identified
in Section 728.141 may
be
land
disposed only if an extract of the waste or of the treatment
residue of the waste developed using the test method
35 Ill.
Adin.
Code
721.Appondix
SMethod
1311,
the
Toxicity
Characteristic
Leaching
Procedure,
does
not
exceed
the
value
shown
in
Section
728.Table
A
for
any hazardous constituent listed in Section
728.Table A for that waste, with the following exceptions:
0004,
D008,
K031,
1(084,
K101,
1(102,
P010,
P011,
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 the toot method in 35
Ill. Mm.
Code 72l.Appondix EMethod
1310.
the Extraction Procedure Toxicity Test.
or Method 1311,
the
Toxicity
Characteristic Leaching Procedure,
or the test method in
Section 728.Appendix A
does
not
exceed
the
yaluoconcentration
shown
in
Section
728.Table
B
for
any hazardous constituent listed
in
Section
728.Table A for that waste.
Methods
1310
and
1311
are
both
found
in
“Test
Methods
for
Evaluating
Solid
Waste,
Physical!
89
Chemical
Methods”.
U.S.
EPA
Publication
SW—846,
as
incorporated
by
reference
in
35
Ill.
Mm.
Code
720.111.
b)
A restricted waste for which a treatment technology
is specified
under Section 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
set
forth
in
Section
728.142(b).
For waste displaying
the characteristic of ignitability
(0001) and reactivity (0003),
that are diluted to meet the deactivation treatment standard in
Section 728.Tables C and D
(DEACT), the treater shall comply with
the precautionary measures specified in 35
Ill.
Adm.
Code
724.117(b) and
35
Ill.
Adm.
Code
725.117(b).
C)
Except as otherwise 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
for
any
hazardous
constituent
listed
in
Section
728.Table B for
that
waste.
d)
If
a
treatment
standard
has
been
established
in
Sections
728.141
through 728.143 for a hazardous waste that
is
itself subject to
those standards rather than the standards for hazardous debris
under Section 728.145.
(Source:
Amended at
18
Ill. Reg.
________,
effective
_____________________-
Section 728.141
Treatment Standards Expressed as Concentrations in Waste
Extract
a)
Section 728.Table A identifies the restricted wastes and the
concentrations
of
their
associated
constituents
whiohthat
may
not
be
exceeded
by
the
extract
of
a
waste
or
waste
treatment
residual
dovolopaxtracted using the toot method in Section 728.Appondix
AMethod
1311.
the
Toxicity
Characteristic
Leachina
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 1311
is found in
“Test
Methods
for
Evaluating
Solid
Waste.
Physical/Chemical
Methods”.
U.S.
SPA
Publication
SW—846,
as
incorporated
by
reference
in
35
Ill.
Adxn.
Code
720.111.
b)
When
wastes
with
differing
treatment
standards
for
a
constituent
of
concern
are combined for purposes of treatment,
the treatment
residue
must
meet
the
lowest treatment standard for the
constituent
of
concern,
except
that mixtures of high and low zinc
nonwastewater
1(061
are
subject
to
the treatment standard for high
zinc
1(061.
C)
The
treatment
standards
for
the
constituents
in
POOl
through
P005
whichthat
are
listed
in
Section
728.Table
A
only
apply
to
wastes
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
POOl
through
FOOS,
then
only
the treatments standards in Section 728.Table A are required.
(Source:
Amended at 18
Ill.
Reg.
_________,
effective
______________________)
Section
728.142
Treatment
Standards
Expressed
as
Specified
Technologies
90
a)
The following wastes in subsections
(a)(1)
and
(2) below and
Sections 728.Table D and 728.Table S must be treated using the
technology or technologies specified in subBections (a)(1)
and
(2)
and Section 728.Table C.
1)
Liquid hazardous wastes containing PCB5 at concentrations
greater than or equal to 50
ppm
but
less
than
500
ppm
must
be incinerated in accordance with technical requirements at
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 PCB5 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
(HOCs)
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.
Adxn. Code 724.Subpart 0 or
35 Ill. Adni. Code 725.Subpart 0.
These treatment standards do not apply where the waste
is
subject
to
a
Subpart
C
of
this Part treatment standard 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. Adm. 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
process,
and that meet the criteria of the 0001 ignitable
liquids containing greater than 10
total organic
constituents
(TOC) subcategory,
is subject to the DEACT
treatment standard described in 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,
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;
D)
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 e4—Section 728.Table P for hazardous debris.
The
applicant
shall
submit
information
demonstrating
that
the
applicant’s
treatment
method
is
in
compliance
with
federal
and
91
state requirements,
including this Part,
35
Ill.
Adxn.
Code
709,
724,
725,
726 and 729 and Sections
22.6
and
39(h)
of the
Environmental
Protection
Act
(Ill.
Rev.
Stat.
1987,
ch.
111½,
pars.
1022.6
and
1039(h)
(415
ILCS
5/22.6
and
5/39(h))), and
is
protective
of
human
health
or
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 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
Subpart
0
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 hazardous wastes contained in such lab packs
are
specified
in
Section
728.Appendix
D
or
Section
728.Appendix
3)
The
lab packs are incinerated
in accordance with the
requirements
of
35
Ill.
Adm.
Code
724.Subpart 0 or
35
Ill.
Mm.
Code 725.Subpart 0; and
4)
Any
incinerator
residues
from
lab packs containing 0004,
D005,
0006,
0007,
DOOB,
0010
and
DOll
are
treated
in
compliance
with
the
applicable treatment standards specified
for
such
wastes
in
Subpart
D.
d)
Radioactive
hazardous
mixed
wastes
with
treatment
standards
specified in Section 728.Table E are not subject to any treatment
standards specified
in Section 728.141, Section 728.143 or Section
728.Table 0.
Radioactive hazardous mixed wastes not subject to
treatment standards
in Section 728.Table S remain subject to all
applicable treatment standards specified in Section 728.141,
Section 728.143 and Section 728.Table D.
HazardouR debris
containing radioactive waste is not subject to the treatment
standards
specified
in
Section
728.Table
F
but
is
subject
to
the
treatment
standards
specified
in Section 728. 145.
(Source:
Amended at
18
Ill. Reg.
________,
effective
____________________
Section 728.Appendix A
Toxicity Characteristic Leaching Procedure
(TCLP)
The Board incorporates by roforonoo
40
CFR
268,
Appondin
I
(1988).
This
ineorporation inaludea no future editions or
amondmcnts.
Note:
The TCLP
(Method 1311)
is published
in
“Test M3thode for Evaluating
Solid
Waste,
Physical/Chemical
Methods”,
U.S.
EPA
Publication
sW-846.
as
incorporated
bY
reference
in
35
Ill.
Mm.
Code
720.111.
(Source:
Amended
at
18
Ill. Reg.
________,
effective
__________________
92
Section 728.Appendix I
EP Toxicity Test Method and Structural Integrity Test
The
Board incorporates by
reference 40 CFR 268,
~ppondix IX,
adopted at 68
Fed.
Rag.
3876,
January
31,
1991.
This Leotion inoorporatos no future
amendments
or
editions.
Note:
The EP
(Method 1310)
is published in “Test Methods for Evaluating Solid
Waste.
Physical/Chemical Methods”. U.S. EPA Publication SW—846,
as
incorporated by reference
in
35 Ill. Adm.
Code 720.111.
(Source:
Amended at
18
Ill. Reg.
_________,
effective
______________________
Section 728.~ableB
Constituent Concentrations in Wastes (CCW)
0, F and K Listed Wastes
CAS No.
for
Regulated
Hazardous
Constituent
subcategory——based on
35 Ill.
(Total)
57—12—5
(Amenable)
57—12—5
7440—38—2
7440—39—3
7440—43—9
(Total)
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
93—76—5
DOO4
Table
A
DOO5
Table
A
0006
Table A
0007
Table
A
0008
Table A
0009
Table
A
0010
Table
A
0011
Table A
0012
Table 0
D013
Table
0
0014
Table D
D015
Table
0
0016
Table 0
0017
Table
0
F001—F005 spent solvents
Acetone
Benzene
n—Butyl alcohol
Carbon tetrachloride
Chlorobenzene
Cresol
(m- and p—isomers)
o-cresol
o-Dichlorobenzene
Ethyl
acetate
67—64—1
0.28
160.
71—43—2
0.070
3.7 A
71—36—3
5.6
2.6
56—23—5
0.057
5.6
108—90—7
0.057
0.77
0.11
5.7
3.2
5.6
95—50—1
0.088
6.2
141—7—6
0.34
33.
Waste See
Code
Also
D003
(Reactive
NA
Regulated Hazardous
Constituent
cyanidea
Cyanides
Cyanides
Arsenic
Barium
Cadmium
Chromium
Lead
Mercury
Selenium
Silver
Endrin
Lindane
Methoxychlor
Toxaphene
2,4—0
2,4,5—TP
Silvex
Concentra—
Concentra-
tion
(mg/L)
tion
(mg/L)
Nonwaste-
Wastewaters
waters
Mm.
Code
721.123(a)(5))
Res.
#
590.
C
0.86
30.
5.0
NA
100.
NA
1.0
NA
5.0
NA
5.0
NA
0.20
NA
1.0
NA
5.0
NA
NA
0.13
A
NA
0.066
A
NA
0.18 A
NA
l.3A
NA
10.0 A
NA
7.9A
93
Ethyl benzene
100—41—4
0.057
6.0
Ethyl ether
60—29—7
0.12
160.
Isobutyl alcohol
78—83—1
5.6
170.
Methylene chloride
75—9—2
0.089
33.
Methyl ethyl ketone
78—93—3
0.28
36.
Methyl isobutyl ketone
108—10-1
0.14
33.
Nitrobenzene
98—95—3
0.068
14.
Pyridine
110—86—1
0.014
16.
Tetrachloroethylene
127—18—4
0.056
5.6
Toluene
108—88—3
0.08
28.
1,1,l—Trichloroethane
71—55—6
0.054
5.6
l,1,2—Trichloroethane
79—00—5
0.030
7.6 A
Trichloroethylene
79—01—6
0.054
5.6
1,l,2—Trichloro—1,2,2—
76—13—1
0.057
28.
trifluoromethane
Trichloromono—fluorome-
75—69—4
0.02
33.
thane
Xylenea
(total)
0.32
28.
P006
Table A
Cyanides (Total)
57—12—5
1.2
590.
Cyanides
(Amenable)
57—12—5
0.86
30.
Cadmium
7440—43—9
1.6
NA
Chromium
7440—47—32
0.32
NA
Lead
7439—92—1
0.040
NA
Nickel
7440—02—0
0.44
NA
P007
Table A
Cyanides
(Total)
57—12—5
1.9
590.
Cyanides
(Amenable)
57—12—5
0.1
30.
Chromium
(Total)
7440—47—32
0.32
NA
Lead
7439—92—1
0.04
NA
Nickel
7440—02—0
0.44
NA
F008
Table
A
Cyanides
(Total)
57—12—5
1.9
590.
Cyanides
(Amenable)
57—12—5
0.13
30.
Chromium
7440—47—32
0.32
NA
Lead
7439—92—1
0.04
NA
Nickel
7440—02—0
0.44
NA
P009
Table A
Cyanidea (Total)
57—12—5
1.9
590.
Cyanides (Amenable)
57—12—5
0.1
30.
Chromium
7440—47—32
0.32
NA
Lead
7439—92—1
0.04
NA
Nickel
7440—02—0
0.44
NA
POlO
NA
Cyanidee (Total)
57—12—5
1.9
1.5
Cyanides
(Amenable)
57—12—5
0.1
NA
POll
Table A
Cyanides
(Total)
57—12—5
1.9
110.
Cyanides
(Amenable)
57—12—5
0.1
9.1
Chromium
(Total)
7440—47—32
0.32
NA
Lead
7439—92—1
0.04
NA
Nickel
7440—02—0
0.44
NA
P012
Table
A
Cyanidea
(Total)
57—12—5
1.9
110.
Cyanides
(Amenable)
57—12—5
0.1
9.1
Chromium (Total)
7440—47—32
0.32
NA
Lead
7439—92—1
0.04
NA
Nickel
7440—02—0
0.44
NA
P019
Table
A
Cyanidea
(Total)
57—12—5
1.2
590.
C
Cyanidea
(Amenable)
57—12—5
0.86
30.
C
Chromium
(Total)
7440—47—32
0.32
NA
94
be treated
126—99—8
107—05—1
75—34—3
107—06—2
78—87—5
10061—01—5
10061—02—6
117—81—7
67—72—1
7440—47—32
7440—02—0
67—66—3
107—06—2
75—35—4
75—9—2
56—23—5
79—00—5
79—01—6
75—01—4
208—96—8
120—12—7
71—43—2
50—32—8
117—81—7
7 5—15—0
218—01—9
105—67—9
100—41—4
86—73—7
91—20—3
85—01—8
108—95—2
129—00—0
108—88—3
57—12—5
7440—47—32
7439—92—1
71—43—2
50—32—8
117—81—7
218—01—9
84—74—2
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
0.046 B
0.21 B
0.025 B
0.089 B
0.057 B
0.054 B
0.054
B
0.27 B
0.046 B
0.089
B
0.057 B
0.054
B
0.054
B
0.27 B
0.055
B
0.055
B
0.055
B
0.059
B
0.059
8
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
0.2
0.037
0.14 B
0.061 B
0.28 B
0.059 B
0.057 B
0.28 A
0.014 A
0.014 A
0.014 A
0.014 A
0.014 A
1.8 A
1.8 A
NA
NA
6.2 A
6.2
A
6.2
A
31. A
6.2
A
6.2 A
5.6 A
33. A
6.2 A
31.
A
6.2
A
6.2
A
5.6 A
33. A
37.
A
28. A
30. A
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
14.
A
22. A
1.8
A
NA
NA
14. A
12.
A
7.3 A
15.
A
3.6
A
via incineration
(INCIN))
0.28 A
0.28 A
P024
(Note:
P024 organic standards must
Tables
2-Chloro-1, 3-butadiene
A&
0
3-Chloropropene
1, 1—Dichloroethane
1,2—Dichloroethane
1,2—Dichloropropane
cis—l, 3—Dichloropropene
trans—1,3—Dichloropropene
Bis (2-ethylhexyl
)
phthalate
Hexachloroethane
Chromium
(Total)
Nickel
P025
(Light
ends aubcategory)
NA
Chloroform
1, 2—Dichioroethane
1, l—Dichloroethylene
Methylene chloride
Carbon tetrachloride
1,1,2—Trichloroethane
Trichloroethylene
Vinyl chloride
P025
(Spent filters or aids and desiccants aubcategory)
NA
Chloroform
67—66-3
Methylene chloride
75-9-2
Carbon tetrachloride
56-23-5
1, 1,2—Trichloroethane
79—00—5
Trichloroethylene
7 9—01-6
Vinyl
chloride
75-01-4
Hexachlorobenzene
118—74-1
Hexachlorobutadiene
87—68—3
Hexachloroethane
67—72-1
P037
Table
A
Acenaphthene
Anthracene
Benzene
Benzo
(
a) anthracene
Benzo(a)pyrene
Bis(2-ethylhexyl)
phthalate
Chrysene
Di-n—butyl phthalate
Ethylbenzene
Pluorene
Naphthalene
Phenanthrene
Phenol
Pyrene
Toluene
Xylene(a)
Cyanides (Total)
Chromium
(Total)
Lead
P038
Table A
Benzene
Benzo(a)pyrene
Bia (2—ethylhexyl)
pht halate
Chrysene
Di—n—butyl
phthalate
95
Ethylbenzene
100—41—4
0.057
B
14.
A
Pluorene
86—73-7
0.059 B
NA
Naphthalene
91—20-3
0.059
B
42.
A
Phenanthrene
85-01-8
0.059
B
34.
A
Phenol
108—95—2
0.039
B
3.6
A
Pyrene
129—00—0
0.067 B
36. A
Toluene
108—88—3
0.080
B
14.
A
Xylene(s)
0.32
B
22.
A
Cyanides
(Total)
57—12—5
0.028
A
1.8
A
Chromium
(Total)
7440—47—32
0.2
NA
Lead
7439—92—1
0.037
NA
P039
(and DOOl and D002 wastes prohibited under Section 728.137)
Tables
Acetone
67—64—1
0.28 B
160. A
A&D
Acenaphthalene
208—96—8
0.059 B
3.4 A
Acenaphthene
83—32-9
0.059
B
4.0
A
Acetonitrile
75—05—8
0.17
B
NA
Acetophenone
96—86—2
0.010
B
9.7 A
2—Acetylaminofluorene
53—96—3
0.059
B
140. A
Acrolien
107—02-8
0.29
B
Acrylonitrile
107—13—1
0.24 B
84. A
Aorolicn
107—02—8
0.39 B
NA
Aldrin
309—00—2
0.021
B
0.068
A
4—Aminobiphenyl
92—67—1
0.13 B
NA
Aniline
62—53—3
0.81
B
14.
A
Anthracene
120—12—7
0.059
B
4.0
A
Aramite
140—57—8
0.36
B
NA
Aroclor
1016
12674—11—2
0.013
B
0.92
A
Aroclor
1221
11104—28—2
0.014
B
0.92
A
Aroclor
1232
11141—16—5
0.013
B
0.92
A
Aroclor
1242
53469—21—9
0.017
B
0.92
A
Aroclor 1248
12672—29—6
0.013
B
0.92 A
Aroclor
1254
11097—69—1
0.014
B
1.8 A
Aroclor
1260
11096—82—5
0.014
B
1.8
A
alpha—BHC
319—84—6
0.00014
0.066 A
B
beta—BHC
319—85—7
0.00014
0.066 A
B
delta—BHC
319—86—8
0.023
B
0.066 A
gamma—El-iC
58—89—9
0.0017
B
0.066
A
Benzene
71—43—2
0.14
B
36.
A
Benzo(a)anthracene
56—55—3
0.059 B
8.2 A
Benzo(b)fluoranthene
205—99—2
0.055
B
3.4
A
Benzo(k)fluoranthene
207—08—9
0.059
B
3.4
A
Benzo(g,h,i)perylene
191—24—2
0.0055
B
1.5
A
Benzo(a)pyrene
50—32—8
0.061
B
8.2 A
Bromodichloromethane
75—27—4
0.35
B
15.
A
Bromoform
(Tribromo—
75—25—2
0.63
B
15.
A
methane)
Bromomethane
(methyl
74—63-9
0.11 B
15.
A
bromide)
4—Bromophenyl phenyl ether 101-55—3
0.055
B
15.
A
n—Butyl alcohol
71—36—3
5.6 B
2.6 A
Butyl benzyl phthalate
85—68—7
0.017
B
7.9 A
2—sec—Butyl—4,6—dinitro—
88—85—7
0.066
B
2.5 A
phenol
Carbon
tetrachioride
56—23—5
0.057
B
5.6
A
Carbon
disulfide
75-15—0
0.014
B
NA
Chlordane
57—74—9
0.0033
B
0.13 A
p—Chloroaniline
106—47—8
0.46 B
16.
A
Chlorobenzene
108—90-7
0.057
B
5.7 A
96
510—15—6
126—99—8
124—48—1
7 5—00—3
111—91—1
111—44—4
67—66—3
39638—32—9
59—50—7
74—87—3
91—8—7
95—57—8
107—05—1
218—01—9
95—48—7
108—94—1
96—12—8
106—93—4
74—95—3
94—75—7
53—19—0
72—54—8
3424—82—6
72—55—9
789—02—6
50—29—3
53—70—3
192—65—4
541—73—1
95—50—1
106—46—7
75—71—8
75—34—3
107—06—2
75—35—4
120—83—2
87—65—0
78—87—5
10061—01—5
10061—02—6
60—57—1
84—66—2
105—67—9
131—11—3
84—74—2
100—25—4
5 34—52—1
51—28—5
121—14—2
606—20—2
117—84—0
621—64—7
12 2—39—4
122—66—7
0.10 B
0.057 B
0.057 B
0.27 B
0.036
B
0.033
B
0.046
B
0.055 B
0.018
B
0.19
B
0.055 B
0.044 B
0.036
B
0.059 B
0.11 B
0.77 B
0.36
B
0.11
B
0.028
B
0.11 B
0.72
B
0.023
B
0.023
B
0.031
B
0.031
B
0.0039 B
0.0039
B
0.055
8
0.061
A
0.036 B
0.088
B
0.090 B
0.23
B
0.059 B
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
0.32
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
NA
NA
16. A
6.0
A
7.2
A
7.2
A
5.6
A
7.2
A
14.
A
33. A
5.6 A
5.7 A
28.
A
8.2 A
5.6
A
3.2
A
NA
15.
A
15.
A
15.
A
10. A
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
7.2
A
7.2
A
33. A
33. A
14.
A
14. A
18.
A
18.
A
18. A
0.13 A
28. A
14.
A
28. A
28. A
2.3 A
160. A
160. A
140. A
28. A
28. A
14.
A
NA
NA
Chlorobenzilate
2-Chloro—l, 3-butadiene
Chiorodibromomethane
Chioroethane
bis(2—Chloroethoxy)methane
bis (2—Chloroethyl)
ether
Chloroform
bis(2—Chloroisopropyl)
ether
p—Chloro—m—creaol
Chioromethane (Methyl
chloride)
2—Chloronaphthalene
2-Chlorophenol
3-Chloropropene
Chrysene
o—Cresol
Cresol
(m— and p—isomers)
Cyclohexanone
1, 2—Dibromo—3—chloro—
propane
1
,2-Dibromoethane
(Ethylene dibromide)
Dibromomethane
2,4-Dichlorophenoxyacetic
acid (2,4—0)
o,p’-DDD
p,p’-DDD
o,p’-DDE
p,p’-DDE
o,p’-DDT
p,p’-DDT
Dibenzo(a,
h) anthracene
Dibenzo(a,e)pyrene
m—D ichlorobenzene
o—Dichlorobenzene
p-Dichlorobenzene
Dichlorodifluoromethane
1,1-Dichloroethane
1, 2-Dichloroethane
1, i—Dichloroethylene
trana-l,2—Dichloroethylene
2, 4—Dichlorophenol
2, 6—Dichlorophenol
1,2—Dichloropropane
cia—i, 3—Dichloropropene
trans-i,3—Dichloropropene
Dieldrin
Diethyl phthalate
2, 4-Dimethyl phenol
Dimethyl phthalate
Di-n—butyl phthalate
1, 4—Dinitrobenzene
4, 6—Dinitro—o—cresol
2,4-Dinitrophenol
2,
4-Dinitrotoluene
2, 6—Dinitrotoluene
Di-n-octyl
phthalate
Di-n-propylnitrosoamine
Diphenylamine
1,2—Diphenyl
hydrazine
97
Diphenylnitrosoamine
1, 4-Dioxane
Disulfoton
Endosulfan
I
Endosulfan
II
Endosulfan sulfate
Endrin
Endrin aldehyde
Ethyl
acetate
Ethyl cyanide
Ethyl
benzene
Ethyl ether
bis
(
2—Ethylhexyl)
phthalate
Ethyl methacrylate
Ethylene oxide
Pamphur
Pluoranthene
Pluorene
Fluorotrichloromethane
Heptachlor
Heptachlor epoxide
Hexachlorobenzene
Hexachlorobutadiene
Hexachlorocyclopentadiene
Hexachlorodibenzofuran
a
Hexachlorodibenzo—p—
dioxins
Hexachloroethane
Hexachloropropene
Indeno(1,2,3,—c,d)pyrene
lodomethane
Isobutanol
Isodrin
Isosafrole
Kepone
Methacrylonitrile
Methanol
Methapyrilene
Hethanol
Methoxychlor
3-Methylcholanthrene
4, 4—Methylene—bia—(2—
chloroaniline)
Methylene chloride
Methyl ethyl ketone
Methyl isobutyl ketone
Methyl methacrylate
Methyl methansulfonate
Methyl parathion
Naphthalene
2—Naphthylamine
p-Nitroanilme
Nitrobenzene
5-Nitro—o-toluidine
4-Nitrophenol
N-Nitrosodiethylamine
N—Nitrosodimethylamine
N—Nitroso-di-n-butylamine
N—Nitroaomethylethylarnine
N-Nitrosomorpholine
B
B
621—64—7
123—91—1
298—04—4
939—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
0.40
B
0.12
B
0.017
a
0.023
B
0.029
B
0.029
B
0.0028
B
0.025
B
0.34
B
0.24
B
0.057
B
0.12
B
0.28
B
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
86—73—7
75—69—4
76—44—8
1024—57—3
118—74—1
87—68—3
77—47—4
0.14 B
0.12
B
0.017
B
0.068
B
0.059
B
0.020 B
0.0012
B
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
0.000063
0.001 A
67—72—1
1888—71—7
193—39—5
74—88—4
78—83—1
465—73—6
120—58—1
143—50—8
126—98—7
67—56—1
91—80—5
67 56
1
72—43—5
56—49—5
101—14—4
0.055
B
0.035
B
0.0055 B
0.019
B
5.6 B
0.021 B
0.081
B
0.0011 B
0.24
B
5.6
B
0.081 B
5.6 0
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
~
1.5 A
NA
0.18
A
15. A
35.
A
75—09—2
78—93—3
108—10—1
80—62—6
66—27—3
298—00—1
91—20—3
91—59—8
100—01—6
98—95—3
99—55—8
100—02—7
55—18—5
62—75—9
924—16—3
105—95—6
59—89—2
0.089
B
0.28
B
0.14 B
0.14
B
0.018
B
0.014
B
0.059
B
0.52 B
0.028
B
0.068
B
0.32 B
0.12 B
0.40
B
0.40
B
0.40
B
0.40 B
0.40
B
33. A
36.
A
33. A
160.
A
NA
4.6
B~
3.1
A
NA
28.
A
14.
A
28. A
29. A
28.
A
NA
17.
A
2.3 A
2.3
A
98
N—Nitrosopiperidine
100—75—4
0.013
B
35.
A
N—Nitrosopyrrolidine
930—55-2
0.013
B
35.
A
Parathion
56—38—2
0.014 B
4.6 A
Pentachlorobenzene
608-93—5
0.055 B
37. A
Pentachlorodibenzo-furans
0.000063
0.001 A
B
Pentachlorodibenzo—p-
0.000063
0.001 A
dioxins
B
Pentachloronitrobenzene
82—68-8
0.055
B
4.8 A
Pentachlorophenol
87—86-5
0.089 B
7.4 A
Phenacetin
62—44-2
0.081
B
16. A
Phenanthrene
85—01—8
0.059
a
3.1 A
Phenol
108-95—2
0.039
B
6.2 A
Phorate
298—02—2
0.021
B
4.6 A
Phthalic anhydride
85—44—9
0.69 B
NA
Pronamide
23950—58—5
0.093 B
1.5 A
Pyrene
129-00—0
0.067
B
8.2
A
Pyridine
110—86—1
0.014
~
16.
A
Safrola
94—59—7
0.081
B
22.
A
Silvex
(2,4,5—TP)
93—72—1
0.72
B
7.9
A
2,4,5—T
93—76—5
0.72
B
7.9
A
1,2,4,5—Tetrachlorobenzene 95—94—3
0.055
8
19.
A
Tetrachlorodibenzofurana
0.000063
0.001 A
B
Tetrachlorodibenzo—p—
0.000063
0.001 A
dioxina
B
1,1,1,2—Tetrachloroethane
630—20—6
0.057 B
42. A
1,1,2,2—Tetrachloroethane
79—34—6
0.057 B
42.
A
Tetrachloroethylerze
127—18—4
0.056
B
5.6 A
2,3,4,6—Tetrachlorophenol
58—90—2
0.030
B
37. A
Toluene
108—88—3
0.080
B
28. A
Toxaphene
6001-35-i
0.0095
B
1.3 A
1,2,4—Trichlorobenzene
120—82—1
0.055 ~
19.
A
1,1,i—Trichloroethane
71—55—6
0.054 B
5.6 A
1,1,2—Trichloroethane
79—00—5
0.054 B
5.6 A
Trichloroethylene
79—01—6
0.054 B
5.6 A
2,4,5—Trichiorophenol
95-95—4
0.18
B
37.
A
2,4,6—Trichlorophenol
88—06—2
0.035
B
37. A
1,2,3—Trichioropropane
96—18—4
0.85 B
28. A
1,1,2—Trichloro—1,2,2—tri— 76—13—1
0.057 B
28. A
fluoroethane
TriB(2,3—dibromopropyl)-
126—72—7
0.11
B
NA
phosphate
Vinyl
chloride
75—01—4
0.27
B
33.
A
Xylene(s)
0.32 B
28. A
Cyanides
(Total)
57—12—5
1.2
B
1.8
A
Fluoride
16964—48—8
35.
B
NA
Sulfide
8496—25—8
14.
B
NA
Antimony
7440-36—0
1.9
B
NA
Arsenic
7440-38—2
1.4
B
NA
Barium
7440—39—3
1.2
8
NA
Beryllium
7440—41—7
0.82
B
NA
Cadmium
7440—43—9
0.20
B
NA
Chromium (Total)
7440—47—32
0.37
B
NA
Copper
7440-50—8
1.3
B
NA
Lead
7439—92—1
0.28
B
NA
Mercury
7439—97—6
0.15 B
NA
Nickel
7440—02—2
0.55
B
NA
Selenium
7782—49—2
0.82
B
NA
Silver
7440—22—4
0.29 B
NA
99
Thallium
7440—28—0
1.4 B
NA
Vanadium
7440—62—2
0.042 B
NA
Zinc
7440—66—0
1.0
B
NA
1(001
Table
A
Naphthalene
91—20—3
0.031
A
1.5
A
Pentachlorophenol
87—86-5
0.031 A
1.5 A
Phenanthrene
85—01—8
0.18 A
7.4 A
Pyrene
129—00—0
0.028 A
1.5 A
Toluene
108—88—3
0.028
A
28.
A
Xylenes
(Total)
0.032 A
33. A
Lead
7439—92—1
0.037 A
NA
1(002
Table A Chromium (Total)
7440—47—32
0.9 B
NA
Lead
7439—92—1
3.4
B
NA
1(003
Table A
Chromium (Total)
7440-47-32
0.9 B
NA
Lead
7439—92—1
3.4 B
NA
1(004
Table A
Chromium (Total)
7440—47—32
0.9 B
NA
Lead
7439—92—1
3.4
B
NA
1(005
Table
A
Chromium
(Total)
7440—47—32
0.9
B
NA
Lead
7439—92—i
3.4
B
NA
Cyanides
(Total)
57—12—5
0.74 B
0
1(006
Table
A
Chromium
(Total)
7440—47-32
0.9
B
NA
Lead
7439—92—i
3.4
B
NA
1(007
Table
A
Chromium
(Total)
7440—47—32
0.9
B
NA
Lead
7439—92—1
3.4
B
NA
D
Cyanidea
(Total)
57—12—5
0.74
B
1(008
Table
A
Chromium (Total)
7440—47—32
0.9 B
NA
Lead
7439—92—1
3.4
B
NA
1(009
NA
Chloroform
67—66—3
0.1
6.0 A
1(010
NA
Chloroform
67—66—3
0.1
6.0
1(011
NA
Acetonitrile
75—05—8
38.
1.8
Acrylonitrile
107—13—1
0.06
1.4
Acrylamide
79—06—1
19.
23.
Benzene
71—43—2
0.02
0.03
Cyanide
(Total)
57—12—5
21.
57.
1(013
NA
Acetonitrile
75—05—8
38.
1.8 A
Acrylonitrile
107—13—1
0.06
1.4 A
Acrylamide
79—06—1
19.
23.
A
Benzene
71—43—2
0.02
0.03 A
Cyanide (Total)
57—12—5
21.
57.
1(014
NA
Acetonitrile
75—05—8
38.
1.8
A
Acrylonitrile
107—13—i
0.06
1.4 A
Acrylamide
79—06—1
19.
23.
A
Benzene
71—43—2
0.02
0.03 A
Cyanide
(Total)
57—12—5
21.
57.
1(015
Table A
Anthracene
120—12—7
0.059
3.4
A
Benzal Chloride
98—87—3
0.28
6.2 A
Sum
of
Benzo(b)fluoran-
207—08—9
0.055
3.4
thene
and
Benzo(k)fluoran—
thene
100
Phenanthrene
85—01-8
0.059
3.4
A
Toluene
108—88—3
0.08
6.0 A
Chromium (Total)
7440—47-32
0.32
NA
Nickel
7440—02—0
0.44
NA
K0i6
NA
Hexachlorobenzene
118—74-1
0.055
28. A
Hexachlorobutadiene
87-68-3
0.055
5.6 A
Hexachlorocyclopentadiene
77—47-4
0.057
5.6
A
Hexachloroethane
67—72—1
0.055
28.
A
Tetrachloroethene
127—18-4
0.056
6.0 A
1(017
NA
1,2—Dichloropropane
78-87—5
0.85
A
B
18.
A
1,2,3—Trichloropropane
96—18—4
0.85
A
B
28.
A
Bis(2—chloroethyl)ether
111—44—4
0.033 A
7.2 A
B
1(018
NA
Chloroethane
76—00—3
0.27
6.0
A
Chloromethane
74—87-3
0.19
NA
1,l—Dichloroethane
75—34—3
0.059
6.0
A
1,2—Dichloroethane
107—06—2
0.21
6.0 A
Hexachlorobenzene
118—74-i
0.055
28. A
Hexachlorobutadiene
87—68-3
0.055
5.6 A
Pentachloroethane
76—01-7
NA
5.6
1,1,l—Trichloroethane
71—55—6
0.054
6.0
Hexachloroethane
67—72—i
0.055
28. A
1(019
NA
Bis(2—chloroethyl)
ether
111—44—4
0.033
5.6 A
Chlorobenzene
108—90—7
0.057
6.0 A
Chloroform
67—66—3
0.046
6.0 A
p—Dichlorobenzene
106—46-7
0.09
NA
1,2—Dichloroethane
107—06—2
0.21
6.0
A
Fluorene
86—73—7
0.059
NA
Hexachloroethane
67—72—i
0.055
28. A
Naphthalene
91—20-3
0.059
5.6 A
Phenanthrene
85—01—8
0.059
5.6
A
1,2,4,5— Tetrachlor—
95—94—3
0.055
NA
obenzene
Tetrachloroethene
127—18—4
0.056
6.0
A
1,2,4—Trichlorobenzene
120—82—1
0.055
19.
A
1,1,l—Trichloroethane
71—55—6
0.054
6.0
A
1(020
NA
1,2—Dichloroethane
106—93—4
0.21
6.0 A
1,1,2,2—Tetrachloroethane
79—34-6
0.057
5.6 A
Tetrachloroethene
127—18—4
0.056
6.0 A
1(021
Table A Chloroform
67—66—3
0.046
B
6.2 A
Carbon tetrachloride
58—23—5
0.057
B
6.2 A
Antimony
7440—36—0
0.60
B
6.2 A
1(022
Table
A
Toluene
108—88—3
0.080
B
0.034
A
Acetophenone
96—86—2
0.010
19.
A
Diphenylamine
22—39-4
0.52
B
NA
Diphenylnitrosamine
86—30-6
0.40
B
NA
Sum of Diphenylaxnine and
NA
13. A
Diphenylnitrosamine
Phenol
108—95—2
0.039
12. A
Chromium
(Total)
7440—47—32
0.35
NA
Nickel
7440—02—0
0.47
NA
1(023
NA
Phthalic anhydride
85—44—9
0.069
28. A
(measured as Phthalic
acid)
101
1(024
NA
Phthalic anhydride
(measured as Phthalic
acid)
75—34—3
87—68—3
67—72—1
76—01—7
630—20—6
79—34—6
71—55—6
79—00—5
127—18—4
7440—43—9
7440—47—32
7439—92—1
7440—02—0
67—66—3
107—06—2
75—35—4
71—55—6
75—01—4
95—50—1
106—46—7
87—68—3
67—72—1
1888—71—7
608—93—5
76—01—7
95—94—3
127—18—4
120—82—1
7440—38—2
77—47—4
57—74—9
76—44—8
1024—57—3
83—32—9
120—12—7
56—55—3
50—32—8
218—01—9
53—70—3
206—44—0
86—73—7
193—39—5
91—20—3
95—48—7
85—01—8
108—95—2
0.059
0.054
0.055
0.055
NA
0.057
0.057
0.054
0.054
0.056
6.4
0.35
0.037
0.47
0.46
0.21
0.025
0.054
0.27
0.088
0.09
0.055
0.055
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
0.059 B
0.11 B
0.059
B
0.039
6.0
A
6.0
A
5.6 A
28. A
5.6 A
5.6
A
5.6 A
6.0 A
6.0 A
6.0
A
NA
NA
NA
NA
6.0
A
6.0
A
6.0
A
6.0 A
6.0
A
NA
NA
5.6
A
28. A
19.
A
28. A
5.6 A
14.
A
6.0
A
19.
A
NA
24. A
0.26
A
0.066
A
0.066
A
2.4 A
2.4 A
3.4 A
3.4 A
3.4 A
3.4 A
3.4 A
3.4 A
3.4 A
3.4 A
3.4 A
NA
3.4 A
NA
3.4 A
NA
85—44—9
0.069
28.
A
1(028
Table A
1,1-Dichloroethane trana-
1,2—
Dichloroethane
Hexachlorobutadiene
Hexachloroethane
Pentachloroethane
1,1,
1, 2—Tetrachloroethane
1,1,2,2—Tetrachloroethane
1,1,1,
—Trichloroethane
1,1,
2—Trichloroethane
Tetrachloroethylene
Cadmium
Chromium (Total)
Lead
Nickel
1(029
NA
Chloroform
1, 2—Dichloroethane
1, l—Dichloroethylene
1,1,1—Trichloroethane
Vinyl chloride
1(030
NA
o-Dichlorobenzene
p—Dichlorobenzene
Hexachlorobutadiene
Hexachloroethane
Hexachloropropene
Pentachlorobenzene
Pentachloroethane
1,2,4,5—Tetrachlorobenzene
Tetrachloroethene
1,2,4—Trichlorobenzene
1(031
Table A Arsenic
1(032
NA
Hexachlorocyclopentadiene
Chlordane
Heptachlor
Heptachlor epoxide
K033
NA
Hexachlorocyclopentadiene
77—47—4
1(034
NA
Hexachlorocyclopentadiene
77—47—4
1(035
NA
Acenaphthene
Anthracene
Benz (a)anthracene
Benzo (a) pyrene
Chrysene
Dibenz (a, h)anthracene
Fluoranthene
Pluorene
Indeno(1,2
,
3—cd)pyrene
Cresols
(rn— and p—isomers)
Naphthalene
o—Cresol
Phenanthrene
Phenol
102
1(036
NA
Pyrene
Disulfoton
1(037
NA
Disulfoton
Toluene
1(038
NA
Phorate
129—00—0
298—04—4
298—04—4
108—88—3
298—02—2
0.067
B
8.2
A
0.025
B
0.1
A
0.025
B
0.1
A
0.080
B
28.
A
0.025
0.1
1.
1(040
NA
Phorate
298—02—2
0.025
0.1
A
7439—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
85—01—8
108—95—2
129—00—0
108—88—3
57—12—5
7440—47—32
7439—92—i
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
8
0.059 B
0.039
B
0.067
B
0.080
B
0.32
B
0.028
A
0.2
0.037
NA
14.
A
12.
A
7.3
A
15.
A
3.6
A
14. A
NA
42. A
34. A
3.6 A
36.
A
14.
A
22.
A
1.8 A
NA
NA
1(049
Table A
Anthracene
Benzene
Benzo
(
a) pyrene
Bis(2—ethylhexyl)
phthalate
Carbon disulfide
0.0095
B
2.6 A
8001—35—1
95—94—3
95—50—1
106—46—7
608—93—5
220—82—i
120—83—2
187—65—0
95—95—4
88—06—2
87—86—5
79—01—6
0.055 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
4.4 A
4,4 A
4.4 A
4,4 A
4.4 A
0.38 A
0.34 A
8.2
A
7.6 A
0.68 A
1.9
A
1.7 A
0.001 A
1(041
NA
Toxaphene
1(042
NA
1,2,4,5—Tetrachlorobenzene
o—Dichlorobanzene
p—Dichlorobenzene
Pentachlorobenzene
1,2,
4—Trichlorobenzene
1(043
NA
2,4-Dichlorophenol
2, 6-Dichloropheno
2,4,5-Trichlorophenol
2,4,6-Trichlorophenol
Tetrachiorophenols
(Total)
Pentachlorophenol
Tetrachloroethene
Hexachiorodibenzo—p—
dioxins
Hexachlorodibenzofurans
Pentachlorodibenzo—p-
dioxina
Pentachlorodibenzo furans
Tetrachlorodibenzo-p-
dioxins
Tetrachiorodibeazo furans
1(046
Table
A
Lead
1(048
Table
A
Benzene
Benzo(a)pyrene
Bis (2—ethylhexyl)
phthalate
Chrysene
Di-n-butylphthalate
Ethylbenzene
Fluorene
Naphthalene
Phenanthrene
Phenol
Pyrene
Toluene
Xylene(s)
Cyanides (Total)
Chromium (Total)
Lead
0.000063
0.001
A
0.000063
0.001 A
0.000063
0.001 A
0.000063
0.001 A
0.000063
0.001
A
120—12—7
0.059
B
28.
A
71—43—2
0.14
B
14.
j~,
117—81—7
0.061
B
12.
A
75—150—0
0.28 B
7.3
75—15—0
0.014
B
NA
103
Chrysene
2218—01—9
0.059
a
15. A
2,4-Dimethyl phenol
105—67—9
0.036
B
NA
Ethylbenzene
100—41-4
0.057
B
14. A
Naphthalane
91—20—3
0.059 B
42. A
Phenanthrene
85—01—8
0.059
B
34.
A
Phenol
108—95—2
0.039 B
3.6 A
Pyrene
129—00—0
0.067 B
36.
A
Toluene
108—88—3
0.08 B
14.
A
Xylene(a)
0.32 B
22.
A
Cyanides
(Total)
56—12—5
0.028 A
1.8 A
Chromium (Total)
7440—47-32
0.2
NA
1(050
Table A
Lead
7439—92-1
0.037
NA
Benzo(a)pyrene
50—32—8
0.061 B
12.
A
Phenol
108—95—2
0.039
B
3.6 A
Cyanidea
(Total)
57—12—5
0.028 A
1.8 A
Chromium
(Total)
7440—47-32
0.2
NA
Lead
7439—29-i
0.037
NA
K051
Table A
Acenaphthene
208—96—8
0.059
B
NA
Anthracene
120—12—7
0.059 B
28. A
Benzene
71—43—2
0.14 B
14. A
Benzo(a) anthracene
117—81—7
0.059 B
20. A
Benzo(a)pyrene
117—81—7
0.061 B
12. A
Bia(2—ethylhexyl)
75—15—0
0.28 B
7.3 A
phthalate
Chrysene
2218—01—9
0.059
B
15.
A
Di—n—butyl phthalate
105—67—9
0.057
B
3.6 A
Ethylbenzene
100-41—4
0.057 B
14. A
Fluorene
86—73—7
0.059 B
NA
Naphthalene
91—20-3
0.059
B
42. A
Phenanthrene
85-01—8
0.059
B
34.
A
Phenol
108—95—2
0.039
B
3.6
A
Pyrene
129—00—0
0.067
B
36.
A
Toluene
108—88—3
0.08 B
14.
A
Xylene(s)
0.32
B
22. A
Cyandidea
(Total)
57—12—5
0.028 A
1.8
A
Chromium (Total)
7440—47—32
0.2
NA
Lead
7439—29—1
0.037
NA
Benzene
71—43—2
0.14 B
14.
A
Benzo(a)pyrene
50—32—8
0.061
B
12.
A
1(052
Table A
o—Cresol
95—48—7
0.11 B
6.2 A
p—Creaol
106—44—5
0.77 B
6.2 A
2,4-Dimethylphenol
105—67—9
0.036
B
NA
Ethylbenzene
100—41—4
0.057
B
14.
A
Naphthalene
91—20—3
0.059 B
42.
A
Phenanthrene
85-01—8
0.059 B
34.
A
Phenol
108—95—2
0.039
B
3.6
A
Toluene
108—88—3
0.08 B
14.
A
Xylenes
0.32 B
22.
A
Cyanidea (Total)
56—12—5
0.028 A
1.8 A
Chromium (Total)
7440-47-32
0.2
NA
Lead
7439—92—1
0.037
NA
1(060
NA
Benzene
71—43—2
0.17
B
0.071
A
Benzo(a)pyrene
50—32—8
0.035
B
3.6
A
Naphthalene
91—20—3
0.028
B
3.4 A
Phenol
108—95—2
0.042
B
3.4
A
Cyanidea (Total)
57—12—5
1.9
1.2
1(061
Table
A
Cadmium
7440—43—9
1.61
NA
104
Chromium (Total)
7440—47—32
0.32
NA
Lead
7439—92—1
0.51
NA
Nickel
7440—02—0
0.44
NA
1(062
Table
A
Chromium (Total)
7440—47—32
0.32
NA
Lead
7439—92—1
0.04
NA
Nickel
7440—02—0
0.44
NA
1(069
Tables
Cadmium
7440—43—9
1.6
NA
A&D
Lead
7439—92—1
0.51
NA
1(071
Table A
Mercury
7439—97—6
0.030
NA
K073
NA
Carbon tetrachioride
58—23-5
0.057 B
6.2 A
Chloroform
67—66—3
0.046 B
6.2 A
Hexachloroethane
67—72-1
0.055
B
30.
A
Tetrachloroethene
127—18-4
0.056
B
6.2
A
1,1,1—Trichloroethane
71—55—6
0.054 B
6.2 A
1(083
Table
A
Benzene
71—43—2
0.24
B
6.6
A
Aniline
62—53—3
0.81
B
14.
A
Diphenylaznine
22—39-4
0.52
B
NA
Diphenylnitrosamine
86—30—6
0.40 B
NA
Sum
of
Diphenylarsine
and
NA
14.
A
Diphenylnitrosamine
Nitrobenzene
98—95—3
0.068
B
14.
A
Phenol
108—95—2
0.039
5.6
A
Cyclohexanone
108—94-1
0.36
30.
A
Nickel
7440-02—0
0.47
NA
1(084
NA
Arsenic
7440—38—2
0.79
NA
KOSS
NA
Benzene
71—43—2
0.14 B
4.4 A
Chlorobenzene
108—90—7
0.057 B
4.4 A
o—Dichlorobenzene
95—50-1
0.088
B
4.4 A
m—Dichlorobenzene
541—73—1
0.036 B
4.4 A
p—Dichlorobenzene
106—46—7
0.090 B
4.4 A
i,2,4—Trichlorobenzene
120—82—1
0.055 B
4.4 A
1,2,4,5—Tetrachiorobenzene 95—94—3
0.055 B
4.4 A
Pentachlorobenzene
608—93-5
0.055
4.4 A
Hexachlorobenzene
118—74—1
0.055
B
4.4 A
Aroclor 1016
12674—11—2
0.013
B
0.9 A
Aroclor
1221
11104—28—2
0.014
B
0.92
A
Aroclor
1232
21141—16—5
0.013
B
0.92
A
Aroclor 1242
53469—21—9
0.017
B
0.92 A
Aroclor
1248
12672—29—6
0.013
3
0.92
A
Aroclor 1254
11097—69—1
0.014 B
1.8 A
Aroclor
1260
11096—82—5
0.014
B
1.8
A
1(086
Table A
Acetone
67—64—1
0.28
160.
A
Acetophenone
96—86—2
0.010
9.7 A
Bis(2-ethylhexyl)phthaiate
117—81—7
0.28 B
28. A
n—Butyi alcohol
71—36—3
5.6
2.6 A
Butylbenzylphthalate
85—68—7
0.017
B
7.9 A
cyclohexanone
108-94-1
0.36
NA
1,2—Dichlorobenzene
95—50—i
0.088
6.0 A
Diethyl phthalate
84—66—2
0.20
B
28. A
Dimethyl phthalate
131—11—3
0.047
B
28. A
Di—n—butyi
phthaiate
84—74—2
0.057
B
28.
A
Di—n—od~y1 phthalate
117—84—0
0.017
B
28.
A
Ethyl
acetate
141—78—6
0.34
B
33.
A
105
100—41—4
67—56—i
108—10—1
78—93—3
75—09—2
91—20—3
98—95—3
108—88—3
71—55—6
79—01—6
(Total)
57—12—5
7440—47—32
7439—92—i
208—96—8
71—43—2
218—01—9
206—44—0
193—39—5
91—20—3
85—01—8
108—88—3
7439—92—1
85—44—9
630—20—6
79—34—6
127—18—4
79—00—5
79—01—6
67—72—i
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
0.057
B
5.6 B
0.14
0.28
0.089
B
0.059
B
0.068
B
e—0.080~
e—0.054~
e—0.054.~
e—0.32 B
1.9
0.32
0.037
e—0
.
0S9~
e—0.14
B
e—0.059
e—0.068~
e—0.0055...~
e—0.059~
e—0.
059~
e—O.08
B
e—0.32
B
0.037
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
0.055
0.055
6.0
A
NA
33.
A
36.
A
33. A
3.1 A
14. A
a—2 8
.~
~-5.
6,~
~—S.6~
a—28.
_.~
1.5
NA
NA
3.4
a—0. 071~.~
4_~
a—3.
4_~
a—3
.
4_~
4_~
e—3
.
4_..~
a—0.65
A
NA
a—5.6
A
a—5.6
A
e—6.0
A
e—6.0
A
a—5.6
A
a—28.
A
e~-5.6
A
a—5.6
A
a—5.6
A
e—6.0
A
e—6.O
A
e—5.6
A
a—5.6
A
fr-5.6 A
a—19.
A
1(097
NA
Hexachlorocyclopentadiene
Chlordane
Heptachlor
Heptachlor epoxide
77—47—4
57—74—9
76—44—8
1024—57—3
e—0. 057~
e—0
.
003 3_,~
e—0. 0012~
e—0. 016,~
2.4
e—0.26
A
a—0.066A
a—0.066A
1(098
NA
Toxaphene
8001—35—1
e—0.
0095..i
e—2
.
6~
1(099
NA
2,4—Dichlorophenoxyacetic
acid
Hexachlorodibenzo—p—
Ethylbenzene
Methanol
Methyl isobutyl ketone
Methyl ethyl ketone
Methylene chloride
Naphthalene
Nitrobenzene
Toluene
1,1, 1-Trichloroethane
Trichloroethylene
Xylene(s)
(Total)
Cyanides
(Total)
Chromium
(Total)
Lead
1(087
Table
A
Acenaphthalene
Benzene
Chrysene
Pluoranthene
Indeno
(1,2,3—cd)
pyrene
Naphthalene
Phenanthrene
Toluene
Xylenes
Lead
1(093
~
Phthalic anhydride
(measured as Phthalic
acid)
1(094
NA
Phthalic anhydride
(measured as Phthalic
acid)
1(095
NA
1,1,l,2—Tetrachloroethane
1,1,2,2—Tetrachloroethane
Tetrachloroethene
1,1,2-Trichloroethane
Trichloroethylene
Hexachloroethane
Pentachloroethane
1(096
NA
1,1,1,2—Tetrachloroethane
1, 1,2,2—Tetrachloroethane
Tetrachloroethene
1,1,2—Trichloroethane
Trichloroethene (Tn-
chloroethvlene)
1,3—Dichlorobenzene
Pentachloroethane
1,2,4—Tnichlorobenzene
85—44—9
0.069
a—28. A
e—28. A
94—75—7
e—1.Q_~
e—0. 001~
e—0. OOlA
106
dioxins
Hexachlorodibenzofurans
Pentachlorodibenzo-p-
dioxins
Pentachlorodibenzofurans
Tetrachlorodibenzo-p—
dioxina
Tetrachlorodibenzofurana
&—0.001_~
a—0.0O1~
e—0.001_~
e—0. 0O1_~
e—O. 001
e—0.001~
,5r—0.001_~~
fr—0.OOi_~
fr-C. 001~
a—C. 00i~
1(102
Table A
o-Nitrophenol
Arsenic
Cadmium
Lead
Mercury
7440—38—2
7440—43—9
7439—92—1
7439—97—6
a—0.
028~
0.79
0.24
0.17
0.082
a—i3.
A
NA
NA
NA
NA
1(115
Table A
Nickel
62—53—3
71—43—2
51—28—5
98—95—3
108—95—2
62—53—3
71—43—2
51—28—5
98—95—3
108—95—2
57—12—5
a—4.5 A
a—O.15 A
a—C. 6i~
-a—C. 073~
e—1.4 A
a-4.5 A
fr-0.i5
A
a—0.61 A
e—O. 073~
a—i.4
A
2.7
7440—02—3-Q
0.47
5.6
a—6.0~
a—5
.
6~
A
~a—5.6
A
a-6.O
A
e—5.6
A
a—S
.
6~
a—5.6
A
e—1.8
A
1(100
Table
A
Cadmium
7440-43-9
1.6
NA
Chromium (Total)
7440—47-32
0.32
NA
Lead
7439—92—1
0.51
NA
1(101
NA
o—Nitroaniline
Arsenic
Cadmium
Lead
Mercury
7440—38—2
7440—43-9
7439—92-1
7439—97-6
e—0.27~
0.79
0.24
0.17
0.082
e—14....~
NA
NA
NA
NA
1(103
~
Aniline
Benzene
2, 4—Dinitrophenol
Nitrobenzene
Phenol
1(104
ri~~
Aniline
Benzene
2, 4—Dinitrophenol
Nitrobenzene
Phenol
Cyanidea
(Total)
1(105
NA
Benzene
Chlorobenzene
o—Dichlorobenzerie
p—Dich lorobenzene
2,4,5—Trichlorophenol
2,4,6—Tnichlorophenol
2-Chlorophenol
Phenol
1(106
Tables
Mercury
A&D
71—43—2
0.14
a—4.4A
108—90—7
0.057
a—4.4A
95—50—1
0.088
a—4.4A
106—46—7
0.090
a-4.4A
95—95—4
0.18
a—4.4A
88—06—2
0.035
a—4.4A
95—57—8
0.044
a—4.4A
108—95—2
0.039
e—4.4A
7439—97—6
0.030
NA
NA
Kill
NA
2,4—Dinitrotoluene
2,6—Dinitrotoluene
121—14—2
606—20—2
0.32
0.55
e—140.~
*—28.~
K1l7
Ethylene dibromide
Methyl bromide
Chloroform
106—93—4
74—83—9
67—66—3
0.028
0.11
0.046
a-15.~
a—i5......~
e—5.6A
K118
Ethylene
dibromide
Methyl
bromide
Chloroform
106—93—4
74-83-9
67—66—3
0.028
0.11
0.046
a—15.~
a-15.~
‘a—5.6A
107
1(131
~
Methyl bromide
74—83—9
0.11
1(132
~
Methyl
bromide
74—83—9
0.11
1(136
~
Ethylene dibromide
106—93—4
0.028
Methyl bromide
74—83—9
0.11
Chloroform
67-66—3
0.046
a
Treatment standard. ~or this erganie senatituent were eete~lishedbased
upon incineration in units operated in accordance with the technical
requiromonto of 36
Ill.
Mm.
Cede 734.Subpart 0 er 725.Subpart 0,
or
b-aocd
upon
-eoinbuotien
in fuel
oubotitution units operating in aooordanco
with applicable technical requirements. A facility may certify
compliance with thooe treatment standardo ascending to provisiono in
Lootion
728.107.
Based on analysis of oompooite samples.
As analysed
using
SW
846
Method
9010~ sample
sises
O..5-i0~ distillation
timoi
ono hour to one hour and fiftocn minutoci.
TABLE
B
(CCW):
P
AND
U LISTED WASTES
CAS No.
for
Concentra-
Commercial
Regulated
Regulated
Concentra-
tion (mg/L)
Waste Chemical
See
Hazardous
Hazardous
tion (mg/L)
Nonwaste—
Code
Name
Also
Constituent
Constituent Wastewaters
waters
P004
Aldnin
Aldnin
309—00—2
O.21~
0.066~
POlO
Arsenic
acid
Table
A
Arsenic
7440—38—2
0.79
NA
POll
Arsenic
Table A Arsenic
7440-38—2
0.79
NA
pentoxide
P012
Arsenic
Table
A
Arsenic
7440—38—2
0.79
NA
trioxide
P013
Barium
Table A Cyanides
57—12—5
1.9
110.
cyanide
(Total)
Cyanides
57—12—5
0.1
9.1
(Amenable)
P020
2—aec—Butyl—~
2—sec—Butyl—
88—85—7
0.066
~-
2.5~
4, 6—dinitro-
4, 6—dinitro—
phenol
phenol
(Dinoseb)
(Dinoseb)
P021
Calcium
Cyanides
57—12—5
1.9
110.
cyanide
(Total)
Cyanidea
57—12—5
0.1
9.1
(Amenable)
P022
Carbon
di-
Table D
Carbon di—
75—15—0
0.014
NA
sulfide
sulfide
P024
p—Chloro-
!i~
p—Chloro—
106—47—8
0.46
~
aniline
aniline
108
P029
Copper
Cyanides
57-12-5
1.9
110.
cyanide
(Total)
Cyanides
57—12—5
0.1
9.1
(Amenable)
P030
Cyanides
Cyanides
57—12—S
1.9
110.
(soluble
(Total)
salts and
complexes)
Cyanides
57—12—5
0.1
9.1
(Amenable)
P036
Dichloro—
Table A
Arsenic
7440—38—2
0.79
NA
phenylarsine
P037
Dieldnin
Dieldrin
60—57—1
~
0.017.~
0.l3~~
P038
Diethyl—
Table A Arsenic
7440—38—2
0.79
NA
arsine
P039
Disulfoton
NA
Disulfoton
298—04—4
0.017
0.1
A
P047
4,6—Dinitro—NA
4,6—Dinitro—
534—52—4
0.28
B
160. A
o—cresol
o—creaol
P048
2,4—Dinitro—NA
2,4—Dinitro—
51—28—5
0.12
B
160. A
phenol
phenol
P050
Endosulfan
NA
Endosulfan
I
939—98—8
0.023
B
0.066
A
Endosulfan
II
33213—6—5
0.029
B
0.13
A
Endosulfan
1031—07—8
0.029
B
0.13
A
sulfate
P051
Endrin
NA
Endnin
72-20-8
0.0028
B
0.13 A
Endrin
7421—93—4
0.025
B
0.13
A
aldehyde
P056
Fluoride
Table
0
Fluoride
18694—48-8
35.
NA
P059
Heptachior
NA
Heptachlor
76—44—8
0.0012
B
0.066
A
Heptachlor
1024—57—3
0.016
B
0.066
A
epoxide
P060
Isodnin
NA
Isodrin
465—73—6
0.021
B
0.066
A
P063
Hydrogen
NA
Cyanidea
57—12—5
1.9
110.
cyanide
(Total)
Cyanides
57—12—5
0.10
9.1
(Amenable)
P065
Mercury
Tables
Mercury
7439-97-6
0.030
NA
fulminate
A
&
0
P071
Methyl
NA
Methyl
298—00-0
0.025
0.1 A
parathion
parathion
P073
Nickel
Table A Nickel
7440—02—0
0.32
NA
carbonyl
P074
Nickel
Table A
Cyanidea
57-12—5
1.9
110.
cyanide
(Total)
Cyanides
57—12—5
0.10
9.1
109
(Amenable)
Nickel
7440—02—0
0.44
NA
P077
p—Nitro—
NA
p—Nitro-
100—01—6
0.028 B
28.
A
aniline
aniline
P082
N—Nitrosodi-Table D
N-Nitrosodi—
62—75-9
0.40 B
NA
methylamine
methylamine
P089
Parathion
NA
Parathion
56—38—2
0.025
0.1 A
P092
Phenylmer—
Tables
Mercury
7439—97—6
0.030
NA
cury acetate A & D
P094
Phorate
NA
Phorate
298—02—2
0.025
0.1 A
P097
Faxnphur
NA
Famphur
52—85—7
0.025
0.1 A
P098
Potassium
NA
Cyanides
57-12—5
1.9
110.
cyanide
(Total)
Cyanidea
57—12—5
0.10
9.1
(Amenable)
P099
Potassium
Table A
Cyanides
57—12—5
1.9
110.
silver
(Total)
cyanide
Cyanides
57—12—5
0.1
9.1
(Amenable)
Silver
7440—22—4
0.29
NA
P101
Ethyl
cyan—
NA
Ethyl
cyanide
107—12—0
0.24 B
360. A
ide (Pro-
(Propane-
panenitrile)
nitnile)
P103
Selenourea
Table A
Selenium
7782—49—2
1.0
B
NA
P104
Silver
Table A
Cyanidea
57—12—5
1.9
110.
cyanide
(Total)
Cyanides
57—12—5
0.10
9.1
(Amenable)
Silver
7440—22—4
0.29
NA
P106
Sodium
NA
Cyanides
57—12—5
1.9
110.
cyanide
(Total)
Cyanides
57—12—5
0.10
9.1
(Amenable)
P110
Tetraethyl
Tables
Lead
7439—92—1
0.Ô40
NA
lead
A&D
P113
Thallic
Table 0
Thallium
7440—28—0
0.14
B
NA
oxide
P114
Thallium
Table A
Selenium
7782—49—2
1.0
NA
selenite
P115
Thallium(I)
Table 0
Thallium
7440—28—0
0.14 B
NA
sulfate
P119
Ammonia
Table
D
Vanadium
7440—62—2
28.
B
NA
vanadate
110
P120
Vanadium
Table C
Vanadium
7440—62-2
28.
B
NA
pentoxide
P121
Zinc cyanide NA
Cyanide.
57—12—5
1.9
110.
(Total)
Cyanides
57—12—5
0.10
9.1
(Amenable)
P123
Toxaphene
NA
Toxaphene
6001-35-1
0.0095 B
1.3 A
0002
Acetone
NA
Acetone
67-64-1
0.28
160. A
U003
Acetonitrile Table C
Acetonitnile
75—05—8
0.17
0.17
0004
AcetophenoneNA
Acetophenone
98—86-2
0.010 A
9.7 A
U005
2—Acetyla-
NA
2—Acetylami—
53—96—3
0.059 B
140. A
minofluorene
nofluorene
U009
Acrylo—
NA
Acrylonitnile
107—13—i
0.24
A
84.
A
nitrile
0012
Aniline
NA
Aniline
62—53—3
0.81
14.
A
0016
Benz(a)—
NA
Benz(a)—
56—55—3
0.059 B
8.2 A
anthracene
anthracene
U0l9
Benzene
NA
Benzene
71—43-2
0.14 B
36.
A
U022
Benzo(a)—
NA
Benzo(a)—
50—32—8
0.061 B
8.2 A
pyrene
pyrene
U024
Bie(2—chlor— NA
Bie(2—chloro—
111—91—1
0.036
7.2 A
oethoxy)met-
ethoxy)meth-
hane
ane
U025
Bia(2—
NA
Bis(2—chloro—
111—44—4
0.033
7.2
A
chloroethyl)
ethyl)
ether
ether
U027
Bis(2—chlor—NA
Bia(2—chloro—
39638—32—9
0.055
7.2 A
oiaopropyl)
isopropyl)
ether
ether
0028
Bis(2—ethyl— NA
Bis(2—ethyl—
117—81—7
0.28 A
28. A
hexyl)-
hexyl)—
phthalate
phthalate
0029
BromomethaneNA
Bromomethane
74—83—9
0.11 A
15. A
(Methyl
(Methyl
bromide)
bromide)
0030
4-Bromo-
NA
4—Bromophenyl
101-55-3
0.055 A
15. A
phenyl
pheny.
ether
phenyl ether
0031
n—Butyl
NA
n—Butyl
71—36—3
5.6
2.6 A
alcohol
alcohol
0032
Calcium
Table
A
Chromium
7440—47-32
0.32
NA
chroznate
(Total)
111
U036
Chlordane
(alpha and
gamma)
0037
Chloro—
benzane
U038
Chloro—
benzilate
U039
p-Chloro-m-
cresol
U043
Vinyl
chloride
U045
Chlorometh-
ane
(Methyl
chloride)
0047
2—Chloro-
naphthalene
U048
2—Chloro-
phenol
U050
Chrysene
U051
Creosote
UO63
Dibenzo(a,
h) anthracene
NA
Chlordane
(alpha
and
gamma)
Table C
Chloro—
benzilate
NA
p-Chloro-m-
cresol
NA
Vinyl
chloride
Chloroform
NA
Chlorornethane
(Methyl
chl-
oride)
NA
2-Chloro-
naphthalene
NA
2-Chloro-
phenol
NA
Chrysene
Table
A
Naphthalene
Pentachloro—
phenol
Phenanthrene
Pyrene
Toluene
Xylenes
(Total)
Lead
Cresola
(in—
and p-iso-
mers)
NA
o,p’-DDD
p,p,-000
NA
Dibenzo(a,h)—
anthracene
85—01—8
129—00—0
108—88—3
7439—92—1
NA
Chlorobenzene
108-90-7
0044
Chloroform
NA
S10—1S—6
59—50—7
75—01—4
67—66—3
74—87—3
91—58--7
95—57—8
218—01—9
B
B
95—48—7
0.11
B
57—74—9
0.00033
0.13 A
0.057
B
5.7 A
0.10 B
NA
0.018 B
14. A
0.27
B
33. A
0.046
B
5.6
A
0.19
B
33.
A
0.055
B
5.6
A
0.044
B
5.7 A
0.059
B
8.2
A
91—20—3
87—86—5
0.031
0.18
1.5
A
7.4
A
0.031
0.028
0.028
0.032
1.5 A
28.
A
33. A
NA
0.037
NA
5.6 A
0.77
B
3.2
A
NA
o—Cresol
U052
Creaols
(Cresylic
acid)
U057
Cyclohexan-
one
U060
DDD
U06l
DDT
Table D
Cyclohexanone
108—94-i
0.36
NA
NA
o,p’—DDT
p,p’—DDT
o,p’—DDD
p,p’-DDD
o,p’—DDE
p, p ‘-DDE
53—19—0
72—54—8
0.023
B
0.023
B
0.087
0.087
A
A
789—02—6
50—29—3
53—19—0
72—54—8
3424—82—6
72—55—9
0.0039
B
0.0039
B
0.023
B
0.023
B
0.031
B
0.031 B
0.087
0.087
0.087
0.087
0.087
0.087
A
A
A
A
A
A
53—70—3
0.055
B
8.2
A
112
0066
1,2—Dibromo—NA
1,2—Dibromo-
96—12—8
0.11 B
15. A
3—chloro—
3—chloro—
propane
propane
U067
1,2—Dibromo—NA
l,2—Dibromo-
106—93—4
0.028 B
15. A
ethane
ethane
(Ethylene
(Ethylene di-
dibromide)
bromide)
0068
Dibromoeth-
NA
Dibromoethane
74-95-3
0.11 B
15. A
ane
0069
Di—n—butyl
NA
Di—n—butyl
84—74—2
0.057 A
28.
A
phthalate
phthalate
0070
o—Dichloro—
NA
o—Dichloro—
95—50—1
0.088 B
6.2 A
benzene
benzene
U071
m—Dichloro—
NA
m-Dichloro—
541—73—1
0.036
6.2 A
benzene
benzene
0072
p—Dichloro—
NA
p-Dichloro—
104—46—7
0.090 B
6.2 A
benzene
benzene
0075
Dichloro—
NA
Djchlorodi-
75—71—8
0.23 B
7.2 A
difluoro—
fluaromethane
methane
U076
3.,l—Di—
NA
1,1—Dichioro-
75—34-3
0.059
B
7.2
A
chloroethane
ethane
U077
1,2—Di—
NA
1,2—Dichloro—
107—06—2
0.21
B
7.2
A
chloroethane
ethane
0078
1,1—Dichlor-NA
1,1—Dichloro—
75—35—4
0.025
B
33.
A
oethylene
ethylene
0079
1,2—Dichlor—NA
trans—1,2—Di—
156—60—5
0.054 B
33.
A
oethylene
chioroethyl—
erze
U080
Methylene
NA
Methylene
75—08-2
0.089 B
33. A
chloride
chloride
U081
2,4—Di—
NA
2,4—Dichioro-
120—83—2
0.044 B
14. A
chiorophenol
phenol
0082
2,6—Dichlor-NA
2,6—Dichloro—
87—65—0
0.044
B
14. A
ophenol
phenol
0083
l,2—Dichlor— NA
1,2—Dichloro—
78—87—5
0.85
B
18. A
opropane
propane
U084
1,3—Dichlor—NA
cis—1,3—Dich—
10061—01—5
0.036
B
18. A
opropene
loropropylene
trans—1,3—Di—
10061—02—6
0.036
8
18.
A
chloropropy1—
ene
U088
Diethyl
NA
Diethyl
84-66—2
0.2
28.
A
phthalate
phthalate
113
0093
p—Dimethyl-
Table
D
aminoazoben—
0101
2,4—Di—
NA
methylphenol
U102
Dimethyl
NA
phthalate
0105
2,4—Dinitro— NA
toluene
U106
2,6—Dinitro—
NA
toluene
0107
Di-n—octyl
NA
phthalate
U108
1,4—Dioxane
NA
U111
Di-n-propyl- NA
nitrosoamine
U112
Ethyl
NA
acetate
U1l7
Ethyl
ether
NA
0118
Ethyl
meth-
NA
acrylate
0120
Pluoranthene NA
0121
Trichloro—
NA
monofluoro—
methane
0127
Hexachloro-
NA
benzene
0128
Hexachloro-
NA
butadiene
0129
Lindane
NA
0130
Hexachloro-
cyclopenta-
diene
U131
Hexachloro-
ethane
p—Dimethyl-
aminoazo—
benzene
2, 4—Dimethyl—
phenol
Dimethyl
phthalate
2,4—Dinitro—
toluene
2, 6—Dinitro-
toluene
Di—n—octyl
phthalate
1, 4—Dioxane
Di-n-propyl-
nitrosoamine
Ethyl
acetate
zene
60—11—7
0.13
B
NA
105—67—9
0.036 B
14. A
131—11—3
0.047
28. A
121—14—2
0.32
B
140. A
606—20—2
0.55
B
28. A
117—84—0
0.017
28. A
123—91—1
0.12
B
170.
A
621—64—7
0.40 B
14. A
141—78—6
0.34 B
33. A
0.12
B
160.
A
0.14
B
160.
A
0.068
B
8.2
A
0.020
B
33.
A
0.055
B
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—85—7
319—86—8
58—89—9
Ethyl
ether
Ethyl
methac-
rylate
Pluoranthene
Trichloro-
monofluoro—
methane
Hexachloro—
benzene
Hexachloro—
butadiene
alpha-BHC
beta-BHC
Delta—BHC
gamma-BHC
(Lindane)
NA
Hexachloro—
cyclopenta-
diene
NA
Hexachloro—
ethane
Table
C
Fluoride
0.00014
B
0. 00014
B
0.023
B
0.0017
B
0.66
A
0.66 A
0.66 A
0.66 A
3.6A
77—47—7
0.057
B
67—72—1
0.055
B
28.
A
16964—48—8
35.
NA
0134
Hydrogen
fluoride
114
0136
Cacodylic
Table
A
Arsenic
7440—38-2
0.79
NA
acid
0137
Indeno—
NA
Indeno(1,2,3—
193—39—5
0.0055 B
8.2 A
(1,2,3—c,d)—
c,d)pyrene
pyrene
0138
lodomethane
NA
Iodomethane
74-88-4
0.19 B
65. A
0140
Isobutyl
NA
Isobutyl
78—83-1
5.6
170. A
alcohol
alcohol
0141
Isosafrole
NA
Isosafrole
120—58—1
0.081
2.6 A
0142
Kepone
NA
Kepone
143-50-8
0.0011
0.13 A
0144
Lead acetate Table A
Lead
7439—92-1
0.040
NA
0145
Lead
Table A
Lead
7439-92-1
0.040
NA
phosphate
0146
Lead sub—
Table A
Lead
7439—92—1
0.040
NA
acetate
Ul51
Mercury
Tables
Mercury
7439-97-6
0.030
NA
A&D
0152
Methacrylo-
NA
Methacryloni-
126-98-7
0.24
B
84. A
nitrile
trile
U154
Methanol
NA
Methanol
67-56-1
5.6
NA
0155
Metha—
NA
Methapyrilene
91-80-5
0.081
1.5
A
pyrilene
U157
3—Methyl—
NA
3—Methylchol—
56—49—5
0.0055 B
15. A
cholanthrene
anthrene
0158
4,4’—Methyi—NA
Methylenebis—
101—14—4
0.50
B
35. A
enebis (2-
(2—chloro-
chloro—
aniline)
aniline)
0159
Methyl ethyl NA
Methyl ethyl
78—93-3
0.28
36. A
ketone
ketone
0161
Methyl iso-
NA
Methyl
iso—
108—10-1
0.14
33.
A
butyl ketone
butyl ketone
U162
Methyl meth-NA
Methyl meth-
80—62-6
0.14
160. A
acrylate
acrylate
0165
Naphthalene
NA
Naphthalene
91—20-3
0.059
B
3.1
A
U168
2—Naphthyl—
Table 0
2—Naphthyl-
91-59-8
0.52 B
NA
amine
amine
0169
NitrobenzeneNA
Nitrobenzene
98—95—3
0.068 B
14. A
0170
4—Nitro-
NA
4—Nitrophenol
100—02—7
0.12 B
29. A
phenol
115
U172
N—Nitrosodi-NA
N—Nitrosodi-
924-16-3
0.40
B
17.
A
n—butylamine
n-butylamine
0174
N—Nitrosodi-NA
N-Nitrosodi-
55-18-5
0.40 B
28.
A
ethylamine
ethylamine
0179
N—Nitroso—
NA
N—Nitroso—
100—75—4
0.013
B
35.
A
piperidine
piperidine
0180
N—Nitroso—
NA
N—Nitroso—
930—55—2
0.013
B
35. A
pyrrolidine
pyrrolidine
0181
5—Nitro—o-
NA
5—Nitro-o-
99-55—8
0.32
B
28.
A
toluidine
toluidine
U183
Pentachioro-NA
Pentachloro-
608-93—5
0.055
B
37.
A
benzene
benzene
U185
Pentachloro-NA
Pentachloro-
82—68—8
0.055
B
4.8 A
nitrobenzene
nitrobenzene
U187
Phenacetin
NA
Phenacetin
62—44—2
0.081
16.
A
U188
Phenol
NA
Phenol
108—95—2
0.039
6.2 A
0190
Phthalic
NA
Phthalic
85-44—9
0.069
28. A
anhydride
anhydride
(measured as
(measured as
Phthalic
Phthalic
acid)
acid)
0192
Pronarnide
NA
Pronaniide
23950—58—5
0.093
1.5 A
0196
Pyridine
NA
Pyridine
110—86—1
0.014
B
16.
A
U203
Safrole
NA
Safrole
94—59-7
0.081
22.
A
0204
Selenium
Table
A
Selenium
7782—49—2
1.0
NA
dioxide
0205
Selenium
Table A
Selenium
7782-49—2
1.0
NA
sulfide
U207
1,2,4,5—
NA
1,2,4,5—
95—94—3
0.055
B
19.
A
Tetrachloro—
Tetrachloro—
benzene
benzene
U208
1,1,1,2—
NA
1,1,1,2—
630—20—6
0.057
42. A
Tetrachloro—
Tetrachloro—
ethane
ethane
0209
1,1,2,2—
NA
1,1,2,2—
79—34—5
0.057 B
42. A
Tetrachloro-
Tetrachloro-
ethane
ethane
U210
Tetrachloro—NA
Tetrachloro-
127—18—4
0.056 B
5.6 A
ethylene
ethylene
0211
Carbon tet-
NA
Carbon tetra—
56—23—5
0.057 B
5.6 A
rachloride
chloride
116
U214
Tallium(I)
Table
C
Thallium
7440—28—0
0.14
B
NA
acetate
U215
Thallium(I)
Table C
Thallium
7440—28—0
0.14
8
NA
carbonate
0216
Thallium(I)
Table D
Thallium
7440—28—0
0.14
B
NA
chloride
0217
Thallium(I)
Table C
Thallium
7440—28—0
0.14
B
NA
nitrate
0220
Toluene
NA
Toluene
108-88-3
0.080
B
28. A
U225
Tribromo—
NA
Tribromo—
75—25—2
0.63
B
15.
A
methane
methane
(Bromoform)
(Bromoform)
0226
1,1,1—Tn—
NA
1,1,1—Tn—
71—55—6
0.054
B
5.6
A
chloroethane
chioroethane
U227
1,1,2—Tn—
NA
1,1,2—Tn—
79—00—5
0.054
8
5.6 A
chloroethane
chloroethane
0228
Tnichloro-
NA
Tnichloro—
79-01—6
0.054
B
5.6 A
ethylene
ethylene
0235
tnis—(2,3—
NA
tnis—(2,3—Di—
126—72—7
0.025
0.10 A
Dibromoprop-
bromopropyl)
-
yl)—
phosphate
phosphate
0239
Xylenes
NA
Xylene
0.32 B—B
28. A
0240
2,4—Dichlor—NA
2,4—Dichloro—
94—75—7
0.72
10.
A
ophenoxya—
phenoxyacetic
cetic
acid
acid
0243
Hexachloro—
NA
Hexachioro—
1888—71—7
0.035
B
28.
propene
propene
0247
MethoxychlorNA
Methoxychior
72-43—5
0.25 B
0.18 A
A
Treatment
standards
for
this
organic
constituent
were
established
based
upon
incineration
in
units
operated
in
accordance
with
the
technical
requirements of 35 Ill. Adm. Code 724.Subpart
Q, or
725.Subpart
Q,
or
based upon combustion in fuel substitution units operating in accor-
dance with applicable technical requirements.
A facility may certify
compliance with these treatment standards according to provisions in
Section 728.107.
B
Based on analysis of composite samples.
C
As analyzed using SW—846 Method 9010 or 9012;
sample size:
log;
distillation time:
one hour and fifteen minutes.
R
Reserved.
NA
Not Applicable.
(Source:
Amended at 18 Ill. Reg.
_________,
effective
_____________________
117
Section
728.Table
C
Technology—Based
Standards
by
RCRA
Waste
Code
Technology
Technology
Code,
Code,
Non—
Waste Descriptions
Waste
Waste—
waste—
end/or Treatment
Codes
See Also
CAB No.
waters
waters
Subcategory
DOOl
Tables A
NA
DEACT, and
DEACT,
and
All descriptions based
&
B
meet
F039;
meet
P039;
on
35
Ill.
Adm.
Code
or
FSUBS;
or
PSUBS;
721.121, except for the
RORGS; or
RORGS; or
Section 721.121(a) (1)
INCIN
INCIN
High TOC subcategory,
managed in non—CWA/non—
CWA-equivalentmon—Class
I SDWA systems
DOOl
NA
NA
DEACT
DEACT
All descriptions based
on
35
Ill. Adm. Code
721.121, except for the
Section 261.121(a) (1)
High TOC subcategory,
managed
in
CWA,
CWA—
equivalent,
or
Class
I
SDWA systems
COOl
NA
NA
NA
FSUBS;
All descriptions
based
RORGS;
or
on
35
Ill.
Adm. Code
INCIN
721.l2l(a)(1)—High TOC
Ignitable
Liquids
Sub—
category——Greater than
or
equal
to
10
total
organic
carbon
D002
Tables
A
NA
DEACT and
DEACT and
Acid,
alkaline,
and
&
B
meet
P039
meet
F039
other
subcategory
based
on
35
Ill.
Adm. Code
721.122 managed in non—
CWA/non-CWA—equivalent
/
non-Class
I SDWA systems
D002
NA
NA
DEACT
DEACT
Acid,
alkaline,
and
other subcategory based
on 35
Ill.
Adm.
Code
721.122 managed in CWA,
CWA-equivalent,
or
Class
I
SDWA
systems
0003
NA
NA
DEACT
(but
DEACT
(but
Reactive sulfides based
not
in-
not
in—
on
35
Ill.
Adm.
Code
eluding
cluding
721.123(a)
(5)
dilution
dilution
as
a
sub—
as
a
sub-
stitute
stitute
for
ade—
for
ade-
quate
quate
treatment)
treatment)
D003
NA
NA
DEACT
DEACT
Explosives
based
on
35
Ill. Adm. Code 721.123
(a)(6),
(7)
and
(8)
118
0003
NA
NA
NA
DEACT
Water reactivee based on
35
Ill.
Adm. Code
72l.l23(a)(2),
(3)
and
(4)
0003
NA
NA
DEACT
DEACT
Other reactives based on
35
Ill. Adm. Code
721. 123 (a)
( 1)
0006
NA
7440-43-9
NA
RTHERM
Cadmium-containing bat-
teries
D008
NA
7439-92-1
NA
RLEAD
Lead acid batteries
(Note:
This
standard
only applies to lead
acid batteries that are
identified as RCRA
hazandous wastes and
that are
not
excluded
elsewhere from
regulation
under
the
land disposal re-
strictions of this Part
or exempted under other
regulations
(see 35
Ill.
Adm.
Code
726.180).)
D009
Tables
A
7439-97-6
NA
IMERC; or
Mercury:
(High
Mercury
&
B
R14ERC
Subcategory—-greater
than on equal to 260
mg/kg
total
Mercury—-
contains mercury and or—
ganics (and are
not
incinerator residues))
D009
Tables
A
7439-97—6
NA
RMERC
Mercury:
(High
Mercury
&
B
Subcategory——greaten
than or equal to 260
mg/kg total Mercury--
inorganics
(including
incinerator residues and
residues
from
RMERC))
D0l2
Table
B
72-20—8
BIODG;
or
NA
Endnin
INCIN
D013
Table
B
58-89—9
CARBN;
or
NA
Lindane
INCIN
0014
Table B
72-43-5
WETOX;
on
NA
Methoxychion
INCIN
D015
Table B
8001-35—1
BIODG;
or
NA
Toxaphene
INCIN
0016
Table
8
94—75-7
CHOXO;
NA
2,4—D
BIODG; or
INCIN
0017
Table
B
93-72-1
CHOXO;
or
NA
2,4,5-TP
INCIN
119
P005
Tables
A
79—46—9
(WETOX or
INCIN
2—Nitropropane
&
B
CHOXO)
fb
CARBN;
or
INCIN
P005
Tables A
110—80—5
BIODG; or
INCIN
2—Ethoxyethanol
& B
INCIN
P024
Tables A
NA
INCIN
INCIN
1(025
NA
NA
LLEXT fb
INCIN
Distillation bottoms
SSTRIP
fb
from the production of
CARBN; or
nitrobenzene by the
INCIN
nitration of benzene
1(026
NA
NA
INCIN
INCIN
Stripping
still
tails
from
the
production
of
methyl ethyl
pynidines
1(027
NA
NA
CARBN;
or
PSUBS;
or
Centrifuge
and
INCIN
INCIN
distillation
residues
from toluene di—
isocyanate production
1(039
NA
NA
CARBN;
or
PSUBS;
on
Filter cake from the
INCIN
INCIN
filtration of diethyl—
phosphorodithioc acid in
the production of phor—
ate
1(044
NA
NA
DEACT
DEACT
Wastewater treatment
sludges from the manu-
facturing and processing
of explosives
K045
NA
NA
DEACT
DEACT
Spent carbon from the
treatment of wastewater
containing
explosives
1(047
NA
NA
DEACT
DEACT
Pink/ned water from TNT
operations
K069
Tables A
NA
NA
RLEAD
Emission
control
dust/
&
B
sludge from secondary
lead smelting:
Non—
Calcium Sulfate Sub—
category
K106
Tables A
NA
NA
RMERC
Wastewater treatment
& B
sludge from the mercury
cell
process
in
chlorine
production:
(High
Mercury Subcategory—
greater
than
or
equal
to
260 mg/kg total mercury)
120
1(107
NA
NA
INCIN;
on
INCIN.
Column bottoms from
CHOXD
fb,
product
separation
from
CARBN;
or
the production of 1,1-
BIODG
fb
dimethylhydrazine
(UDMH)
CARBN
from carboxylic acid
hydrazides
1(108
NA
NA
INCIN; or
INCIN.
Condensed column
CiOXD
fb,
overheads from product
CARBN;
or
separation
and
condensed
BIODG Lb
reactor vent gases from
CAB.BN
the production of 1,1-
dimethylhydrazine
(UDMH)
from carboxyiic acid
hydrazides
K109
NA
NA
INCIN;
or
INCIN.
Spent
filter cartridges
CHOXD
fb,
from
product
CARBN;
or
purification from the
BIODG
Lb
production
of
1,1-
CARBN
dimethylhydrazine (UDMH)
from carboxylic acid
hydrazides
1(110
NA
NA
INCIN;
or
INCIN.
Condensed
column
CHOXD Lb,
overheads from
CAREN; or
intermediate separation
BIODG Lb
from the production of
CARBN
1, 1—dimethylhydrazine
(UDMH)
from
carboxylic
acid hydrazides
1(112
NA
NA
INCIN; or
INCIN.
Reaction by-product
CHOXO
fb,
water from the drying
CARBN;
or
column
in
the
production
BIODG
fb
of toluenediamine via
CABEN
hydrogenation
of
dinitrotoluene
1(113
NA
NA
CAREN;
or
PStJBS;
or
Condensed liquid light
INCIN
INCIN
ends from the
purification
of
toluenedjainine
in
the
production
of
toluenediamine via
hydrogenation
of
di-
nitrotoluene
1(114
NA
NA
CARBN;
or
FSUBS; or
Vicinals from the
INCIN
INCIN
purification of tol—
uenediamine in the
production
of
toluenedi-
amine via hydrogenation
of dinitrotoluene
1(115
NA
NA
CARBN; or
FSUBS;
or
Heavy
ends from the
INCIN
INCIN
purification
of
toluenediamine
in
the
production of tol—
uenediamine
via
hydrogenation
of
di-
nitrotoluene
121
1(116
NA
NA
CAP.BN;
or
FSUBS; or
Organic condensate from
INCIN
INCIN
the
solvent
recovery
column in the production
of toluene diisocyanate
via phosgenation of
toluenediaxnine
1(123
NA
NA
INCIN; or
INCIN.
Process waatewater
CHOXD
Lb
(including
supernates,
(BIODG or
filtrates, and
CARBN)
washwaters)
from the
production of
ethylenebis-
dithiocarbamic acid and
it.
salts
1(124
NA
NA
INCIN;
or
INCIN.
Reactor vent scrubber
CHOXD
fb
water from the
(BIODG or
production of
CABBN)
ethylenebiedi—
thiocarbamic
acid
and
its salts
1(125
NA
NA
INCIN; or
INCIN.
Filtration,
evaporation,
CHOXD
Lb
and centrifugation
(BIODG or
solids from the
CARBN)
production of
ethylenebisdi—
thiocarbaxnic acid and
its salts
1(126
NA
NA
INCIN; or
INCIN.
Baghouse dust and floor
CHOXD fb
sweepings in milling and
(BIODG or
packaging operations
CARBN)
from
the
production
or
formulation of ethylene
bisdithiocarbaxnic acid
and its salts
POOl
NA
81—81—2
(WETOX or
FSUBS;
or
Warfanin (0.3)
CHOXD)
fb
INCIN
CARBN;
or
INCIN
P002
NA
591-08-2
(WETOX
or
INCIN
1—Acetyl-2-thiourea
CHOXD)
fb
CAREN; or
INCIN
P003
NA
107—02—8
NA
FSUBS;
or
Acroiein
INCIN
P005
NA
107—18—6
(WETOX or
FSUBS; or
Ally.
alcohol
CHOXD)
fb
INCIN
cARBN; or
INCIN
P006
NA
20859—73-8
CHOXD;
CHOXD;
Aluminum phosphide
CHRED;
or
CHRED;
or
INCIN
INCIN
122
P007
NA
2763-96-4
(WETOX or
INCIN
5—Aminoethyl 3—
CHOXD)
fb
isoxazolol
CARBN;
or
INCIN
P008
NA
504—24—5
(WETOX or
INCIN
4—Aminopyridine
CHOXD)
fb
CAREN;
or
INCIN
P009
NA
131—74—8
CHOXD;
PSUBS; CH—
Ammonium picrate
CHRED;
OXD;
CARBN;
CHRED; or
BIODG; or
INCIN
INCIN
P014
NA
108-95-5
(WETOX or
INCIN
Thiophenol
(Benzene
CHOXD)
Lb
thiol)
CARBN; or
INCIN
P015
NA
7440—41-7
RXETL or
RMETL;
or
Beryllium
dust
RTHRM
RTHRM
P016
NA
542-88-1
(WETOX or
INCIN
Bis(chloromethyl)ether
CHOXD)
Lb
CARBN;
or
INCIN
P017
NA
598—31-2
(WETOX or
INCIN
Bromoacetone
CHOXD)
fb
CARBN;
or
INCIN
P018
NA
357—57-3
(WETOX or
INCIN
Brucine
CHOXD)
Lb
CARBN; or
INCIN
P022
Table
B
75-15-0
NA
INCIN
Carbon disulfide
P023
NA
107-20-0
(WETOX
or
INCIN
Chloroacetaldehyde
CHOXD)
Lb
CARBN;
or
INCIN
P026
NA
5344-82—1
(WETOX or
INCIN
l—(o-Chlorophenyl)thio-
CHOXD)
fb
urea
CARBN;
or
INCIN
P027
NA
542—76—7
(WETOX or
INCIN
3—Chloropropionitrile
CHOXD)
Lb
~ABBN; or
INCIN
P028
NA
100—44-7
(WETOX or
INCIN
Benzyl chloride
CHOXD)
Lb
CARBN;
or
INCIN
123
P031
NA
460-19-S
CHOXD;
CHOXD;
Cyanogen
WETOX; or
WETOX;
or
INCIN
INCIN
P033
NA
506-77-4
CHOXD;
CHOXO;
Cyanogen chloride
WETOX;
or
WETOX;
or
INCIN
INCIN
P034
NA
131-89—5
(WETOX or
INCIN
2-Cyclohexyl-4,6-di-
CHOXD)
Lb
nitrophenol
CARBN; or
INCIN
P040
NA
297-97-2
CARBN;
or
FSUBS;
or
0,0-Diethyl
0—pyrazinyl
INCIN
INCIN
phosphorothioate
P041
NA
311-45-5
CARBN;
or
FSUBS;
or
Diethyl-p-nitrophenyl
INCIN
INCIN
phosphate
P042
NA
51-43—4
(WETOX or
INCIN
Epinephrine
CHOXD)
Lb
CARBN;
or
INCIN
P043
NA
55-91—4
CARBN;
or
FSUBS;
or
Diisopropylfluorophos-
INCIN
INCIN
phate
(DFP)
P044
NA
60-51-5
CARBN; or
FSUBS;
or
Dimethoate
INCIN
INCIN
P045
NA
39196-18-4
(WETOX or
INCIN
Thiofanox
CHOXD)
Lb
CARBN;
or
INCIN
P046
NA
122-09—8
(WETOX or
INCIN
alpha,alpha-Dimethyl—
CHOXD) Lb
phenethylamine
CARBN; or
INCIN
P047
NA
534—52-1
(WETOX or
INCIN
4,6-Dinitro—o—cresol
CHOXD)
fb
salts
CARBN;
or
INCIN
P049
NA
541—53-7
(WETOX
or
INCIN
2,4—Dithiobiuret
CHOXD)
fb
CARBN;
or
INCIN
P054
NA
151—56-4
(WETOX or
INCIN
Azinidine
CHOXO)
fb
CARBN; or
INCIN
P056
Table
B
7782-41-4
NA
ADGAS
fb
Fluorine
NEUTR
P057
NA
640-19-7
(WETOX or
INCIN
Fluoroacetamide
CHOXD)
fb
CARBN; or
INCIN
124
P058
NA
62—74—8
(WETOX or
INCIN
Pluoroacetic acid,
CHOXO) Lb
sodium salt
CARBN;
or
INCIN
P062
NA
757-58-4
CARBN;
or
FSUBS
or
Naxaethyltetraphosphate
INCIN
INCIN
P064
NA
624-83—9
(WETOX or
INCIN
Isocyanic acid,
ethyl
CHOXO)
Lb
ester
CARBN;
or
INCIN
P065
Tables A
628-86-4
NA
RMERC
Mercury fulminate:
&
B
(High
Mercury
Sub-
category——greater than
or equal to 260 mg/kg
total Mercury——either
incinerator residues or
residues from RMERC)
P065
Tables A
628-86-4
NA
IMERC
Mercury fulminate:
(All
& B
nonwastewaters that are
not incinerator residues
or
are
not residues from
RNERC; regardless of
Mercury
Content)
P066
NA
16752-77—5
(WETOX or
INCIN
Methomyl
CHOXD)
fb
CARBN; or
INCIN
P067
NA
75—55-8
(WETOX
or
INCIN
2-Methylazinidine
CHOXD)
Lb
CARBN; or
INCIN
P068
NA
60-34—4
CHOXD;
CH-
FSUBS;
CH-
Methyl
hydrazine
RED;
OXD;
CARBN;
CHRED; OR
BIODG;
or
INCIN
INCIN
P069
NA
75—86-5
(WETOX or
INCIN
Methyllactonitrile
CHOXD)
Lb
CARBN;
or
INCIN
P070
NA
116-06-3
(WETOX or
INCIN
Aldicarb
CHOXD)
Lb
CARBN; or
INCIN
P072
NA
86—88-4
(WETOX or
INCIN
1—Naphthyl-2—thiourea
CHOXD)
Lb
CARBN;
or
INCIN
125
PO7S
NA
54—11—5
(WETOX
or
INCIN
Nicotine and salts
CHOXD)
Lb
CARBN;
or
INCIN
P076
NA
10102-43-9
ADGAS
ADGAS
Nitric oxide
P078
NA
10102-44-0
ADGAS
ADGAS
Nitrogen dioxide
P081
NA
55-63—0
CHOXD; CH-
PSUBS; CH-
Nitroglycerin
RED;
OXD;
CARBN;
CHRED;
or
BIODG;
or
INCIN
INCIN
P082
Table B
62—75-9
NA
INCIN
N—Nitrosodimethylamine
P084
NA
4549-40-0
(WETOX or
INCIN
N—Nitrosomethylvinyl—
CHOXO)
Lb
amine
CARBN;
or
INCIN
P085
NA
152-16-9
CARBN; or
FSUBS; or
Octamethylpyrophosphor—
INCIN
INCIN
amide
P087
NA
20816—12-0
RMETL;
or
RMETL; or
Osmium tetroxide
RTHEM
RTHBi4
P086
NA
145-73-3
(WETOX
or
FSUBS;
or
Endothal.
CHOXD) fb
INCIN
CARBN;
or
INCIN
P092
Tables
A
62—38-4
NA
RMERC
Phenyl mercury acetate:
& B
(High Mercury Sub-
category——greater than
or equal to 260 mg/kg
total
Mercury-—either
incinerator
residues or
residues from RMERC)
P092
Tables A
62-38-4
NA
IMERC; or
Phenyl mercury acetate:
&
B
RMERC
(All nonwastewaters that
are not incinerator
residues and are not
residues from RMERC:
regardless of Mercury
Content)
P093
NA
103-85-5
(WETOX or
INCIN
Phenyithiourea
CHOXD)
Lb
CARBN;
or
INCIN
P095
NA
75—44-5
(WETOX or
INCIN
Phosgene
CHOXD)
fb
CARBN;
or
INCIN
P096
NA
7803-51-2
CHOXD;
CH-
CHOXD;
CH-
Phosphine
RED;
or
RED;
or
INCIN
INCIN
126
P102
NA
107—19—7
(WETOX or
PSUBS;
or
Propargyl alcohol
CHOXO)
Lb
INCIN
CAREN; or
INCIN
P105
NA
26628-22-8
CHOXO;
CM-
PSUBS; CM-
Sodium azide
RED; CAREN
OXD;
81000; or
CHRED;
or
INCIN
INCIN
P108
NA
57-24-9
A
(WETOX
or
INCIN
Strychnine and
salts
CHOXD)
Lb
CARBN;
or
INCIN
P109
NA
3689—24-5
CARBN;
or
FSUSS; or
Tetraethyldithiopyro-
INCIN
INCIN
phosphate
P112
NA
509-14—8
CHOXD;
CM-
PSUBS; CM-
Tetranitromethane
RED;
OXD;
CARBN;
CHRED;
or
BIODG;
or
INCIN
INCIN
P113
Table B
1314-32—5
NA
RTHRN;
or
Thallic
oxide
STABL
P115
Table B
7446—18—6
NA
RTMRZ4;
or
Thallium
(I)
sulLate
STABL
P116
NA
79-19-6
(WETOX
or
INCIN
Thiosemicarbazide
CHOXD)
Lb
CARBN;
or
INCIN
P118
NA
75-70—7
(WETOX or
INCIN
Trichlorornethanethiol
CHOXD)
Lb
CARBN;
or
INCIN
P119
Table B
7803-55-6
NA
STABL
Ammonium
vanadate
P120
Table
B
1314-62-1
NA
STABL
Vanadium
pentoxide
P122
NA
1314-84-7
CHOXD;
CM-
CMOXD;
CM—
Zinc
Phosphide
(~1O)
RED;
or
RED;
or
INCIN
INCIN
U00l
NA
75-07-0
(WETOX or
INCIN
Acetaldehyde
CHOXD)
Lb
CARBN;
or
INCIN
0003
Table
B
75-05—8
NA
INCIN
Acetonitrile
U006
NA
75—36-5
(WETOX
or
INCIN
Acetyl chloride
CHOXD)
Lb
CARBN;
or
INCIN
127
U007
NA
79—06-i
(WETOX or
INCIN
Acrylainide
CHOXD)
Lb
CARBN;
or
INCIN
U008
NA
79—10-7
(WETOX or
PSUBS;
or
Acrylic acid
CMOXD)
Lb
INCIN
CARBN;
or
INCIN
UO10
NA
50-07-7
(WETOX or
INCIN
Mitomycin C
CHOXD)
Lb
CARBN;
or
INCIN
0011
NA
61-82-5
(WETOX or
INCIN
Axnitrole
CMOXD)
fb
CARBN;
or
INCIN
U014
NA
492—80—8
(WETOX
or
INCIN
Auramine
CHOXD)
Lb
CARBN;
or
INCIN
0015
NA
115-02—6
(WETOX or
INCIN
Azaserine
CHOXD)
Lb
CARBN; or
INCIN
U016
NA
225-51—4
(WETOX or
FSUBS; or
Benz(c)acridine
CMOXD)
Lb
INCIN
CARBN;
or
INCIN
U0l7
NA
98—87—3
(WETOX
or
INCIN
Benzal
chloride
CHOXD)
Lb
CAREN; or
INCIN
0020
NA
98-09—9
(WETOX
or
INCIN
Benzenesulfonyl chloride
CMOXD)
Lb
CARBN;
or
INCIN
0021
NA
92-87-5
(WETOX or
INCIN
Benzidine
CHOXD)
Lb
CARBN; or
INCIN
U023
NA
98—07—7
CHOXD;
CM—
FSUBS;
CM—
Benzotrichloride
RED;
CXC;
CARBN;
CHRED;
or
BIODG;
or
INCIN
INCIN
0026
NA
494-03-1
(WETOX or
INCIN
Chiornaphazin
CHOXD)
Lb
CAREN;
or
INCIN
128
0033
NA
353-50-4
(WETOX or
INCIN
Carbonyl fluoride
CHOXD)
Lb
CARBN;
or
INCIN
0034
NA
75—87—6
(WETOX or
INCIN
Trichloroacetaldehyde
CHOXD)
Lb
(Chloral)
CAREN; or
INCIN
0035
NA
305-03-3
(WETOX or
INCIN
Chloraxnbucil
CHOXD)
fb
CARBN; or
INCIN
U038
Table
B
510-15—6
NA
INCIN
Chlorobenzilate
U041
NA
106-89-8
(WETOX or
INCIN
1-Chioro-2,3-epoxy-
CHOXD)
Lb
propane
(Epichloro—
CABBN; or
hydrin)
INCIN
0042
Table
B
110-75-8
NA
INCIN
2—Chloroethyl vinyl
ether
U046
NA
107-30-2
(WETOX or
INCIN
Chloromethyl methyl
CHOXD)
Lb
ether
CAREN;
or
INCIN
U049
NA
3165—93-3
(WETOX
or
INCIN
4-Chloro—o—toluidine
CHOXD)
Lb
hydrochloride
CARBN; or
INCIN
0053
NA
4170-30—3
(WETOX or
PSUBS; or
Crotonaldehyde
CHOXD)
Lb
INCIN
CABBN;
or
INCIN
0055
NA
98-82-8
(WETOX or
PSUBS;
or
Cumene
CHOXD)
Lb
INCIN
CARBN; or
INCIN
0056
NA
110-82--i
(WETOX
or
FSUBS;
or
Cyclohexane
CHOXD)
Lb
INCIN
CARBN;
or
INCIN
U057
Table
B
108-94—1
NA
PSUBS; or
Cyclohexanone
INC IN
U058
NA
50—18-0
CARBN;
or
FSUBS; or
Cyclophosphainide
INCIN
INCIN
U059
NA
20830—81-3
(WETOX
or
INCIN
Daunomycin
CMOXD)
fb
CARBN; or
INCIN
129
U062
NA
2303—16—4
(WETOX
or
INCIN
Diallate
CHOXD)
fb
CARBN;
or
INCIN
U064
NA
189—55—9
(WETOX or
PSUBS; or
1,2,7,8—Dibenzopyrene
CHOXD)
fb
INCIN
CARBN; or
INCIN
0073
NA
91—94—i
(WETOX or
INCIN
3,3’—Dichlorobenzidine
CHOXD)
Lb
CAREN; or
INCIN
U074
NA
1476—11—5
(WETOX or
INCIN
cis—l,4—Dichloro-2—bu—
CHOXD)
Lb
tene;
trans—l,4—Di-
CARBN; or
chloro-2-butene
INCIN
U085
NA
1464—53—5
(WETOX
or
FSUBS;
or
1,2:3,4—Diepoxybutane
CHOXD)
fb
INCIN
CARBN; or
INCIN
U086
NA
1615-80-i
CHOXD;
FSUBS;
N,N-Diethylhydrazine
CHRED;
CHOXD;
CARBN;
CMRED; or
BIODG; or
INCIN
INCIN
U087
NA
3288—58—2
CARBN;
or
FSUBS;
or
0,0—Diethyl S—methyl-
INCIN
INCIN
dithiophosphate
U089
NA
56-53-1
(WETOX or
PSUBS;
or
Diethyl stilbeatrol
CHOXD)
Lb
INCIN
CARBN;
or
INCIN
U090
NA
94—58—6
(WETOX
or
FSUBS;
or
Dihydrosafrole
CHOXD)
Lb
INCIN
CARBN;
or
INCIN
U09i
NA
119-90-4
(WETOX or
INCIN
3,3’-Dimethoxybenzidine
CHOXD)
Lb
CARBN;
or
INCIN
U092
NA
124-40-3
(WETOX or
INCIN
Dimethylamine
CHOXD)
Lb
CARBN;
or
INCIN
U093
Table
B
621-90-9
NA
INCIN
p-Dimethylaxninoazo—
benzene
U094
NA
57—97-6
(WETOX or
PSUBS;
or
7,12—Dimethylbenz(a)—
CHOXD)
fb
INCIN
anthracene
CARBN; or
INCIN
130
0095
NA
119—93—7
(WETOX or
INCIN
3,3’—Dimethylbenzidine
CHOXD)
Lb
CAP.BN;
or
INCIN
U096
NA
80—15—9
CHOXD;
PSUBS;
alpha,alpha—Cimethyl-
CHRED;
CHOXD;
benzyl hydroperoxide
CABBN;
CHRED; or
BIODG; or
INCIN
INCIN
0097
NA
79—44-7
(WETOX
or
INCIN
Diniethylcarbamoyl chior—
CHOXO) Lb
ide
CARBN; or
INCIN
0098
NA
57-14-7
CHOXD; CM-
FSUBS; CH-
l,1—Dimethylhydrazine
RED;
OXD;
CARBN;
CHRED;
or
810CC;
or
INCIN
INCIN
0099
NA
540-73-8
CHOXD;
CM-
PSUBS;
CM-
1,2-Dimethyihydrazine
RED;
OXD;
CARBN;
CHRED;
or
BIODG;
or
INCIN
INCIN
0103
NA
77-78—i
CHOXD;
CM-
PSUBS;
CM-
Dixnethyl sulfate
RED;
OXD;
CABEN;
CHRED;
or
810CC;
or
INCIN
INCIN
U109
NA
122—66—7
CHOXD;
CM—
PSUBS; CM-
1,2—Diphenylhydrazine
RED;
OXD;
CARBN;
CHRED;
or
BIODG; or
INCIN
INCIN
0110
NA
142-84—7
(WETOX or
INCIN
Cipropylamine
CHOXO)
fb
CABBN;
or
INC IN
U1l3
NA
140—88-5
(WETOX
or
PSUBS;
or
Ethyl
acrylate
CHOXD)
Lb
INCIN
CABBN;
or
INCIN
U114
NA
111—54—6
(WETOX
or
INCIN
Ethylenebisdithio-
CHOXD)
fb
carbamic
acid
CAREN; or
INCIN
0115
NA
75-21—8
(WETOX
or
CHOXD;
or
Ethylene
oxide
CMOXD)
Lb
INCIN
CARBN; or
INCIN
131
U116
NA
96-45-7
(WETOX
or
INCIN
Ethylene thiourea
CHOXD)
Lb
CARBN;
or
INCIN
U119
NA
62-50—0
(WETOX or
INCIN
Ethyl methanesulfonate
CHOXD) Lb
CARBN; or
INCIN
U122
NA
50-00—0
(WETOX
or
PSUBS; or
Formaldehyde
CHOXD) Lb
INCIN
CARBN;
or
INCIN
U123
NA
64-18—6
(WETOX
or
FSUBS; or
Formic acid
CHOXD)
fb
INCIN
CAP.BN;
or
INCIN
U124
NA
110—00-9
(WETOX or
FSUBS; or
Puran
CMOXD)
Lb
INCIN
CARBN;
or
INCIN
0125
NA
98-01—1
(WETOX
or
FSUBS;
or
Purfural
CHOXD)
Lb
INCIN
CARBN;
or
INCIN
0126
NA
765-34—4
(WETOX or
FSUBS; or
Glycidaldehyde
CHOXD)
Lb
INCIN
CARBN;
or
INCIN
U132
NA
70-30—4
(WETOX
or
INCIN
Hexachlorophene
CMOXD)
Lb
CARBN;
or
INCIN
Ul33
NA
302—01—2
CHOXD;
FSUBS;
Hydrazine
CHRED;
CHOXD;
CARBN;
CMRED; or
BIODG;
or
INCIN
INCIN
U134
Table B
7664-39-3
NA
ADGAS
Lb
Hydrogen Fluoride
NEUTR;
or
NEUTR
U135
NA
7783-06-4
CMOXD;
CM-
CHOXD; CM-
Hydrogen
Sulfide
RED;
or
RED;
or
INCIN
INCIN
U143
NA
303—34—4
(WETOX or
INCIN
Lasiocarpine
CMOXD)
Lb
CARBN;
or
INCIN
132
0147
NA
108-31-6
(WETOX or
FSUBS;
or
Maleic anhydride
CHOXD)
Lb
INCIN
CABBN;
or
INCIN
U148
NA
123-33-1
(WETOX or
INCIN
Maleic hydrazide
CHOXD)
fb
CARBN;
or
INCIN
U149
NA
109-77-3
(WETOX or
INCIN
Malononitrile
CHOXD)
fb
CAP.BN;
or
INCIN
0150
NA
148-82—3
(WETOX or
INCIN
Melphalan
CHOXD)
Lb
CABBN;
or
INCIN
U151
Tables
A
7439-97-6
NA
RMERC
Mercury:
(High Mercury
&
B
Subcategory——greater
than or equal to 260
mg/kg total Mercury)
Ui53
NA
74—93-1
(WETOX or
INCIN
Methanethiol
CHOXD)
Lb
CARBN;
or
INCIN
0154
NA
67—56-1
(WETOX
or
PSUBS;
or
Methanol
CHOXD)
Lb
INCIN
CARBN;
or
INCIN
U156
NA
79-22-1
(WETOX or
INCIN
Methyl chlorocarbonate
CHOXD)
Lb
CARBN;
or
INCIN
U160
NA
1338-23—4
CMOXD;
FSUBS;
Methyl ethyl ketone per-
CHRED;
CHOXD;
oxide
CARBN;
CHRED;
or
BIODG;
or
INCIN
INCIN
Ul63
NA
70-25-7
(WETOX or
INCIN
N-Methyl—N’-nitro-N-
CHOXD)
Lb
Nitrosoguanidine
CARBN; or
INCIN
0164
NA
56—04-2
(WETOX
or
INCIN
Methylthiouracil
CHOXD)
Lb
CARBN; or
INCIN
U166
NA
130—15-4
(WETOX
or
PSUBS;
or
l,4—Naphthoquinone
CHOXD)
Lb
INCIN
CAP.BN; or
INCIN
133
Ui67
NA
134-32-7
(WETOX
or
INCIN
1-Naphthylamine
CMOXD)
Lb
CARBN;
or
INCIN
0168
Table B
91-59-8
NA
INCIN
2-Naphthylamine
U171
NA
79-46-9
(WETOX or
INCIN
2—Nitropropane
CHOXD)
fb
CARBN; or
INCIN
0173
NA
1116-54-7
(WETOX or
INCIN
N—Nitroso-diethanolamine
CHOXD)
Lb
CABBN; or
INCIN
U176
NA
759-73—9
(WETOX or
INCIN
N-Nitroso-N—ethylurea
CHOXD)
Lb
CARBN;
or
INCIN
U177
NA
684—93-5
(WETOX
or
INCIN
N-Nitroso-N-methylurea
CMOXD)
Lb
CARBN;
or
INCIN
0178
NA
615—53-2
(WETOX or
INCIN
N-Nitroso-N-methyl-
CHOXD)
Lb
urethane
CARBN;
or
INCIN
Ul82
NA
123—63—7
(WETOX or
FSUBS;
or
Paraldehyde
CHOXD)
Lb
INCIN
CARBN; or
INCIN
U184
NA
76—01-7
(WETOX
or
INCIN
Pentachloroethane
CHOXD)
Lb
CARBN;
or
INCIN
U186
NA
504—60—9
(WETOX or
FSUBS;
or
1,3-Pentadiene
CHOXD)
fb
INCIN
CARBN;
or
INCIN
U189
NA
1314-80-3
CMOXD; CM-
CHOXD;
CM-
Phosphorus sulfide
RED;
or
RED;
or
INCIN
INCIN
0191
NA
109—06-8
(WETOX
or
INCIN
2—Picoline
CHOXD)
Lb
cARBN; or
INCIN
Ui93
NA
1120—71—4
(WETOX or
INCIN
1,3—Propane sultone
CMOXD)
Lb
CABBN;
or
INCIN
134
0194
NA
107—10—8
(WETOX or
INCIN
n-Propylamine
CHOXD)
Lb
CARBN;
or
INCIN
0197
NA
106-51-4
(WETOX
or
PSUBS;
or
p-Senzoquinone
CMOXD)
Lb
INCIN
CAREN;
or
INCIN
0200
NA
50—55-5
(WETOX
or
INCIN
Reserpine
CMOXD)
Lb
CAREN;
or
INCIN
U201
NA
108-46-3
(WETOX or
PSUBS;
or
Resorcinol
CHOXD)
Lb
INCIN
CARBN; or
INCIN
0202
NA
81—07-2 A
(WETOX or
INCIN
Saccharin and salts
CHOXD)
Lb
CARBN; or
INCIN
U206
NA
18883—66—4
(WETOX
or
INCIN
Streptozatocin
CHOXD)
Lb
CARBN;
or
INCIN
0213
NA
109-99-9
(WETOX or
FSUBS;
or
Tetrahydrofuran
CHOXD)
Lb
INCIN
CARBN; or
INCIN
0214
Table
B
563—68—8
NA
RTHRM;
or
Thallium
(I)
acetate
STABL
U215
Table
B
6533-73-9
NA
RTHRM;
or
Thallium
(I)
carbonate
STABL
U216
Table
B
7791—12—0
NA
RTHRM;
or
Thallium
(I) chloride
STABL
0217
Table
B
10102—45-1
NA
RTMRM; or
Thallium
(I) nitrate
STABL
0218
NA
62555
(WETOX or
INCIN
Thioacetamide
CHOXD)
Lb
CAREN;
or
INCIN
0219
NA
62-56—6
(WETOX
or
INCIN
Thiourea
CHOXD)
Lb
CARBN;
or
INCIN
0221
NA
25376—45-8
CARBN;
or
PSUBS; or
Toluenediaznine
INCIN
INCIN
135
U222
NA
636-21—5
(WETOX or
INCIN
o-Toluidine hydro-
CHOXD)
Lb
chloride
CAP.BN; or
INCIN
U223
NA
26471-62-5
CARBN;
or
PSUBS; or
Toluene diiaocyanate
INCIN
INCIN
U234
NA
99—35—4
(WETOX
or
INCIN
sym—Trinitrobenzene
CHOXD)
fb
CARBN; or
INCIN
U236
NA
72-57-1
(WETOX or
INCIN
Trypan Blue
CHOXD)
Lb
CARBN;
or
INCIN
U237
NA
66—75—1
(WETOX or
INCIN
Uracil mustard
CHOXD)
fb
CARBN;
or
INCIN
U238
NA
51-79—6
(WETOX or
INCIN
Ethyl carbamate
CHOXO) Lb
CARBN; or
INCIN
0240
NA
94-75—7~
(WETOX or
INCIN
2,4—Dichiorophenoxy—
CHOXD)
Lb
acetic acid (salts and
CARBN;
or
esters)
INCIN
0244
NA
137—26—8
(WETOX or
INCIN
Thiraxn
CMOXD) Lb
CARBN;
or
INCIN
0246
NA
506-68-3
CMOXD;
CHOXD;
Cyanogen bromide
WETOX;
or
WETOX; or
INCIN
INCIN
0248
NA
81—81—2
(WETOX or
PSUBS;
or
Warfarin
(0.3
or
less)
CHOXD)
Lb
INCIN
CARBN;
or
INCIN
0249
NA
1314—84—7
CMOXD; CM-
CMOXD;
CM—
Zinc Phosphide
(10)
RED;
or
RED;
or
INCIN
INCIN
U328
NA
95—53—4
INCIN;
or
INCIN; or
o—toluidine
CHOXD
Lb,
Thermal
(BIODG or
Destructio
CARBN);
or
n.
BIODG
Lb
CARBN
136
U353
NA
106-49-0
INCIN; or
INCIN; or
p-toluidine
CHOXD fb,
Thermal
(BIODG or
Destructio
CARBN); or
n.
BIODG Lb
CAREN
U359
NA
110-80-5
INCIN; or
INCIN;
or
2—ethoxy—ethanol
CHOXD Lb,
PSUBS.
(810CC or
CARBN); or
8IODG Lb
CARBN
A
CAS Number given for parent compound only.
B
This waste code exists in gaseous form and
is not categorized
as
wastewater or nonwastewater Loris.
NA
Not Applicable.
BOARD NOTE:
When a combination of these technologies
(i.e.,
a treatment
train)
is
specified as a single treatment standard, the order of application
is specified
in this Table by indicating the Live letter technology code that
must be applied first, then the designation “Lb”
(an abbreviation for “Fol-
lowed by”), then the Live letter technology code for the technology that must
be applied next, and so on.
When
more
than
one
technology (or treatment
train)
are specified a alternative treatment standards,
the five letter
technology codes
(or the treatment trains) are separated by
a semicolon
(;)
with the last technology preceded by the word “or”.
This indicates that any
one of these BDAT technologies or treatment trains can be used for compliance
with the standard.
See Section 728.Table C for a listing of the technology
codes and technology-based treatment standards.
Derived from 40 CFR 268.42,
Table
2
(1992),
as amended at
57
Fed. Reg.
37273
(Aug.
18,
1992).
(Source:
Amended at 18
Ill. Rag.
_________,
effective
_____________________
