ILLINOIS POLLUTION CONTROL BOARD
October 24,
1991
IN THE MATTER OF:
)
R91—26
RCRA WOOD PRESERVING RULES
)
(Identical
in Substance Rules)
COMPLIANCE DATES
)
PROPOSAL FOR PUBLIC COMNENT
PROPOSED OPINION
AND
ORDER OF THE BOARD
(by J. Anderson):
On August 8, 1991, the Board entered a final Opinion and Order
in R91-1.
A!aong other things, the Board adopted new regulations
regulating wood preservers.
These rules were derived from USEPA
regulations adopted at 55 Fed.
Reg.
50450, December 6,
1990.
As
was
discussed
on
p.
11-14
of
the
R9l—3.
Opinion,
USEPA
administratively stayed the wood preserving rules
at
56 Fed Reg.
27332, June 13,
1991.
The Board addressed the stay in R91—l, even
though it was outside the normal batch period for the Docket.
As was discussed in the R91—l Opinion,
com!nenters asked the
Board to delay adoption of the wood preserving rules until after
the
USEPA
administrative
stay
expired.
Instead,
the
Board
determined to adopt the USEPA wood preserving rules,
along with
USEPA’s language staying the rules; however, the stay applied only
to
those
who
made
prior
date-certain
filings
of
required
information.
To qualify for the USEPA administrative stay,
wood
preservers
had
to
notify
USEPA
by
August
6,
1991,
that
they
intended to upgrade drip pads by placing an impermeable coating on
the surface.
Wood preservers also have to notify USEPA by November
6,
1991, with a plan and financial commitments for the upgrading,
which upgrading must then be completed by February 6,
1992.
This Docket concerns only the non-HSWA portions of the wood
preserving
rules.
Non—HSWA requirements
are not
effective
in
authorized states, such as Illinois, until they are adopted by the
states.
As was discussed on p.
13 of the R91-.
Opinion, USEPA and
wood preservers subject only to the non-HSWA portions of the USEPA
rules may have been operating on the assumption that Illinois would
not adopt the USEPA rules because of the USEPA stay and anticipated
USEPA modification of their rules.
However,
the Environmental
Protection Act (See Sections 7.2(a) and 22.4(a)) expects the Board
to adopt these
rules,
subject to the stay.
In that the Board’s
action might have
caused
confusion,
the Board had extended the
initial
notification date,
from August 6 to November
6,
1991,
to
qualify for the stay from the Board rules.
Since
the
R91-1
rules were filed however,
Board staff has
received
several
calls
from
wood
preservers
claiming
that the
coating operation requires outdoor temperatures
in excess of 70.
126—7 15
2
F.
It
is
therefore
physically
impossible to
comply
with
the
conditions of the stay by preparing
a plan and carrying out
the
coating operation before February
6, at least in Illinois.
As was discussed above,
and in R91-l, USEPA has stayed these
requirements and may not expect the States to adopt them at all
until after the federal rules have been modified in a subsequent
rulemaking. In any event, 40 CFR 271.21(e) would not require State
action on the non-HSWA components until July
1,
1992.
The Board
is therefore now proposing to extend the upgrading compliance date
to July 1,
1992.
The Board will also extend the date for the plan
and
financial
cominittments
to
February
6,
1992,
to
give
wood
preservers time to file the plan and financial committments after
the Board’s rules become effective.
Our instant proposal is a correction to R91—l, as contemplated
in Section 7.2(b)
of the Act.
In this Docket the Board
is doing
that which it would have done in R91-1, had it been fully advised
of the facts.
The Board will therefore
amend the
“stay”
language
in the
Board Notes
following listings F034 and F035
in Section 721.131,
as is set forth below.
It apparently is not necessary to amend the
operative language
in Section 724.673
and 725.543.
The stay of
F032
is HSWA-driven, and apparently cannot be extended.
The
Board
directs
that the text
of the proposed rules be
published in the Illinois Register.
The Board will receive public
comment
for
45
days
following
the date
of
publication
in
the
Illinois Register.
Because of the time constraints
involved in
advancing these dates, the Board cautions that it will act quickly
following expiration of the comment period, and does not anticipate
allowing post—adoption comment.
ORDER
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
Section
721.101
Purpose and Scope
721.102
Definition of Solid Waste
721.103
Definition of Hazardous Waste
721.104
Exclusions
126—716
3
721.105
Special Requirements
for Hazardous Waste
Generated by
Small Quantity Generators
721.106
Requirements for Recyclable Materials
721.107
Residues of Hazardous Waste in Empty Containers
721.108
PCB Wastes Regulated under TSCA
SUBPART
B:
CRITERIA FOR IDENTIFYING THE CHARACTERISTICS
OF HAZARDOUS WASTE AND FOR LISTING HAZARDOUS WASTES
Section
721.110
Criteria for Identifying the Characteristics of Hazardous
Waste
721.111
Criteria for Listing Hazardous Waste
SUBPART C:
CHARACTERISTICS
OF HAZARDOUS WASTE
Characteristic of Ignitability
Characteristic of Corrosivity
Characteristic of Reactivity
Toxicity Characteristic
Section
721.130
721.131
Hazardous Wastes From Nonspecific Sources
721.132
Hazardous Waste from Specific Sources
721.133
Discarded Commercial Chemical Products, Off—Specification
Species, Container Residues and Spill Residues Thereof
721.135
Wood Preserving Wastes
Appendix A
Appendix B
Appendix C
Table A
Table B
Table C
Appendix G
Appendix H
Appendix I
Table A
Table B
Table C
Representative Sampling Methods
Method
1311
Toxicity
Characteristic
Leaching
Procedure
(TCLP)
Chemical Analysis Test Methods
Analytical
Characteristics
of
Organic
Chemicals
(Repealed)
Analytical
Characteristics
of
Inorganic
Species
(Repealed)
Sample Preparation/Sample Introduction Techniques
(Repealed)
Basis for Listing Hazardous Wastes
Hazardous Constituents
Wastes Excluded under 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
General
Section
721.120
721.121
721.122
721. 123
721.124
SUBPART D:
LISTS OF HAZARDOUS WASTE
General
126—717
4
Appendix 3
Method
of
Analysis
for
Chlorinated
Dibenzo-p-
Dioxins and Dibenzofurans
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.
1989,
ch.
111½, pars.
1022.4 and 1027).
SOURCE:
Adopted
in
R81-22,
43
PCB
427,
at
5
Ill.
Reg.
9781,
effectivp
as
noted
in
35
Iii.
Adm.
Code
700.106;
amended
and
codified in R81—22,
45 PCB 317, at 6
Ill. Reg.
4828,
effective as
noted in 35 Ill. Adm. Code 700.106; amended in R82-18,
51 PCB 31,
at
7
Ill. Reg.
2518, effective February 22,
1983; amended in R82-
19,
53 PCB 131, at 7 Ill.
Reg.
13999, effective October 12,
1983;
amended
in R.4-34,
61 PCB 247,
at
8
Ill.
Reg.
24562,
effective
December
11,
1984;
amended
in
R84—9,
at
9
Ill.
Reg.
11834,
effective July 24,
1985;
amended in R85—22 at
10
Ill.
Reg.
998,
effective January 2,
1986;
amended in R85—2 at 10
Ill.
Reg. 8112,
effective May
2,
1986;
amended in R86—1
at
10
Ill.
Reg.
14002,
effective August 12,
1986; amended in R86—19 at 10 Ill. Reg. 20647,
effective December 2, 1986; amended in R86-28 at 11 Ill. Reg. 6035,
effective March 24, 1987; amended in R86—46 at 11 Ill. Reg. 13466,
effective August 4, 1987; amended in R87—32 at 11 Ill.
Reg..
16698,
effective September
30,
1987;
amended
in R87-5
at
11
Ill.
Reg.
19303,
effective November 12,
1987;
amended in R87—26 at
12
Ill.
Reg. 2456, effective January 15,
1988; amended in R87-30 at 12 Ill.
Reg.
12070, effective July 12,
1988; amended in R87—39 at 12 Ill.
Reg. 13006, effective July 29,
1988; amended in R88—l6 at 13 Ill.
Reg.
382, effective December 27, 1988; amended in R89-l at 13 Ill.
Reg.
18300,
effective November 13,
,1989;
amended in R90—2
at
14
Ill. Reg.
14401,
effective August 22,
1990;
amended
in R90-l0 at
14
Ill. Reg.
16472, effective September 25,
1990; amended in R90-
17 at 15 Ill. Reg.
7950, effective May 9,
1991; amended in R90—ll
at 15 Ill. Reg. 9332, effective June 17, 1991; amended in R91—l at
15 Ill.
Reg.
,
effective
;
amended in R91-
26 at
Ill. Reg.
,
effective
SUBPART D:
LISTS OF HAZARDOUS WASTE
Section 721.131
Hazardous Wastes From Nonspecific Sources
a)
The following solid wastes
are listed hazardous wastes
from non—specific sources unless they are excluded under
35
Ill.
Adm.
Code
720.120 and
720.122
and
listed
in
Appendix I.
E
P
A Industry and Hazardous Waste
Haz-
Hazardous
a r
a
Waste No.
Code
126—718
5
FOOl
The
following
spent
halogenated
(T)
solvents
used
in
degreasing:
tetra—
chloroethylene,
trichloroethylene,
methylene
chloride,
1,1,l—trichloro-
ethane,
carbon
tetrachloride
and
chlorinated
fluorocarbons;
all
spent
solvent
mixtures
and
blends
used
in
degreasing
containing,
before
use,
a
total
of
ten
percent
or
more
(by
volume)
of
one
or
more
of
the
above
halogenated solvents
or those
solvents
listed in F002, F004 or F005;
and still
bottoms
from
the
recovery
of
these
spent
solvents
and
spent
solvent
mixtures.
F002
The
following
spent
halogenated
(T)
solvents:
tetrachioroethylene,
methylene chloride,
trichloroethylene,
1,1, 1—trichloroethane,
chlorobenzene,
1,1,2-trichloro-1, 2, 2-trifluoroethane,
orthodichlorobenzene,
trichloro—
fluoroinethane
and
1,1,2—trichloro—
ethane;
all spent solvent mixtures and
blends containing,
before use,
a total
of ten percent or more
(by volume)
of
one
or
more
of
the
above
halogenated
solvents
or
those
solvents
listed
in
FOOl,
F004 or F005;
and
still
bottoms
from
the
recovery
of
these
spent
solvents and spent solvent mixtures.
F003
The
following
spent
non-halogenated
(I)
solvents:
xylene,
acetone,
ethyl
acetate,
ethyl
benzene,
ethyl
ether,
methyl
isobutyl
ketone,
n-butyl
alcohol,
cyclohexanone
and
methanol;
all
spent
solvent mixtures and blends
containing,
before use, only the above
spent non—halogenated solvents; and all
spent
solvent
mixtures
and
blends
containing,
before use, one or more of
the above non—halogenated solvents and
a
total
of
ten
percent
or
more
(.by
volume)
of
one
or
more
of
those
solvents listed in FOOl,
F002,
F004 or
F005;
and
still
bottoms
from
the
recovery
of
these
spent
solvents
and
spent solvent mixtures.
F004
The
following
spent
non—halogenated
(T)
solvents:
cresols
and
cresylic
acid
126—719
6
and
nitrobenzene;
all
spent
solvent
mixtures and blends
containing,
before
use,
a total of ten percent or more
(by
volume)
of
one
or more
of
the
above
non-halogenated
solvents
or
those
solvents
listed
in
FOOl,
F002
or
F005;
and still bottoms
from the recovery of
these
spent
solvents and spent solvent
mixtures.
FOO5
The
following
spent
non-halogenated
(
I
solvents:
toluene,
methyl
ethyl
T)
ketone,
carbon
disulfide,
isobutano.,
pyridine,
benzene,
2—ethoxyethanol
and
2—nitropropane;
all
spent
solvent
mixtures and blends, containing, before
use, a total of ten percent or more (by
volume)
of
one
or
more
of
the
above
non—halogenated
solvents
or
those
solvents
listed
in
FOOl,
F002
or
F004;
and still bottoms from the recovery of
these spent solvents and spent
solvent
mixtures.
F006
Wastewater
treatment
sludges
from
(T)
electroplating
operations
except
from
the
following
processes:
(1)
sulfuric
acid
anodizing
of
aluminum;
(2)
tin
plating
on
carbon
steel;
(3)
zinc
plating
(segregated
basis)
on
carbon
steel;
(4)
aluminum
or
zinc—aluminum
plating
on
carbon
steel;
(5)
cleaning/stripping associated with tin,
zinc
and
aluminum
plating
on
carbon
steel;
and
(6)
chemical
etching
and
milling of aluminum.
FO19
See Below
FOO7
Spent
cyanide
plating
bath
solutions
(
R
from electroplating operations.
T)
F008
Plating bath residues from the bottom
(
R
of
plating
baths
from
electroplating T)
operations where
cyanides are used
in
the
process.
F009
Spent
stripping
and
cleaning
bath
(
R
solutions
from
electroplating
T)
operations
where
cyanides
are
used
in
the process.
126—7 20
7
FOlO
Quenching bath residues from oil baths
(
R
from
metal
heat
treating
operations
T)
where
cyanides
are
used
in
the
process.
FOil
Spent
cyanide
solutions
from
salt
bath
(
R
pot cleaning
from metal
heat
treating T)
operations.
F0l2
Quenching wastewater treatment sludges
(T)
from
metal
heat
treating
operations
where
cyanides
are
used
in
the process.
F019
Wastewater
treatment
sludges
from the
(T)
chemical
conversion
coating
of
aluminum
except
from
zirconium
phosphating
in
aluminum
can
washing
when
such
phosphating
is
an
exclusive
conversion
coating
process.
F020
Wastes
(except
wastewater
and
spent
(H)
carbon
from
hydrogen
chloride
purification)
from
the
production
or
manufacturing
use
(as
a
reactant,
chemical intermediate or component in a
formulating process)
of tn-
or tetra-
chlorophenol,
or of intermediates used
to produce their pesticide deri.vatives.
(This
listing does
not
include
wastes
from
the production of hexachlorophene
from
highly
purified
2,4,5-trichioro—
phenol.
)
F021
Wastes
(except
wastewater
and
spent
(H)
carbon
from
hydrogen
chloride
purification)
from
the
production
or
manufacturing
use
(as
a
reactant,
chemical intermediate or component in a
formulating
process)
of
pentachioro—
phenol,
or
of
intermediates
used
to
produce
its
derivatives.
FO22
Wastes
(except
wastewater
and
spent
(H)
carbon
from
hydrogen
chloride
purification)
from
the
manufacturing
use
(as
a
reactant,:
chemical
intermediate
or
component
in
a
formulating process)
of
tetra—,
penta—
or
hexachlorobenzenes
under
alkaline
conditions.
F023
Wastes
(except
wastewater
and
spent
(H)
carbon
from
hydrogen
chloride
126—72 1
8
purification)
from
the
production
of
materials on equipment previously used
for the production or manufacturing use
(as
a
reactant,
chemical
intermediate
or
component
in
a
formulating
process)
of tn-
and tetnachlorophenols.
(This
listing
does
not
include
wastes
from
equipment used only for the production
or use
of hexachiorophene
from highly
purified 2,4,5- tnichlorophenol.
FO24
Process
wastes
including
but
not
(T)
limited
to,
distillation
residues,
heavy ends,
tars,
and reactor cleanout
wastes,
from the production of certain
chlorinated
aliphatic
hydrocarbons
by
free
radical
catalyzed
processes.
These
chlorinated
aliphatic
hydrocarbons
are
those
having
carbon
chain
lengths ranging from one to and
including
five,
with
varying
amounts
and positions of chlorine substitution.
(This
listing
does
not
include
wastewaters,
wastewater
treatment
sludges,
spent
catalysts
and
wastes
listed
in
this
Section
or
Section
721.132.)
FO25
Condensed light ends,
spent filters and
(T)
filter aids,
and spent desicant wastes
from
the
production
of
certain
chlorinated
aliphatic
hydrocarbons
by
free
radical
catalyzed
processes.
These
chlorinated
aliphatic
hydrocarbons
are
those
having
carbon
chain
lengths ranging
from one
to and
including
five,
with
varying
amounts
and positions of chlorine substitution.
F026
Wastes
(except
wastewater
and
spent
(H)
carbon
from
hydrogen
chloride
purification)
from
the
production
of
materials on equipment previously used
for
the
manufacturing
use
(as
a
reactant,
chemical
intermediate
or
component
in
a
formulating
process)
of
tetra—,
penta—
or
hexachlorobenzene
under alkaline conditions.
FO27
Discarded
unused
formulations
(H)
containing tn—,
tetra— or pentachloro—
phenol or discarded unused formulations
126—722
9
containing compounds derived from these
chiorophenols.
(This
listing does not
include
formulations
containing
hexa—
chiorophene
synthesized
from
prepurified
2,4,
5-trichiorophenol
as
the sole component).
F028
Residues
resulting
from
the
(T)
incineration
or
thermal
treatment
of
soil
contaminated with hazardous waste
numbers
FO2O,
FO21,
FO22,
F023,
F026
and FO27.
FO32
Wastewaters,
process
residuals,
(T)
preservative
drippage
and
spent
formulations
from
wood
preserving
processes
generated
at
plants
that
currently
use or have previously used
chlorophenolic
formulations
(except
potentially
cross—contaminated
wastes
that
have
had
the
F032
waste
code
deleted
in
accordance
with
Section
721.135
and
where
the
generator
does
not resume or
initiate use of chloro—
phenolic
formulations).
This
listing
does
not
include
KOOl
bottom
sediment
sludge from the treatment of wastewater
from wood preserving processes that use
creosote or pentachiorophenol.
BOARD NOTE:
The listing of wastewaters
that
have
not
come
into
contact
with
process
contaminants
is
stayed
administratively.
The
listing
for
plants
that
have
previously
used
chlorophenolic
formulations
is
administratively
stayed whenever these
wastes
are
covered
by
the
F034
or
FO35
listings.
These
stays will remain
in
effect
until
further
administrative
action
is
taken.
Furthermore,
the
FO32
listing
is
administratively
stayed
with
respect
to
the
process area receiving
drippage
of
these
wastes
provided
persons
desiring
to
continue operating
notify
USEPA
by
August
6,
1991,
of
their intent to upgrade or install drip
pads,
and
by
November
6,
1991,
provide
evidence
to
USEPA
that
they
have
adequate financing to pay for drip pad
upgrades
or
installation,
as
provided
in
the administrative
stay.
The stay
126—7 23
10
of listings will remain
in effect until
February
6,
1992,
for
existing
drIp
pads,
and until
May
6,
1992,
for new
drip pads.
F034
Wastewaters,
process
residuals,
(T)
preservative
drippage
and
spent
formulations
from
wood
preserving
processes
generated
at
plants
that
use
creosote
formulations.
This
listing
does
not include K001 bottom
sediment
sludge from the treatment of wastewater
from wood preserving processes that use
creosote
or
pentachiorophenol.
BOARD
NOTE:
The listing of wastewaters
that
have
not
come
into
contact with
process
contaminants
is
stayed
administratively.
These
stays
will
remain
in
effect
until
further
administrative
action
is
taken.
Furthermore, the F034 and F035 listings
are
administratively
stayed
with
respect to
the
process
area
receiving
drippage of these wastes provided that,
by Novembcr
6,
1~1February 6.
1992,
persons desiring
to continue operating
notify
the Agency
of their
intent
to
upgrade
or
install
drip
pads,
and
provide
evidence
to
the
Agency
that
they have adequate financing to pay for
drip pad upgrades
or
installation,
as
provided
in
the
administrative
stay.
The
stay
of
listings
will
remain
in
effect
until
February
6,
l~92, for
existing
drip
pads,
and
until
May
6,
1~2, for new drip pad2July 1.
1992.
FO35
Wastewaters,
process
residuals,
(T)
preservative
drippage
and
spent
formulations
from
wood
preserving
processes
generated
at
plants
that
use
inorganic
preservatives
containing
arsenic
or
chromium.
This
listing
does
not include KOOl bottom sediment sludge
from the treatment of wastewater
from
wood
preserving
processes
that
use
creosote or pentachlorophenol.
BOARD NOTE:
The listing of wastewaters
that
have
not
come
into
contact with
process
contaminants
is
stayed
126—724
11
administratively.
These
stays
will
remain
in
effect
until
further
administrative
action
is
taken.
Furthermore,
the F034 and F035 listings
are
administratively
stayed
with
respect to
the process
area
receiving
drippage of these wastes provided that,
by
Novcinber
6,
l99lFebruarv
6.
1992,
persons desiring to continue operating
notify
the Agency
of
their
intent to
upgrade
or
install
drip
pads,
and
provide
evidence
to
the
Agency
that
they have adequate financing to pay for
drip pad upgrades or
installation,
as
provided
in
the
administrative
stay.
The
stay
of
listings
will
remain
in
effect
until
February
6,
1992,
for
existing drip
pads,
and until
May
6,
1002,
for new drip pad33uly
1,
1992.
FO37
Petroleum
refinery
primary
oil/water/
(T)
solids separation sludge
--
Any sludge
generated
from
the
gravitational
separation
of
oil/water/solids
during
the
storage
or
treatment
of
process
wastewaters
and
oily
cooling
wastewaters
from petroleum refineries.
Such
sludges
include,
but
are
not
limited
to,
those generated
in:
oil/
water/solids
separators;
tanks
and
impoundments;
ditches
and
other
conveyances;
suiups;
and
stormwater
units
receiving
dry
weather
flow.
Sludges
generated
in
stormwater units
that do not receive dry weather
flow,
sludges
generated
in
aggressive
biological
treatment units
as
defined
in subsection
(b) (2)
(including sludges
generated
in
one
or
more
additional
units
after
wastewaters
have
been
treated
in
aggressive
biological
treatment
units)
and
K051
wastes
are
not included in this listing.
F038
Petroleum
refinery
secondary
(T)
(emulsified)
oil/water/solids
separation
sludge
-—
Any
sludge
or
float
generated
from
the
physical
or
chemical separation of oil/water/solids
in process wastewaters and oily cooling
wastewaters
from petroleum refineries.
Such
wastes
include,
but
are
not
126—725
12
limited
to,
all
sludges
and
floats
generated
in:
induced air
floatation
(IAF)
units,
tanks
and
impoundments,
and all sludges generated in DAF units.
Sludges
generated
in stormwater
units
that do not receive dry weather
flow,
sludges
generated
in
aggressive
biological
treatment
units
as
defined
in subsection
(b) (2)
(including sludges
generated
in
one
or
more
additional
units
after
wastewaters
have
been
treated
in
aggressive
biological
treatment units),
F037,
K048
and K051
wastes
are
not
included
in
this
listing.
F039
Leachate resulting from the
treatment,
(T)
storage
or
disposal
of
wastes
classified by more than one waste code
under
Subpart
D,
or from a mixture of
wastes classified under Subparts
C and
D.
(Leachate
resulting
from
the
management
of
one
or
more
of
the
following USEPA hazardous wastes and no
other
hazardous
wastes
retains
its
hazardous waste
code(s):
F020,
F021,
F022, P023, FO26,
FO27 or P028.)
BOARD NOTE:
The primary hazardous properties of these
materials
have
been
indicated
by
the
letters
T
(Toxicity),
R
(Reactivity),
I
(Ignitability),
and
C
(Corrosivity).
The letter H indicates Acute Hazardous
Waste.
b)
Listing
specific
definitions.
1)
For the purpose of the FO37 and FO.38 listings,
oil!
water/solids is defined as oil or water or solids.
2)
For the purposes of the F037 and F038 listings:
A)
Aggressive
biological
treatment
units
are
defined
as
units
which
employ
one
of
the
following four treatment methods:
activated
sludge; trickling filter; rotating biological
contactor
for
the
continuous
accelerated
biological oxidation of wastewaters; or, high-
rate aeration.
High—rate aeration is a system
of
surface
impoundments or
tanks,
in
which
intense
mechanical
aeration
is
used
to
completely mix the wastes, enhance biological
activity, and:
126—7 26
13
i)
The units employ a minimum of 6 horsepower
per million gallons of treatment volume;
and either
ii)
The hydraulic retention time of the unit
is no longer than
5 days; or
iii)
The hydraulic
retention
time
is
no
longer
than
30
days
and
the
unit
does
not
generate
a
sludge
that
is
a
hazardous
waste
by
the
toxicity
characteristic.
B)
Generators
and
treatment,
storage or
disposal
(TSD)
facilities have the burden
of proving
that their sludges are exempt from listing as
F037
or
F038
wastes
under
this
definition.
Generators and TSD facilities shall maintain,
in
their
operating
or
other
on
site
records,
documents and data sufficient to prove that:
i)
The
unit
is
an
aggressive
biological.
treatment
unit
as
defined
in
this
subsection; and
ii)
The
sludges
sought
to be exempted from
P037 or F038 were actually generated in
the aggressive biological treatment unit.
3)
Time of generation.
For the purposes of:
A)
The F037 listing, sludges are considered to be
generated at the moment of deposition in the
unit, where deposition is defined as at least
a
temporary
cessation
of
lateral
particle
movement.
B)
The F038 listing:
i)
Sludges
are considered to be generated at
the moment
of
deposition
in
the
unit,
where
deposition
is
defined
as
at
least
a
temporary
cessation
of
lateral
particle
movement; and
ii)
Floats are considered to be generated at
the moment they are formed in the top of
the unit.
(Source:
Amended at
15
Ill.
Reg.
,
effective
IT
IS
SO
ORDERED.
126—7 27
14
I, Dorothy M.
Gunn,
Clerk of the Illinois Pollution Control
hat the above Pr
on and Order
Board, do hereby cert
was adopted on the
___________
day of
~
1991, by a
vote of
7~)
~
£
Clerk
Illinois Pol(on
Control Board
126—728