TITLE
35:
ENVIRONMENTAL PROTECTION
SUBTITLE
G:
WASTE DISPOSAL
EC
CHAPTER I:
POLLUTION CONTROL BOARD
CLERK’S
SUBCHAPTER
C:
HAZARDOUS WASTE OPERATING REQUIREMENTS
SEP
4
2008
HAZARDOUS
PART 720
WASTE MANAGEMENT SYSTEM: GENERAL
‘
r,1utjon
3
STATE
OF
Control
IWNOIS
Board
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
720.104
Electronic Reporting
SUBPART B:
DEFINITIONS AND REFERENCES
Section
720.110
Definitions
720.111
References
SUBPART C:
RULEMAKING
PETITIONS AND OTHER
PROCEDURES
Section
720.120
Rulemaking
720.121
Alternative Equivalent Testing Methods
720.122
Waste
Delisting
720.123
Petitions
for Regulation
as
Universal Waste
720.130
Procedures
for Solid Waste Determinations
720.131
Solid Waste
Determinations
720.132
Boiler
Determinations
720.133
Procedures for Determinations
720.140
Additional Regulation of Certain Hazardous Waste Recycling
Activities
on a Case-by-Case
Basis
720.141
Procedures for Case-by-Case Regulation of Hazardous Waste Recycling
Activities
720.Append-ixAPPENUIX
A Overview of Federal RCRA Subtitle
C
(Hazardous Waste)
Regulations
AUTHORITY:
Implementing Sections 7.2, 13, and 22.4 and authorized
by
Section 27
of the Environmental Protection Act
[415
ILCS 5/7.2, 13, 22.4, and
27]
SOURCE: Adopted in R81-22
at 5
Ill. Reg. 9781, effective May 17, 1982; amended
and codified in R8l-22 at
6
Ill. Reg. 4828, effective May 17, 1982; amended in
R82-19
at
7 Ill. Reg. 14015, effective October 12, 1983; amended in R84-9 at
9
Ill. Reg. 11819, effective July 24, 1985; amended in R85-22 at 10 Ill. Reg. 968,
effective January 2, 1986; amended in R86-l at 10 Ill. Reg. 13998, effective
August 12, 1986; amended in R86-19 at 10 Ill. Reg. 20630, effective December 2,
1986; amended
in R86-28
at 11 Ill.
Reg. 6017, effective March 24, 1987;
amended
in R86-46 at
11 Ill. Reg.
13435,
effective August 4, 1987; amended in R87-5
at
11
Ill.
Reg.
19280, effective November 12, 1987; 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-l6
at
13 Ill. Reg. 362, effective
December 27, 1988; amended in R89-l at 13 Ill. Reg. 18278, effective November
13, 1989; amended in R89-2 at 14 Ill. Reg. 3075, effective February 20, 1990;
amended
in R89-9 at 14 Ill. Reg. 6225,
effective April 16, 1990; amended in R90-
10 at 14
Ill. Reg. 16450, effective
September 25, 1990; amended in R90-17 at 15
Ill. Reg.
7934,
effective
May 9,
1991; amended in R90-ll
at
15 Ill. Reg. 9323,
effective June 17, 1991; amended
in R91-l
at
15 Ill. Reg. 14446, effective
NovembcrSeotember 30, 1991;
amended in R91-l3
at
16 Ill. Reg. 9489, effective
June 9,
1992; amended in R92—l at 16
Ill. Reg. 17636, effective November 6,
1992;
amended in R92-lO at 17
Ill. Reg. 5625, effective March 26, 1993; amended
in
R93-4
at
17 Iii. Reg.
20545, effective November 22, 1993; amended in R93-16
at
18 Ill. Reg. 6720,
effective April 26, 1994; amended in R94-7 at 18 111. Reg.
12160, effective July
29, 1994; amended in R94-17
at
18 Ill. Reg. 17480,
effective November 23,
1994; amended in R95-6
at
19 Ill. Reg. 9508, effective
June
27, 1995; amended
in R95-20
at
20 Ill. Reg. 10929, effective August 1,
1996; amended in
R96-lO/R97-3/R97-5
at
22 111. Reg. 256, effective December 16,
1997; amended in
R98-l2
at
22 Ill. Reg. 7590, effective April 15, 1998; amended
in R97—21/R98-3/R98-5
at
22 111. Reg. 17496, effective September 28, 1998;
amended in
R98-21/R99-2/R99-7
at
23 111. Reg. 1704, effective January 19, 1999;
amended in R99-15 at
23 Ill. Reg. 9094, effective July 26, 1999; amended in R00-
5 at
24 Ill. Reg. 1063,
effective January
6,
2000; amended in R00-13 at 24 111.
Reg. 9443,
effective June 20, 2000; amended in R0l-3 at 25 Ill. Reg. 1266,
effective January
11, 2001; amended in R01-21/R0l-23 at 25 Ill. Reg. 9168,
effective July 9,
2001; amended in R02-l/R02-12/R02-17 at 26 Ill. Reg. 6550,
effective April
22, 2002; amended in R03-7 at 27 Ill. Reg. 3712,
effective
February 14, 2003;
amended in R03-18 at 27 Ill. Reg. 12713, effective
July
17,
2003; amended
in R05-8
at
29 Ill. Reg. 5974, effective April 13, 2005;
amended
in R05-2 at 29
111. Reg. 6290, effective April 22, 2005; amended in
R06-5/R06-
6/R06-7 at 30
Ill. Reg. 2930, effective February 23, 2006; amended in
R06-
16/R06-17/R06-l8
at
31 Ill. Reg. 730, effective December 20, 2006;
amended in
R07-5/R07-l4 at
32 Ill. Reg. 11726, effective July 14, 2008;
amended in R09-3
at
33
Ill. Reg.
, effective
SUBPART B:
DEFINITIONS AND REFERENCES
Section
720.110
Definitions
When used in 35
Ill. Adm. Code 720 through 728, 733, 738, and 739 only,
the
following terms
have the meanings given below:
“Aboveground
tank” means a device meeting the definition of tank that
is
situated
in such
a
way that the entire surface
area
of the
tank is completely
above the plane of the adjacent
surrounding surface and the entire surface area
of
the tank (including the tank
bottom) is able
to be
visually inspected.
“Active life
TT of a facility
means
the
period from the initial receipt of
hazardous waste at the
facility until the Agency receives certification of final
closure.
“Active portion”
means that portion of a facility where treatment, storage, or
disposal
operations are being or have been conducted after May 19, 1980, and
which is not a
closed portion.
(See
also “closed portion” and “inactive
portion.”)
“Administrator” means the Administrator of the United States
Environmental
Protection Agency or the Administrator’s designee.
“Agency”
means the Illinois Environmental Protection Agency.
‘Ancillary equipment”
means any device, including,
but
not limited to, such
devices
as
piping,
fittings, flanges, valves, and pumps, that is used to
distribute, meter,
or control the flow of hazardous waste from its point of
generation to storage
or treatment tanks, between hazardous waste storage and
treatment tanks to a
point of disposal onsite, or to a point of shipment for
disposal off-site.
“Aquifer” means a
geologic formation, group of formations, or part of a
formation
capable of yielding a significant amount of groundwater to wells or
springs.
“Authorized
representative” means the person responsible for the
overall
operation of a
facility or an operational unit
(i.e.,
part of a facility), e.g.,
the plant
manager, superintendent, or person of equivalent
responsibility.
TTBatteryTT
means
a
device that consists of one or more
electrically connected
electrochemical cells that is designed to receive, store, and
deliver electric
energy.
An electrochemical cell is a system consisting of an
anode, cathode,
and an
electrolyte, plus such connections
(electrical
and
mechanical)
as
may
be
needed to
allow the cell to deliver or
receive electrical energy. The term
battery also includes an intact,
unbroken battery from which the electrolyte has
been
removed.
“Board” means the Illinois
Pollution Control Board.
“Boiler” means an enclosed
device using controlled flame combustion and having
the
following characteristics:
Boiler physical characteristics.
The
unit must have physical provisions for
recovering and exporting thermal
energy
in the form of steam, heated fluids, or heated gases;
and the unit’s
combustion chamber and primary energy
recovery sections must
be
of integral
design. To be of integral
design, the combustion chamber and the primary energy
recovery sections
(such
as
waterwalls and superheaters) must be physically
formed into one
manufactured or assembled unit. A unit in which the combustion
chamber and the
primary energy recovery sections are joined only by ducts or
connections
carrying flue gas is not integrally designed; however,
secondary
energy recovery
equipment
(such
as
economizers or air preheaters) need not be
physically formed
into the same unit as the combustion chamber and the primary
energy
recovery section. The following units are not precluded from
being
boilers
solely
because
they are not of integral design: process
heaters
(units
that
transfer energy directly to a process
stream)
and fluidized bed
combustion
units; and
While in
operation, the unit must maintain a thermal energy
recovery
efficiency
of at
least
60
percent, calculated in terms of the recovered energy compared
with
the thermal value of the fuel; and
The
unit
must
export and utilize at least 75 percent of the
recovered energy,
calculated on an annual basis. In this calculation, no credit may be
given
for
recovered heat used internally in the
same
unit.
(Examples
of internal
use are
the
preheating of fuel or combustion
air, and the driving of induced or forced
draft fans or
feedwater pumps.); or
Boiler by
designation. The unit is one that the Board has determined, on
a
case-by-case
basis, to be a boiler, after considering the standards in Section
720.132.
‘Carbon regeneration unit’ means any enclosed thermal treatment device used
to
regenerate spent
activated
carbon.
“Cathode ray tube” or “CRT” means a vacuum tube, composed primarily of glass,
which is the visual or video display component of an electronic device. A
“used,
intact CRT” means a CRT whose vacuum has not been released. A “used,
broken CRT” means
glass
removed from its housing or casing whose vacuum has been
released.
“Certification”
means
a statement of professional opinion based upon knowledge
and belief.
“Closed portion”
means
that portion of a facility that an owner or operator has
closed in accordance
with
the approved facility closure plan and all applicable
closure requirements.
(See
also
“active
portion” and “inactive portion.”)
“Component” means
either
the
tank
or ancillary equipment of a tank system.
“Confined
aquifer” means an aquifer
bounded above and below by impermeable beds
or by beds of
distinctly lower permeability
than that
of
the aquifer
itself;
an
aquifer
containing confined groundwater.
“Container”
means any portable device in which
a
material is stored,
transported,
treated, disposed of, or otherwise handled.
“Containment building” means a hazardous waste management unit that is used
to
store
or treat hazardous waste pursuant
to
the provisions of Subpart DD of
35
Ill.
Adm.
Code
724 and Subpart DD of 35 Ill. Adm. Code 725.
“Contingency plan” means a document setting out an organized, planned and
coordinated course of action to be followed in case of a fire, explosion, or
release of hazardous waste or hazardous waste constituents that could threaten
human health or the environment.
“Corrosion expert” means a person who, by reason of knowledge of the physical
sciences and the principles of engineering and mathematics, acquired by a
professional education and related practical experience, is qualified to engage
in
the practice of corrosion control on buried or submerged metal piping
systems
and
metal tanks. Such a person must be certified as being qualified by the
National Association of Corrosion Engineers
(NACE)
or be a registered
professional engineer who has certification or licensing that includes education
and
experience in corrosion control on buried or submerged metal piping systems
and metal tanks.
“CRT collector” means a person who receives used, intact CRT5 for recycling,
repair, resale,
or donation.
“CRT glass manufacturer” means an operation or part of an operation that
uses a
furnace
to
manufacture CRT glass.
“CRT processing” means conducting all of the following activities:
Receiving broken
or intact
CRT5;
Intentionally
breaking intact CRTs or further breaking or separating broken
CRT5; and
Sorting or
otherwise managing glass removed from CRT monitors.
Designated
facility’ means either of the following entities:
A hazardous waste
treatment, storage, or disposal facility that has been
designated on the
manifest
by
the generator, pursuant
to 35
Ill. Adm. Code
722.120, of which
any of the following is true:
The facility has
received
a
RCRA permit
(or
interim
status)
pursuant to 35 Ill.
Adm. Code 702, 703,
and
705;
The facility has
received
a
RCRA permit from USEPA pursuant
to
40 CFF. 124 and
270
(2005)
The facility has
received
a
RCRA permit from
a
state authorized by USEPA
pursuant to 40
CFP. 271 (2005); or
The facility
is regulated pursuant to 35 Ill. Adm. Code
721.106(c) (2)
or Subpart
F of 35 111.
Adm. Code 266; or
A
generator site designated by the hazardous waste generator on the manifest to
receive
back
its
own waste as a return shipment from a designated hazardous
waste
treatment, storage, or disposal facility that has rejected the waste in
accordance with 35 Ill. Adm. Code
724.172(f)
or
725.172(f).
If a
waste is destined to a facility in a state other than Illinois that has
been
authorized by USEPA pursuant to 40 CFR 271, but which has not yet obtained
authorization
to
regulate that waste as hazardous, then the designated facility
must be a
facility allowed by the receiving state to accept such waste.
TDestination
facility” means a facility that treats, disposes of,
or recycles
a
particular category of universal waste, except those management
activities
described in
35
Ill. Adm. Code
733.113(a)
and
(C)
and
733.133(a)
and
(c).
A
facility
at
which a particular category of universal waste is only
accumulated
is
not
a
destination facility for the purposes of
managing
that
category
of
universal waste.
“Dike” means an embankment
or ridge
of
either natural or manmade materials
used
to
prevent the
movement of liquids, sludges, solids, or other materials.
“Dioxins and
furans” or “D/F” means tetra, penta- , hexa- , hepta- , and octa
chlorinated
dibenzo dioxins and furans.
“Director”
means the Director of the Illinois Environmental Protection Agency.
“Discharge” or “hazardous waste discharge” means the accidental or intentional
spilling,
leaking, pumping, pouring, emitting, emptying, or dumping of hazardous
waste
into or on any land or water.
“Disposal” means the discharge, deposit, injection, dumping, spilling, leaking,
or
placing of any solid waste or hazardous waste into or on any land
or water
so
that
such solid waste or hazardous waste or any constituent thereof
may
enter
the
environment or be emitted into the air or discharged into any waters,
including groundwaters.
“Disposal
facilityTT
means a facility or part of a facility at which hazardous
waste is intentionally placed into or on any land or water and at which waste
will remain after closure. The term disposal facility does not include a
corrective action management unit
(CANU)
into which remediation wastes are
placed.
“Drip pad” means an
engineered
structure consisting of a
curbed, free-draining
base,
constructed of non-earthen
materials
and designed to convey
preservative
kick-back or drippage
from
treated
wood, precipitation and surface water runon
to an associated
collection system
at
wood preserving plants.
“Elementary
neutralization unit” means
a
device
of
which the following is
true:
It is used for
neutralizing wastes that are hazardous only
because
they exhibit
the corrosivity
characteristic defined in
35
Ill. Adm.
Code
721.122 or which
are
listed in
Subpart U of
35
Ill. Adm.
Code
721 only for this reason; and
It meets the
definition of tank, tank system, container, transport vehicle,
or
vessel in this
Section.
“EPA hazardous
waste number” or “USEPA hazardous waste number” means the number
assigned by USEPA to each
hazardous
waste
listed
in Subpart
D
of 35
Iii.
Adm.
Code
721 and to each characteristic identified in Subpart C of 35
Ill. Adm.
Code
721.
“EPA identification number” or “USEPA identification number” means
the
number
assigned by USEPA pursuant to 35
Iii. Adm.
Code 722 through 725 to
each
generator; transporter;
and treatment, storage,
or
disposal facility.
“EPA region”
or “USEPA region” means the
states
and territories found in any
one
of the
following ten regions:
Region
I: Maine, Vermont, New Hampshire, Massachusetts, Connecticut, and Rhode
Island.
Region II: New York, New Jersey, Commonwealth of Puerto Rico, and the U.S.
Virgin Islands.
Region III: Pennsylvania, Delaware, Maryland, West Virginia, Virginia, and the
District of Columbia.
Region IV: Kentucky, Tennessee, North Carolina, Mississippi, Alabama, Georgia,
South
Carolina, and Florida.
Region V: Minnesota, Wisconsin, Illinois, Michigan, Indiana, and Ohio.
Region VI: New Mexico, Oklahoma, Arkansas, Louisiana, and Texas.
Region VII:
Nebraska, Kansas, Missouri, and
Iowa.
Region
VIII: Montana, Wyoming, North Dakota, South Dakota, Utah, and Colorado.
Region
IX: California, Nevada, Arizona, Hawaii, Guam, American Samoa, and
Commonwealth
of the Northern Mariana Islands.
Region
X:
Washington, Oregon, Idaho,
and Alaska.
“Equivalent method” means any testing or analytical
method approved by the Board
pursuant to
Section 720.120.
“Existing hazardous waste management (HWM)
facility” or “existing facility”
means
a
facility that was in operation or for which construction
commenced on or
before November 19, 1980. A facility had commenced construction
if the owner or
operator had obtained the federal,
State,
and local approvals
or permits
necessary
to
begin physical construction and either
of
the
following had
occurred:
A continuous on-site, physical construction program had
begun; or
The
owner
or operator had entered into contractual
obligations that could not
be
canceled or modified without substantial
loss
for
physical construction of the
facility
to be
completed within
a
reasonable time.
“Existing portion” means that land surface area
of an existing waste management
unit,
included in the original Part A permit application,
on which wastes have
been
placed prior
to
the issuance of
a
permit.
“Existing tank system” or “existing component” means
a tank system or component
that
is
used
for the storage or treatment of hazardous
waste and which was in
operation, or for which installation was commenced, on or prior
to
July 14,
1986. Installation will be considered
to
have commenced if the owner or
operator has obtained all federal, State, and local approvals or permits
necessary
to
begin physical construction of the site or installation of
the tank
system and if either of the following is true:
A continuous on-site physical construction or installation program has
begun; or
The owner or operator has entered into contractual obligations that cannot
be
canceled or modified without substantial loss for physical construction of
the
site or installation of the tank system to be completed within
a
reasonable
time.
“Explosives or munitions emergency” means a situation involving the
suspected or
detected presence of unexploded ordnance
(UXO),
damaged or deteriorated
explosives or munitions, an improvised explosive device
(lED),
other
potentially
explosive material or device, or other potentially harmful military chemical
munitions or device, that creates an actual or potential imminent threat
to
human health, including safety, or the environment, including property,
as
determined by an explosives or munitions emergency response specialist.
Such
situations may require immediate and expeditious action
by
an explosives or
munitions emergency response specialist to control, mitigate, or eliminate
the
threat.
“Explosives or munitions emergency response” means all
immediate response
activities by an explosives and munitions emergency response specialist
to
control, mitigate, or eliminate the actual or potential threat encountered
during an explosives or munitions emergency. An explosives or munitions
emergency response may include in-place render-safe procedures, treatment,
or
destruction of the explosives or munitions or transporting those items
to
another location to be rendered safe, treated, or destroyed. Any reasonable
delay
in the completion of an
explosives or munitions emergency response caused
by a
necessary,
unforeseen,
or uncontrollable circumstance will not terminate
the explosives or
munitions emergency.
Explosives and munitions emergency
responses can occur on
either
public or private lands and are not limited to
responses
at
RCRA
facilities.
“Explosives or munitions emergency response specialist” means an individual
trained in chemical
or conventional
munitions or explosives handling,
transportation,
render-safe
procedures, or destruction techniques. Explosives
or munitions emergency response specialists include United States Department of
Defense
(USDOD)
emergency explosive ordnance disposal
(EOD),
technical escort
unit
(TEU),
and USDOD-certified civilian or contractor personnel and other
federal,
State,
or local government or civilian personnel who are similarly
trained in explosives or munitions emergency responses.
“Facility” means the
following:
All contiguous
land and structures,
other appurtenances, and
improvements
on the
land used for
treating, storing, or
disposing of hazardous
waste.
A
facility
may consist
of several treatment, storage, or disposal operational units
(e.g.,
one or more
landfills, surface impoundments, or combinations of
them)
For the purpose
of implementing corrective action pursuant
to 35
Ill. Adm.
Code
724.201 or 35
Ill. Adm.
Code
727.201, all contiguous property under the control
of the owner
or operator seeking
a
permit under Subtitle
C
of RCRA. This
definition also
applies
to
facilities implementing corrective action pursuant
to
RCRA section
3008(h).
Notwithstanding
the immediately-preceding paragraph of this definition,
a
remediation waste
management site is not
a
facility that is
subject to 35
Iii.
Adm. Code 724.201, but a
facility
that is subject to corrective action
requirements if the site is located within such a facility.
“Federal agency”
means any department, agency, or other instrumentality
of the
federal government,
any independent
agency
or establishment of the federal
government,
including any government corporation and the Government Printing
Office.
“Federal, State,
and local approvals or permits necessary
to
begin physical
construction”
means permits and approvals required under federal,
State,
or
local hazardous waste control statutes, regulations, or ordinances.
“Final closure” means the closure of all hazardous waste management units at the
facility in accordance with all applicable closure requirements so that
hazardous waste management activities pursuant to 35 Ill. Adm. Code 724 and 725
are
no longer conducted at the facility unless subject to the provisions of
35
Ill.
Adm. Code 722.134.
“Food-chain crops” means tobacco, crops grown for human consumption, and crops
grown for feed for animals whose products are consumed by humans.
“Freeboard” means the
vertical
distance between the top of a tank or surface
impoundment dike and the surface of the waste contained therein.
“Free liquids”
means liquids that
readily separate from the solid portion of a
waste under
ambient temperature and pressure.
GasificationTT
means, for
the purpose of complying with 35 Ill. Adm.
Code
721.104
(a) (12) (A),
a
process
conducted in an enclosed device or system that is
designed and operated to process petroleum feedstock, including oil-bearing
hazardous secondary
materials
through a series of highly controlled
steps-r
utilizing thermal decomposition, limited oxidation, and
gas
cleaning-r
to
yield
a
synthesis gas composed primarily of hydrogen and carbon monoxide
gas.
“Generator” means
any
person, by site, whose act or process produces hazardous
waste identified
or listed
in 35 Ill. Adm. Code 721 or whose act first
causes a
hazardous waste to become subject to regulation.
“Groundwater” means water
below the land surface in a zone of saturation.
“Hazardous waste” means
a
hazardous waste
as
defined in
35 Ill. Adm. Code
721. 103.
“Hazardous waste constituent” means
a
constituent that
caused the hazardous
waste
to
be listed in Subpart D of
35
Ill. Adm.
Code
721,
or a constituent
listed in
35
Ill. Adm.
Code
721.124.
“Hazardous waste management unit” is
a
contiguous area
of land on or in which
hazardous waste is placed, or the largest area in which
there is significant
likelihood of mixing hazardous waste constituents in the
same area. Examples of
hazardous waste management units
include a
surface impoundment,
a waste pile,
a
land
treatment area,
a
landfill
cell,
an incinerator,
a tank and its associated
piping
and underlying containment system,
and a
container
storage area. A
container alone
does
not constitute
a unit; the
unit
includes containers, and
the
land or
pad
upon which they
are placed.
“Inactive portion” means that
portion of a
facility
that is not operated after
November 19, 1980.
(See
also “active portion” and “closed
portion.”)
“Incinerator” means any enclosed device of which the following
is true:
The
facility uses controlled flame combustion, and
both of the following are
true of the facility:
The facility does not meet the criteria for classification
as a
boiler,
sludge
dryer, or carbon regeneration unit, nor
The
facility is not listed as an industrial furnace; or
The
facility meets the definition of infrared incinerator
or plasma arc
incinerator.
“Incompatible waste” means a hazardous waste that is unsuitable for the
following:
Placement in a particular device or facility because it may
cause
corrosion
or
decay of containment materials (e.g., container inner liners or tank walls);
or
Commingling with another waste
or material under uncontrolled conditions
because
the
commingling might produce
heat or pressure, fire, or explosion, violent
reaction, toxic dusts, mists, fumes
or gases, or flammable fumes or gases.
(See
Appendix E to 35 Ill. Adm.
Code 724 and Appendix E to 35 Ill. Adm. Code 725
for references that list examples.)
TTlndustrial
furnace’ means any of the following
enclosed
devices
that are
integral components of manufacturing processes
and that use thermal treatment
to
accomplish recovery of materials or energy:
Cement kilns;
Lime kilns;
Aggregate kilns;
Phosphate kilns;
Coke ovens;
Blast furnaces;
Smelting, melting and refining furnaces
(including pyrometallurgical devices
such
as
cupolas, reverberator furnaces,
sintering machines, roasters, and
foundry
furnaces)
Titanium
dioxide chloride
process oxidation reactors;
Methane reforming furnaces;
Pulping
liquor recovery
furnaces;
Combustion devices
used
in the recovery
of sulfur values from spent sulfuric
acid;
Halogen acid furnaces
(HAF5)
for the production
of acid from halogenated
hazardous waste generated
by
chemical production
facilities where
the
furnace is
located
on the site of a chemical production facility, the acid product
has a
halogen acid content of at least three percent, the acid product is
used in a
manufacturing process, and, except for hazardous waste burned
as
fuel, hazardous
waste fed to the furnace has a minimum halogen content of 20 percent, as
generated; and
Any
other such device as the Agency determines
to be
an industrial furnace
on
the
basis of one or more of the following factors:
The
design and use of the device primarily
to
accomplish recovery of material
products;
The
use of the device to burn or reduce raw materials
to
make
a
material
product;
The
use of the device to burn or reduce secondary materials as effective
substitutes for raw materials, in processes using raw materials as principal
feedstocks;
The use of
the device
to
burn or reduce
secondary materials as ingredients in an
industrial process
to
make
a
material product;
The use
of the device in common industrial practice
to
produce
a
material
product; and
Other relevant
factors.
“Individual generation site” means
the contiq-uous site at or on which one
or
more hazardous wastes are generated.
An
individual
generation site, such
as a
large manufacturing plant, may have one or more
sources of hazardous waste
but
is considered a single or individual generaLion
site if the site or property is
contiguous.
“Infrared incinerator” means any enclosed device
that uses electric powered
resistance heaters as a source of radiant heat
followed by an afterburner using
controlled flame combustion and which
is
not listed
as an industrial furnace.
“Inground tank” means a device meeting
the definition of tank whereby a portion
of the
tank wall is situated
to
any
degree within the ground, thereby preventing
visual inspection of that external
surface area of the tank that is in the
ground.
“In operation”
refers
to a
facility
that is treating, storing, or disposing
of
hazardous
waste.
“Injection well” means a well into which fluids
are being injected.
(See
also
“underground injection.
“)
“Inner liner” means a continuous layer of material placed inside
a tank or
container that protects the construction materials of
the
tank
or container from
the contained waste or reagents used
to
treat the waste.
“Installation inspector” means a person who, by reason of knowledge of
the
physical sciences and the principles of engineering, acquired
by a
professional
education and related practical experience, is qualified
to
supervise the
installation of
tank systems.
“International shipment” means the transportation of hazardous waste into
or out
of the jurisdiction of
the United
States.
“Lamp” or
“universal waste lamp” means
the balb or tube portion of an electric
lighting
device. A lamp is specifically
designed to produce radiant energy,
most
often in the ultraviolet, visible,
or infrared regions of the
electromagnetic
spectrum. Examples
of common universal waste lamps include,
but
are not limited to,
fluorescent, high
intensity discharge, neon, mercury vapor,
high-pressure sodium,
and metal
halide lamps.
‘Land treatment facility”
means
a facility or part of a facility at which
hazardous waste
is applied onto or
incorporated into the soil surface; such
facilities
are disposal facilities
if the waste will remain after closure.
“Landfill” means
a
disposal facility
or part of a facility where hazardous waste
is placed
in or on land and which is
not a pile, a land treatment facility,
a
surface
impoundment, an underground injection
well, a salt dome formation,
a
salt bed
formation, an underground mine,
a
cave, or
a
corrective
action
management unit
(CAMU).
“Landfill
cellTT
means a discrete volume of
a
hazardous waste landfill that
uses
a
liner to provide isolation of wastes from
adjacent
cells or wastes. Examples
of
landfill cells are trenches and pits.
“LOS” means
leak detection
system.
“Leachate”
means any
liquid, including
any suspended
components in the
liquid,
that has
percolated through
or drained
from hazardous waste.
“Liner”
means
a continuous layer
of natural or
manmade materials
beneath or on
the sides
of
a
surface impoundment,
landfill,
or
landfill cell that
restricts
the downward
or lateral
escape of hazardous
waste,
hazardous
waste constituents,
or leachate.
“Leak-detection
system” means
a system
capable of
detecting the
failure of
either
the
primary
or secondary
containment
structure
or the presence
of a
release of
hazardous
waste or accumulated
liquid
in
the secondary containment
structure.
Such a system
must employ
operational
controls
(e.g., daily visual
inspections
for releases
into the secondary
containment system
of aboveground
tanks)
or
consist
of an interstitial
monitoring
device designed
to detect
continuously
and
automatically the
failure
of the
primary or secondary
containment
structure
or the presence
of
a
release
of
hazardous waste
into the
secondary
containment
structure.
“Management”
or “hazardous
waste
management” means
the
systematic control
of the
collection,
source
separation, storage,
transportation,
processing,
treatment,
recovery,
and disposal
of hazardous
waste.
“Manifest”
means the shipping
document USEPA
Form 8700-22 (including,
if
necessary,
USEPA Form
8700-22A)
originated and
signed by the generator
or
of feror
that contains
the information
required
by
Subpart
B
of 35
Ill. Adm. Code
722 and the
applicable
requirements
of 35 Ill. Adm. Code
722
through
727.
“Manifest
tracking
numberT
means the alphanumeric
identification
number
(i.e.,
a
unique
three
letter suffix preceded
by nine numerical
digits) that
is
pre
printed
in
Item
4 of the manifest
by a registered
source.
“Mercury-containing
equipment”
means a
device or part
of
a
device
(including
thermostats,
but
excluding
batteries and lamps)
that
contains elemental
mercury
integral
to
its function.
“Military
munitions” means
all ammunition
products and components
produced or
used by
or
for the United
States
Department
of
Defense or the United
States
Armed Services
for national defense
and
security,
including military
munitions
under the
control
of the United
States
Department
of
Defense
(USDOD),
the United
States Coast
Guard, the
United States Department
of Energy
(USDOE),
and National
Guard
personnel.
The term
military munitions
includes: confined
gaseous,
liquid,
and
solid propellants,
explosives, pyrotechnics,
chemical
and riot
control
agents,
smokes, and incendiaries
used
by
USDOD components,
including
bulk
explosives and
chemical warfare
agents, chemical
munitions, rockets,
guided
and
ballistic missiles,
bombs, warheads,
mortar rounds,
artillery ammunition,
small
arms
ammunition, grenades,
mines, torpedoes,
depth charges,
cluster
munitions
and
dispensers, demolition
charges,
and devices and components
of
these items
and
devices.
Military
munitions do not
include
wholly inert
items,
improvised
explosive
devices,
and nuclear
weapons, nuc]ear
devices,
and
nuclear
components
of
these items
and devices.
However, the
term
does include
non
nuclear
components
of
nuclear
devices, managed
under
USDOE’s nuclear
weapons
program after
all
sanitization
operations required
under
the Atomic Energy
Act
of
1954
(42
USC
2014
et seq.), as
amended, have been
completed.
‘Mining overburden
returned
to the
mine site” means any
material
overlying
an
economic
mineral
deposit
that is
removed
to gain access
to
that
deposit and
is
then
used
for
reclamation
of a surface mine.
“Miscellaneous
unit”
means
a
hazardous
waste management
unit where hazardous
waste
is
treated, stored,
or disposed of
and that is
not a container;
tank;
surface
impoundment;
pile; land
treatment
unit;
landfill; incinerator;
boiler;
industrial
furnace;
underground
injection
well with
appropriate technical
standards
pursuant
to 35 Iii. Adm.
Code 730;
containment
building; corrective
action
management unit
(CAMU)
;
unit eligible
for
a
research,
development,
and
demonstration
permit pursuant
to
35
Ill. Adm.
Code
703.231;
or staging pile.
“Movement”
means
hazardous waste
that is transported
to a facility
in an
individual
vehicle.
“New
hazardous
waste management
facility”
or “new facility”
means a facility
that
began
operation, or for
which construction
commenced after
November 19,
1980.
(See
also
“Existing hazardous
waste management
facility.”)
“New tank
system” or
“new tank component”
means
a
tank system
or component
that
will
be used
for the storage
or treatment
of hazardous waste
and for which
installation
commenced after
July 14, 1986;
except,
however, for
purposes of
35
Ill. Adm.
Code
724.293(g)
(2)
and
725.293(g)
(2),
a new
tank system is
one for
which
construction
commenced after
July 14, 1986.
(See
also “existing
tank
system.”)
“Onground
tank”
means a device
meeting the definition
of tank that
is situated
in such
a way
that
the bottom of
the tank is on
the
same level as the
adjacent
surrounding
surfaces
so that the external
tank
bottom
cannot be visually
inspected.
“On-site”
means
the same or
geographically contiguous
property
that may be
divided
by
public or
private right-of-way,
provided
the
entrance and exit
between
the
properties
is at a crossroads
intersection
and
access
is
by
crossing
as opposed
to
going along
the right-of-way.
Noncontiguous
properties
owned
by
the
same
person but
connected
by a right-of-way
that
the owner controls
and to
which
the public
does
not
have
access is also
considered
on-site property.
“Open
burning”
means the
combustion
of any material
without
the following
characteristics:
Control of
combustion
air
to
maintain
adequate
temperature
for efficient
combustion;
Containment
of the combustion
reaction in an
enclosed
device to
provide
sufficient
residence
time and mixing
for complete
combustion; and
Control of
emission of
the
gaseous
combustion
products.
(See
also
“incineration”
and
“thermal treatment.”)
“Operator”
means
the
person responsible
for the overall
operation of a
facility.
“Owner”
means
the
person
that owns a facility
or part of a facility.
“Partial closure”
means
the
closure
of a hazardous
waste
management unit
in
accordance
with the applicable
closure requirements
of 35 Ill.
Adm.
Code
724
or
725
at
a
facility
that
contains
other active hazardous
waste management
units.
For
example,
partial closure
may
include
the closure
of
a
tank
(including
its
associated
piping and underlying
containment
systems),
landfill
cell, surface
impoundment,
waste
pile, or other
hazardous
waste management
unit,
while other
units of the
same
facility continue
to operate.
‘Performance
Track member
facility”
means a facility
that has
been
accepted
by
USEPA
for
membership
in the
National
Environmental
Performance
Track
Program
(Program)
and
which is still
a
member
of that
Program.
The National
Environmental
Performance
Track Program
is a voluntary,
facility-based,
program
for
top
environmental
performers.
A program member
must demonstrate
a good
record
of
compliance
and
past success
in achieving environmental
goals,
and it
must
commit
to
future
specific quantified
environmental
goals, environmental
management
systems,
local
community outreach,
and annual reporting
of measurable
results.
BOARD
NOTE:
The National
Environmental
Performance
Track
program
is operated
exclusively
by
USEPA. USEPA
established
the program
in 2000
(see
65 Fed.
Reg.
41655
(July
6,
2000))
and
amended it in
2004
(see
69
Fed.
Reg. 27922 (May
17,
2004)) .
USEPA
confers membership
in the program
on application
of interested
and eligible
entities.
Information
about the
program
is available
from a
website maintained
by
USEPA:
www.epa.gov/
performancetrack.
“Person”
means
an individual,
trust,
firm,
joint stock
company,
federal
agency,
corporation
(including
a
government
corporation)
, partnership,
association,
state,
municipality,
commission,
political subdivision
of
a state,
or any
interstate body.
“Personnel”
or “facility personnel”
means
all persons
who work
at
or oversee
the
operations
of
a
hazardous waste
facility
and
whose
actions or failure
to act
may
result in
noncompliance
with
35
Ill.
Adm. Code
724 or
725.
“Pesticide”
means any substance
or mixture
of
substances intended
for
preventing,
destroying, repelling,
or mitigating
any
pest or intended
for
use as
a
plant
regulator,
defoliant, or
desiccant,
other
than any article
that
fulfills
one of the
following
descriptions:
It
is a
new animal drug under
section
201(v)
of the
Federal
Food, Drug and
Cosmetic
Act
(FFDCA; 21 USC
321(v)),
incorporated
by
reference
in Section
720.111(c);
It is an
animal drug that
has been determined
by
regulation
of the federal
Secretary
of
Health and Human
Services pursuant
to
FFDCA section
512
(21
USC
360b),
incorporated
by reference
in Section
720.111(c),
to be an
exempted
new
animal drug;
or
It is an
animal feed under
FFDCA section
201(w)
(21
USC
321(w)),
incorporated
by
reference
in
Section
720.111(c),
that bears
or
contains any
substances
described
in
either of
the
two
preceding
paragraphs of this
definition.
BOARD NOTE:
The
second exception
of corresponding
40
CFR
260.10 reads
as
follows:
“Is
an animal drug
that has
been determined
by
regulation
of
the
Secretary
of
Health and Human
Services
not to be a new
animal drug.”
This
is
very similar
to
the language of
section
2(u)
of the
Federal Insecticide,
Fungicide,
and Rodenticide
Act (FIFRA;
7 USC
136(u)).
The three exceptions,
taken
together, appear
intended not
to include as
pesticide
any material
within
the
scope of
federal Food
and Drug Administration
regulation.
The Board
codified
this
provision
with
the intent of retaining
the same meaning
as its
federal counterpart
while
adding
the definiteness
required under Illinois
law.
pile” means any
noncontainerized
accumulation
of solid, non-flowing hazardous
waste that is used
for
treatment or
storage, and that is not
a
containment
building.
TTplasma
arc
incineratorlT
means any enclosed
device that uses
a
high intensity
electrical discharge or arc as a source
of heat followed by an afterburner
using
controlled flame combustion and which is
not listed as an industrial furnace.
“Point source” means any discernible,
confined, and discrete conveyance,
including, but not
limited
to, any pipe, ditch,
channel, tunnel, conduit, well,
discrete fissure,
container,
rolling stock,
concentrated animal feeding
operation, or
vessel
or other floating craft
from which pollutants are or may
be
discharged. This
term
does not include return
flows from irrigated agriculture.
“Publicly
owned
treatment
worksTT
or “POTW” is
as
defined
in 35 Ill. Adm.
Code
310.110.
“Qualified
groundwater
scientist” means
a
scientist
or engineer who has received
a baccalaureate
or postgraduate
degree in the natural
sciences or engineering,
and has
sufficient training
and experience in groundwater
hydrology and related
fields, as
demonstrated
by state registration, professional
certifications, or
completion of
accredited
university courses that enable
the individual to make
sound
professional judgments
regarding groundwater monitoring
and contaminant
rate and
transport.
BOARD NOTE: State
registration
includes, but is not limited
to, registration
as
a
professional engineer
with the Department of Professional
Regulation, pursuant
to 225
ILCS 325 and
68
Ill.
Adm. Code 1380. Professional
certification
includes, but
is not limited
to, certification under the
certified groundwater
professional program of
the National Ground Water Association.
“RCRA” means the Solid Waste Disposal
Act, as amended
by
the Resource
Conservation and Recovery Act of
1976, as amended
(42
USC
6901
et seq.).
“RCRA standardized permit” means
a RCRA permit issued pursuant
to
Subpart
J of
35
Ill. Adm. Code 703 and Subpart
G of 35 Ill. Adm. Code 702 that authorizes
management of hazardous waste. The
RCRA standardized permit may have two
parts:
a
uniform portion issued in all
cases and a supplemental portion issued
at the
discretion of the Agency.
“Regional Administrator” means the Regional Administrator
for the USEPA region
in which the facility is located or the Regional Administrator’s
designee.
“Remediation waste” means all solid and hazardous
wastes, and all media
(including groundwater, surface water, soils, and
sediments)
and debris that
are
managed for implementing cleanup.
“Remediation waste management
site” means a facility where
an owner or operator
is or
will
be
treating,
storing, or disposing of hazardous
remediation wastes.
A
remediation waste
management site is not
a
facility
that is subject to
corrective action pursuant
to 35 Ill. Adm.
Code
724.201,
but a remediation waste
management site is
subject to corrective action requirements
if the site is
located
in such
a
facility.
“Replacement unit” means
a
landfill,
surface impoundment, or waste
pile unit
from which all or substantially
all of the waste is removed,
and
which is
subsequently reused to treat, store,
or dispose of hazardous waste.
Replacement
unit
does
not include a unit from which waste is removed
during closure, if the
subsequent reuse
solely
involves the disposal of waste from
that
unit
and other
closing units or
corrective
action areas at the facility, in accordance
with a
closure or
corrective
action plan approved
by
USEPA or the Agency.
‘Representative sample”
means a sample of a universe or whole
(e.g.,
waste
pile,
lagoon, groundwater) that
can be expected to exhibit the average properties
of
the universe or whole.
“Runoff”
means
any rainwater,
leachate, or other liquid that drains over land
from
any part
of
a
facility.
“Runon”
means
any rainwater,
leachate, or other liquid that drains over land
onto
any part
of
a
facility.
“Saturated
zone” or “zone of
saturation” means that part of the earth’s crust
in
which
all
voids are filled with
water.
“SIC code”
means “Standard
Industrial Classification code,”
as
assigned
to a
site by the
United
States
Department
of Transportation, Federal Highway
Administration,
based
on the particular
activities that occur on the site,
as
set forth
in its publication “Standard
Industrial Classification Manual,”
incorporated by
reference in Section
720.111(a).
“Sludge”
means any solid, semi-solid,
or liquid waste generated from a
municipal, commercial, or industrial wastewater
treatment plant, water supply
treatment plant, or air pollution control
facility, exclusive of the treated
effluent from
a
wastewater treatment plant.
“Sludge dryer” means any enclosed thermal treatment
device that is used to
dehydrate sludge and which has
a
total thermal input,
excluding the heating
value of the sludge itself, of 2,500 Btu/lb or less
of sludge treated on a wet-
weight basis.
“Small quantity generator” means a generator that generates
less than 1,000 kg
of hazardous waste in a calendar month.
“Solid waste” means a solid waste as defined in 35 Ill. Adm.
Code
721.102.
“Sorbent” means a material that is used to soak up free liquids
by
either
adsorption or absorption, or both. “Sorb” means to either adsorb or
absorb, or
both.
“Staging pile’ means an accumulation of solid, non-flowing “remediation waste”
(as
defined in this
Section)
that is not a containment building
and that is used
only during remedial operations for temporary storage
at a
facility.
Staging
piles must be designated by the Agency according
to 35
Ill. Adm.
Code
724.654.
“State” means any
of
the several states, the District of Columbia, the
Commonwealth
of Puerto
Rico, the Virgin Islands, Guam, American Samoa, and
the
Commonwealth
of the Northern
Mariana Islands.
“Storage” means the holding of hazardous
waste for a temporary period, at the
end
of which the hazardous waste is treated,
disposed of, or stored elsewhere.
“Sump” means
any pit
or reservoir that meets the definition of tank and
those
troughs or
trenches connected
to it that serve to collect hazardous waste for
transport
to
hazardous waste storage, treatment,
or disposal facilities; except
that, as
used
in the landfill, surface impoundment,
and waste pile rules, sump
means any lined pit or reservoir that serves
to collect liquids drained from
a
leachate collection and removal system or leak
detection system for subsequent
removal from the system.
Surface impoundment” or ‘impoundment’ means
a facility or part of a facility
that is
a
natural topographic depression, manmade
excavation, or diked area
formed primarily of earthen materials (although
it may be lined with manmade
materials)
that is designed
to
hold an
accumulation of liquid wastes or wastes
containing free liquids and which is not an
injection well. Examples of surface
impoundments are holding, storage, settling
and aeration pits, ponds, and
lagoons.
“Tank” means a stationary device, designed
to contain an accumulation of
hazardous waste that is constructed primarily
of nonearthen materials (e.g.,
wood, concrete, steel, plastic) that provide structural
support.
“Tank system” means a hazardous waste storage or treatment
tank and its
associated ancillary equipment and containment
system.
“TEQ” means toxicity equivalence, the international
method of relating the
toxicity of various dioxin and furan
congeners to the toxicity of 2,3,7,8-
tctrachlorodibcnzotetra-chlorodibenzo-p-dioxin.
“Thermal treatment” means the treatment of hazardous
waste in a device that
uses
elevated temperatures as the primary means
to
change
the
chemical,
physical, or
biological character or composition of the hazardous waste. Examples of
thermal
treatment processes are incineration, molten salt, pyrolysis, calcination,
wet
air oxidation, and
microwave discharge.
(See
also “incinerator” and
“open
burning.”)
“Thermostat” means a
temperature
control device that contains metallic mercury
in an ampule
attached
to a
bimetal
sensing element and mercury-containing
ampules
that have been removed from
such a temperature control device in
compliance with
35
Ill. Adm.
Code 733.113(c)
(2)
or
733.133(c) (2).
“Totally enclosed treatment facility” means
a facility for the treatment of
hazardous
waste that is directly connected
to an industrial production process
and
which is constructed and operated
in a manner that prevents the release
of
any
hazardous waste or any constituent
thereof into the environment during
treatment. An
example
is a pipe in which waste acid is neutralized.
“Transfer
facility” means any
transportation related facility, including
loading
docks,
parking areas, storage
areas, and other similar areas where shipments
of
hazardous
waste are held during the
normal course of transportation.
“Transport vehicle” means a motor vehicle
or rail car used for the
transportation of cargo by any mode. Each cargo-carrying
body
(trailer,
railroad freight car,
etc.)
is a separate transport vehicle.
“Transportation” means the movement
of hazardous waste
by
air, rail, highway,
or
water.
“Transporter” means a person engaged in
the off-site transportation of hazardous
waste
by air, rail, highway, or water.
“Treatability
study”
means the
following:
A
study in
which
a
hazardous waste
is subjected to a treatment process
to
determine the
following:
Whether
the waste
is amenable
to the treatment process;
What
pretreatment
(if
any)
is required;
The optimal process
conditions
needed to achieve the desired
treatment;
The
efficiency
of
a
treatment
process for a specific waste or wastes;
and
The characteristics
and volumes
of residuals from
a
particular treatment
process;
Also included
in this
definition for the purpose of
35
Ill. Adm.
Code 721.104(e)
and
Ct)
exemptions are liner
compatibility, corrosion and other material
compatibility
studies, and
toxicological and health effects studies. A
treatability study
is not
a means to commercially treat or dispose of hazardous
waste.
Treatment”
means any method,
technique, or process, including neutralization,
designed to
change the physical,
chemical, or biological character or
composition
of any hazardous waste
so as to neutralize the waste, recover
energy
or
material resources from the waste,
or render the waste non-hazardous or
less
hazardous;
safer
to
transport,
store, or dispose of; or amenable for recovery,
amenable
for storage, or reduced
in
volume.
“Treatment zone” means
a
soil area
of the unsaturated zone of a land treatment
unit within which hazardous constituents
are degraded, transformed, or
immobilized.
“Underground
injection” means
the subsurface emplacement of fluids through
a
bored, drilled,
or driven well
or through a dug well, where the depth of
the dug
well is
greater than the largest
surface dimension.
(See
also “injection
well.”)
“underground tank” means a device meeting the
definition of tank whose entire
surface area is totally below the surface of
and
covered
by the ground.
“Unfit-for-use tank system’
T means a tank system that has
been determined,
through an integrity assessment or other inspection,
to be
no longer
capable of
storing or
treating hazardous
waste without posing
a
threat of release of
hazardous waste
to
the environment.
“United
States”
means the
50 states, the District of Columbia, the Commonwealth
of
Puerto Rico, the
U.S.
Virgin
Islands, Guam, American Samoa, and the
Commonwealth of the Northern Mariana
Islands.
Tiuniversal
wasteTl
means any of the following
hazardous wastes that are managed
pursuant
to
the universal waste requirements
of 35 111. Adm. Code 733:
Batteries,
as
described in
35
Ill.
Adm. Code 733.102;
Pesticides, as described in
35
Ill.
Adm. Code 733.103;
Mercury-containing
equipment,
as
described
in 35 Ill.
Adm.
Code
733.104; and
Lamps, as
described
in 35 111. Adm.
Code 733.105.
Universal
waste handler’
means either
of the following:
A generator
(as
defined in this
Section)
of universal
waste; or
The
owner or
operator
of a facility,
including
all
contiguous
property,
that
receives
universal waste
from other universal
waste
handlers,
accumulates
the
universal
waste, and sends
that universal
waste
to
another universal
waste
handler,
to
a destination facility,
or
to a foreign
destination.
ITuniversal
waste handler”
does not
mean either
of the
following:
A
person
that treats (except
under the provisions
of
Section
733.113(a)
or
(c)
or
733.133(a)
or
(C)),
disposes
of, or recycles
universal waste;
or
A
person
engaged
in
the off-site transportation
of universal
waste by
air, rail,
highway,
or
water, including
a universal
waste transfer
facility.
“Universal
waste
transporter”
means
a
person engaged
in the off-site
transportation
of universal waste
by
air, rail, highway,
or water.
“Unsaturated
zoneTl
or
“zone of
aerationhT
means the
zone
between the land
surface
and
the
water table.
“Uppermost
aquifer”
means the geologic
formation
nearest the natural
ground
surface that
is an
aquifer, as well
as
lower
aquifers
that are hydraulically
interconnected
with this
aquifer within
the facility’s property
boundary.
“USDOT”
or
“Department of Transportation”
means
the
United States
Department
of
Transportation.
“Used
oil”
means any oil that
has
been
refined from
crude oil,
or any synthetic
oil, that
has
been
used and
as a
result
of
such use
is contaminated
by
physical
or chemical
impurities.
‘
T
USEPA’
or
“EPA” means the
United
States
Environmental
Protection
Agency.
“Vessel”
includes
every description
of watercraft
used or capable of
being
used
as
a means
of transportation
on the
water.
“Wastewater
treatment
unitTh
means
a
device
of which
the following
is true:
It is part
of a
wastewater treatment
facility
that
has an NPDES permit
pursuant
to
35 Ill.
Adm. Code
309 or a pretreatment
permit
or
authorization
to
discharge
pursuant to
35 Ill. Adm.
Code 310;
It
receives
and treats or stores
an influent wastewater
that is
a
hazardous
waste as
defined
in
35 Ill. Adm.
Code 721.103,
or
generates and accumulates
a
wastewater
treatment
sludge that is
a hazardous waste
as defined in 35
Ill. Adm.
Code
721.103,
or treats or
stores a wastewater
treatment
sludge that is a
hazardous
waste
as defined in
35 Ill. Adm.
Code 721.103; and
It meets the
definition
of tank or
tank system in
this
Section.
“Water
(bulk
shipment) means the bulk
transportation of hazardous waste that is
loaded or carried on board
a
vessel without
containers or labels.
“Well” means any shaft or pit dug or bored into
the earth, generally of a
cylindrical form, and often walled with bricks or tubing
to
prevent
the earth
from
caving in.
“Well
injection”
(See
“underground injection.”)
“Zone of engineering
control” means an area under the control of the owner
or
operator
that,
upon
detection of a hazardous waste release, can
be
readily
cleaned
up
prior
to
the
release of hazardous waste or hazardous constituents
to
groundwater
or
surface
water.
(Source:
Amended at 33 Ill. Reg.
, effective
Section 720.111
References
The
following
documents
are incorporated
by
reference
for the purposes of this
Part and 35 Ill.
Adm.
Code 702 through 705, 721 through
728, 730, 733, 738, and
739:
a)
Non-Regulatory
Government Publications and Publications of Recognized
Organizations and Associations:
ACI. Available from the American Concrete
Institute, Box 19150, Redford
Station, Detroit, Michigan 48219:
ACI 318-83: “Building
Code
Requirements for
Reinforced Concrete,’
Tadopted
November 1983, referenced in
35
Ill. Adm.
Code 724.673 and 725.543.
ANSI. Available from the American National
Standards Institute, 1430 Broadway,
New York, New York 10018, 212-354-3300:
See
ASME/ANSI B31.3 and B3l.4 and
supplements below in this subsection
(a)
under
ASME.
API. Available from the American
Petroleum Institute, 1220 L Street, N.W.,
Washington, D.C.
20005, 202-682-8000:
“Cathodic Protection of Underground Petroleum
Storage Tanks and Piping
Systems,
API Recommended Practice 1632, Second
Edition, December 1987, referenced in
35
Ill. Adm. Code 724.292, 724.295, 725.292,
and 725.295.
“Evaporative Loss from External Floating-Roof Tanks,”
API publication 2517,
Third Edition, February 1989, USEPA-approved for
35 Ill. Adm. Code 725.984.
“Guide for Inspection of
Refinery Equipment,” Chapter XIII, “Atmospheric
and Low
Pressure Storage Tanks,” 4th Edition,
1981, reaffirmed December 1987, referenced
in 35
Ill. Adm. Code 724.291, 724.293,
725.291, and 725.292.
“Installation of Underground Petroleum Storage
Systems,’
TAPI Recommended
Practice 1615, Fourth Edition, November 1987,
referenced in 35 Ill. Adm.
Code
724 .292.
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
B31.3a-1988
and
B3l.3b-l988,
referenced
in
35 Ill. Adm.
Code
724.292
and
725.292. 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—l987,
referenced
in 35
Ill. Adm.
Code
724.292
and 725.292.
Also available
from
ANSI.
ASTM. Available
from American
Society for
Testing and
Materials,
100
Barr
Harbor Drive,
West
Conshohocken, PA
19428-2959,
610-832-9585:
ASTM
C 94-90,
“Standard
Specification
for Ready-Mixed
Concrete,”
approved
March
30, 1990,
referenced
in
35 Ill. Adm. Code
724.673 and
725.543.
ASTM
D
88-87,
“Standard
Test
Method for Saybolt
Viscosity,” approved
April 24,
1981,
reapproved
January
1987, referenced
in
35
Ill.
Adm.
Code 726.200.
ASTM
D 93-85,
“Standard Test
Methods
for
Flash Point by
Pensky-Martens
Closed
Tester,”
approved
October 25, 1985,
USEPA-approved
for
35
Ill. Adm.
Code
721.121.
ASTM
D 140-70,
“Standard
Practice
for
Sampling
Bituminous Materials,”
approved
1970,
referenced
in Appendix
A
to 35
Ill.
Adm. Code
721.
ASTM D 346-75,
“Standard
Practice for
Collection
and
Preparation of Coke
Samples
for Laboratory
Analysis,”
approved 1975,
referenced
in
Appendix
A
to
35 Ill.
Adm.
Code
721.
ASTM D 420-69,
“Guide to Site Characterization
for
Engineering, Design,
and
Construction
Purposes,”
approved 1969,
referenced
in
Appendix A to 35
Ill. Adm.
Code
721.
ASTM
D 1452-65,
“Standard Practice
for
Soil
Investigation
and Sampling
by
Auger
Borings,”
approved
1965, referenced
in Appendix
A to
35 Iii. Adm. Code
721.
ASTM ID
1946-90, “Standard
Practice for
Analysis of Reformed
Gas by Gas
Chromatography,”
approved
March 30, 1990,
USEPA-approved for
35 Ill. Adm.
Code
724.933
and
725.933.
ASTM ID
2161-87, “Standard
Practice
for Conversion of
Kinematic
Viscosity
to
Saybolt
Universal or to
Saybolt Furol Viscosity,”
March
27,
1987, referenced
in
35
Iii.
Adm. Code
726.200.
ASTM ID
2234-76, “Standard
Practice for
Collection
of
a Gross
Sample of
Coal,”
approved
1976,
referenced
in Appendix A
to 35 Ill. Adm.
Code
721.
ASTM D 2267-88,
“Standard Test Method
for
Aromatics in
Light Naphthas
and
Aviation
Gasolines
by Gas Chromatography,”
approved
November
17, 1988,
USEPA
approved for
35 Ill. Adm.
Code 724.963.
ASTM
ID
2382-88,
“Standard Test
Method for Heat
of
Combustion of
Hydrocarbon
Fuels by
Bomb Calorimeter
(High
Precision
Method),”
approved October
31, 1988,
USEPA-approved
for
35 Ill. Adm. Code
724.933 and 725.933.
ASTM
D
2879-92,
“Standard
Test Method for
Vapor Pressure-Temperature
Relationship
and
Initial
Decomposition
Temperature
of
Liquids
by
Isoteniscope,”
approved
1992,
USEPA-approved for
35 Iii.
Adm. Code
725.984,
referenced in 35
Ill.
Adm.
Code
724.963 and
725.963.
ASTM
U
3828-87,
“Standard
Test Methods
for Flash Point
of Liquids
by Setaf
lash
Closed
Tester,”
approved
December 14, 1988,
USEPA-approved
for 35 Ill. Adm.
Code
721.121(a).
ASTM E 168-88,
“Standard
Practices
for General Techniques
of Infrared
Quantitative
Analysis,” approved
May
27, 1988, USEPA-approved
for
35
Ill.
Adm.
Code
724.963.
ASTM E 169-87,
“Standard
Practices
for General
Techniques
of Ultraviolet-Visible
Quantitative
Analysis,”
approved February
1, 1987,
USEPA-approved
for
35
Ill.
Adm.
Code
724.963.
ASTM E 260-85,
“Standard Practice
for
Packed
Column
Gas Chromatography,”
approved June
28,
1985, USEPA-approved
for 35
Ill.
Adm.
Code 724.963.
ASTM
G
21-70
(1984a),
“Standard
Practice
for
Determining Resistance
of Synthetic
Polymer
Materials
to Fungi,”
referenced in
35
Ill. Adm. Code 724.414
and
725.414.
ASTM
G
22-76
(1984b),
“Standard Practice
for
Determining
Resistance of Plastics
to
Bacteria,”
referenced
in
35
Ill.
Adm. Code 724.414
and 725.414.
GPO.
Available
from the Superintendent
of
Documents,
U.S. Government
Printing
Office, Washington,
D.C. 20402, 202-512-1800:
Standard
Industrial
Classification
Manual
(1972),
and
1977 Supplement,
republished
in 1983, referenced
in
35
Ill. Adm.
Code
702.110 and
Section
720.110.
“Test
Methods for Evaluating
Solid Waste,
Physical/Chemical
Methods,” USEPA
publication
number
EPA-530/SW-846
(Third
Edition,
November
1986),
as amended
by
Updates
I
(July
1992),
II
(November
1994),
hA
(August,
1993), IIB (January
1995)
, III
(December
1996)
, lilA
(April
1998)
, and
IIIB
(November
2004)
(document number
955-001-00000-1)
.
See below in this
subsection
(a)
under
NTIS.
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,
referenced
in
35 Ill. Adm. Code
724.292,
724.295, 725.292,
and
725.295.
NFPA.
Available
from the
National
Fire Protection
Association,
1 Batterymarch
Park,
Boston,
MA 02269, 617-770-3000
or
800-344-3555:
“Flammable
and Combustible
Liquids
Code,” NFPA
30,
issued
July 18, 2003,
as
supplemented
by TIA 03-1,
issued
July 15, 2004, and
corrected
by
Errata
30-03-
01,
issued
August 13, 2004,
USEPA-approved
for 35 Ill.
Adm.
Code 724.298,
725.298,
and
727.290, referenced
in
35
Ill. Adm.
Code
725.301 and
726.211.
NTIS.
Available
from
the U.S. Department
of Commerce,
National
Technical
Information
Service, 5285 Port
Royal Road,
Springfield,
VA 22161,
703-605-6000
or
800-553-6847
(Internet
address:
www.ntis.gov):
“APTI Course 415:
Control of
Gaseous Emissions,” December 1981,
USEPA
publication number EPA-450/2-81-005,
NTIS document number PB8O-208895,
USEPA
approved for
35
Ill. Adm.
Code 703.210, 703.211, 703.352, 724.935,
and 725.935.
BOARD NOTE:
“APTI” denotes
USEPA’s “Air Pollution Training Institute”
(Internet
address:
www. epa.
gov/air/oaqps/eog/)
“Generic
Quality
Assurance Project
Plan for Land Disposal Restrictions
Program,”
USEPA publication number EPA-530/SW-87-0l1,
March 15, 1987, NTIS
document number
PB88-170766, referenced
in 35 Iii. Adm. Code 728.106.
“Method
1664,
Revision A,
n-Hexane Extractable Material
(HEM; Oil and
Grease)
and
Silica Gel Treated n-Hexane Extractable Material
(SGT-HEM; Non-polar
Material)
by
Extraction
and Gravimetry,” USEPA
publication number EPA-821/R-98-
002, NTIS document number PB99-12l949, USEPA-approved
for Appendix I to 35 Iii.
Adm.
Code 721.
BOARD
NOTE:
EPA-821/R--98-002
is also available on
the Internet for free
download as a PDF document from the USEPA website
at:
www.
epa.
gov/waterscience/methods/1664
0514
. pdf.
“Methods
for
Chemical
Analysis of Water and Wastes,” Third
Edition, March 1983,
USEPA
document
number EPA-600/4-79-020,
NTIS document number PB84-128677,
referenced in
35
Ill. Adm.
Code 725.192.
BOARD NOTE: EPA-600/4-79-020 is
also available on the Internet
as a
viewable/printable HTML document from
the USEPA website at:
www.epa.gov/clariton/clhtml/pubtitleORD.html
as document 600479002.
“Procedures Manual for Ground Water Monitoring
at Solid Waste Disposal
Facilities,” August 1977, EPA-530/SW-6l1,
NTIS document number PB84-l74820,
referenced in
35
Iii. Adm.
Code
725.192.
“Screening Procedures for Estimating
the Air Quality Impact of Stationary
Sources,” October 1992, USEPA publication
number EPA-454/R-92-019, NTIS
document
number 93-219095, referenced in
35
Iii.
Adm. Code 726.204 and 726.206.
BOARD NOTE: EPA-454/R-92-0l9 is also available
on the Internet for free
download
as a
WordPerfect document from
the USEPA website
at
the following
Internet address: www.epa.gov/scramool/guidance/guide/scrng.wpd.
“Test
Methods for Evaluating Solid Waste,
Physical/Chemical Methods,” USEPA
publication number EPA-530/SW-846
(Third
Edition, November 1986; Revision
6,
January
2005),
as amended by Updates I
(July
1992),
II
(November 1994),
hA
(August
1993),
IIB (January
1995),
III (December
1996),
lilA (April
1998),
and
IIIB
(November 2004) (document
number
955-001-00000-1),
generally referenced
in
Appendices A and I to 35 111. Adm.
Code
721 and
35 Iii. Adm. Code 726.200,
726.206, 726.212, and 728.106
(in
addition
to the references cited below for
specific
methods)
Method 0010
(November
1986) (Modified
Method
5
Sampling
Train),
USEPA-approved
for
Appendix I
to 35
Ill. Adm.
Code 721.
Method 0011
(December 1996)
(Sampling
for Selected Aldehyde and
Ketone Emissions
from Stationary
Sources),
USEPA-approved
for Appendix I
to 35
Ill.
Adm. Code 721
and
for Appendix I
to 35
Ill. Adm.
Code 726.
Method 0020
(November 1986) (Source
Assessment
Sampling System), USEPA-approved
for Appendix I to 35 Ill. Adm.
Code
721.
Method
0023A
(December 1996)
(Sampling Method
for
Polychlorinated
Dibenzo-p
Dioxins
and
Polychlorinated
Dibenzofuran Emissions
from Stationary
Sources),
USEPA-approved
for
Appendix
I to
35 Ill. Adm.
Code
721, Appendix I
to 35
Ill.
Adm.
Code
726, and
35 Ill. Adm. Code
726.204.
Method
0030
(November
1986)
(Volatile
Organic
Sampling
Train),
USEPA-approved
for Appendix
I to 35
Ill. Adm.
Code 721.
Method
0031
(December 1996)
(Sampling
Method for Volatile
Organic Compounds
(SMVOC)),
USEPA-approved
for
Appendix
I
to 35 111. Adm.
Code 721.
Method 0040
(December
1996)
(Sampling
of
Principal
Organic
Hazardous
Constituents
from Combustion
Sources Using
Tedlar(r)
Bags),
USEPA-approved
for
Appendix
I to
35 111. Adm.
Code 721.
Method
0050
(December
1996) (Isokinetic
HC1/Cl2
Emission
Sampling
Train),
USEPA
approved for
Appendix
I
to
35 Ill.
Adm.
Code 721,
Appendix
I
to
35 Ill. Adm.
Code 726,
and 35 Ill.
Adm. Code 726.207.
Method
0051
(December
1996)
(Midget
Impinger
HC1/C12
Emission
Sampling
Train),
USEPA-approved
for Appendix I
to 35 Ill. Adm.
Code
721, Appendix
I to 35 Ill.
Adm. Code 726,
and
35 Ill. Adm.
Code 726.207.
Method
0060
(December 1996)
(Determination
of Metals
in
Stack
Emissions),
USEPA
approved
for
Appendix I
to 35 Ill. Adm.
Code 721, Appendix
I to 35 111. Adm.
Code
726,
and 35
Ill. Adm.
Code 726.206.
Method 0061
(December 1996)
(Determination
of Hexavalent
Chromium
Emissions
from
Stationary
Sources),
USEPA-approved
for Appendix I
to
35
Ill.
Adm. Code
721,
35
Ill.
Adm.
Code
726.206, and
Appendix
I
to 35 111. Adm. Code
726.
Method 1O1OA
(November
2004) (Test
Methods
for
Flash
Point
by Pensky-Martens
Closed Cup
Tester),
USEPA-approved
for Appendix I
to 35
Ill. Adm.
Code
721.
Method
lO2OB
(November
2004) (Standard
Test
Methods
for Flash Point
by Setaf
lash
(Small
Scale)
Closed—cup
Apparatus),
USEPA-approved
for Appendix I
to 35
Ill.
Adm.
Code
721.
Method
lllOA
(November 2004)
(Corrosivity
Toward
Steel),
USEPA-approved
for
35
Ill. Adm. Code
721.122 and Appendix
I
to
35 Ill. Adm.
Code 721.
Method
1310B
(November
2004) (Extraction
Procedure
(EP)
Toxicity Test
Method
and
Structural
Integrity
Test),
USEPA-approved
for Appendix
I to 35 Ill. Adm.
Code
721 and
referenced in Appendix
I to
35
Ill.
Adm.
Code
728.
Method 1311
(November 1992)
(Toxicity
Characteristic
Leaching
Procedure),
USEPA
approved
for
Appendix
I to 35 Ill.
Adm.
Code
721; for
35 Ill. Adm. Code
721.124,
728.107,
and
728.140; and for
Table T
to 35
Ill. Adm. Code
728.
Method 1312
(November
1994)
(Synthetic Precipitation
Leaching
Procedure),
USEPA
approved
for
Appendix
I to 35 Ill.
Adm. Code 721.
Method
1320
(November
1986)
(Multiple
Extraction
Procedure),
USEPA-approved
for
Appendix I to 35
Ill. Adm. Code
721.
Method
1330A
(November
1992)
(Extraction
Procedure for Oily
Wastes),
USEPA
approved
for
Appendix
I
to
35 Ill. Adm.
Code
721.
Method
9OlOC
(November
2004)
(Total
and Amenable Cyanide:
Distillation),
USEPA
approved
for Appendix I to 35 Iii. Adm. Code 721 and 35 Ill. Adm. Code
728.140,
728.144, and 728.148,
referenced
in Table H to 35 Ill. Adm. Code
728.
Method 9012B
(November
2004) (Total
and
Amenable Cyanide
(Automated
Colorimetric, with
Off-Line
Distillation)),
USEPA-approved for Appendix I to 35
Ill. Adm. Code 721
and
35
Ill. Adm.
Code
728.140, 728.144, and 728.148,
referenced in Table
H
to 35
Ill.
Adm. Code
728.
Method 9040C
(November
2004)
(pH Electrometric
Measurement),
USEPA-approved for
35 Ill. Adm. Code
721.122 and Appendix I
to 35
Iii. Adm.
Code
721.
Method 9045D
(November
2004) (Soil
and Waste pH), USEPA-approved for Appendix I
to 35
111. Adm. Code
721.
Method 9060A
(November
2004)
(Total Organic
Carbon),
USEPA-approved for Appendix
I
to 35
Ill. Adm. Code
721 and
35
Ill. Adm.
Code
724.934, 724.963, 725.934, and
725.
963.
Method 9070A
(November
2004)
(n-Hexane Extractable Material
(HEM)
for Aqueous
Samples),
USEPA-approved for Appendix I
to 35
111. Adm.
Code
721.
Method 9071B
(April
1998) (n-Hexane
Extractable Material
(HEM)
for Sludge,
Sediment, and
Solid Samples), USEPA-approved for Appendix I to 35 111. Adm. Code
721.
Method
9095B
(November 2004) (Paint
Filter Liquids
Test),
USEPA-approved for
Appendix
I
to
35 111. Adm. Code 721 and 35 Ill. Adm. Code
724.290, 724.414,
725.290,
725.414, 725.981, 727.290, and 728.132.
BOARD
NOTE: EPA-530/SW-846 is also available on the
Internet for free download
in
segments in PDF format from the USEPA website at:
www.epa.gov/SW-846.
OECD.
Organisation for Economic Co-operation and Development,
Environment
Directorate,
2 rue Andre Pascal, 75775 Paris Cedex 16, France
(www.oecd.org),
also OECD
Washington Center, 2001 L Street, NW, Suite 650,
Washington, DC
20036-
4922,
202-785-6323 or 800-456-6323 (www.oecdwash.org):
OECD
TTAmber
List of Wastes,
TT Appendix 4 to the OECD Council
Decision
C(92)39/Final
(March
30, 1992, revised May
1993)
(Concerning the
Control of
Transfrontier Movements of Wastes Destined for
Recovery Operations), USEPA
approved for 35 Ill. Adm. Code 722.189,
referenced in
35
Ill. Adm. Code 722.181.
OECD Amber Tier, Section IV
of
the
annex
to
the OECD Council Decision
C(92)39/Final
(Concerning the Control of Transfrontier Movements of Wastes
Destined for
Recovery Operations)
(revised
May
1993),
referenced in 35 Ill. Adm.
Code
722.181.
Annex to
OECD Council Decision C(88)90/Final, as amended by C(94)152/Final
(revised July
1994),
referenced in 35 Ill. Adm. Code
722.187.
OECD
‘Green List of
Wastes,
TT Appendix
3 to
the OECD Council Decision
C(92)39/Final
(March
30, 1992, revised
May 1994) (Concerning the Control of
Transfrontier
Movements
of
Wastes Destined for Recovery Operations), USEPA
approved for 35
Ill. Adm.
Code
722.189, referenced in
35
Ill. Adm. Code 722.181.
OECD “Green Tier,”
Section III of the annex to the
OECD Council Decision
C(92)39/Final
(Concerning the Control of
Transfrontier Movements of Wastes
Destined for
Recovery Operations)
(revised
May
1993),
referenced in 35 Ill. Adm.
Code
722.181.
OECD Guideline
for Testing of Chemicals, “Ready
Biodegradability,” Method 301B
(July 17,
1992),
“C02 Evolution
(Modified
Sturm
Test),
“ referenced in 35 Ill.
Adm. Code
724.414.
OECD “Red List of
Wastes,” Appendix 5 to the OECD Council
Decision C(92)39/Final
(March
30, 1992,
revised May
1993),
USEPA-approved for 35 Iii.
Adm.
Code
722.189, referenced
in
35
Ill. Adm.
Code
722.181.
OECD “Red Tier,”
Section V of the annex
to
the OECD Council
Decision
C(92)39/Final
(Concerning the Control of Transfrontier Movements
of Wastes
Destined for Recovery
Operations)
(revised
May
1993),
referenced
in
35
Ill. Adm.
Code
722.181.
Table
2.B of the
Annex of OECD Council Decision
C(88)90(Final) (May 27,
1988),
amended
by
C(94)152/Final (July 28,
1994),
“Decision of the
Council on
Transfrontier
Movements of Hazardous Wastes,” referenced in 35
Ill. Adm.
Code
722.181 and 722.187.
STI. Available
from the Steel Tank Institute, 728 Anthony
Trail, Northbrook, IL
60062,
708-498-1980:
“Standard
for Dual Wall Underground
Steel Storage Tanks”
(1986),
referenced in
35 Ill.
Adm. Code 724.293.
USDOD. Available from the United States
Department of Defense:
“DOD
Ammunition and Explosives Safety
Standards” (DOD
6055.09-STD),
as in effect
on February
29, 2008, referenced in 35 Ill. Adm. Code
726.305.
“The Motor
Vehicle Inspection Report”
(DD
Form
626),
as
in effect in March 2007,
referenced in 35
Ill. Adm. Code 726.303.
“Requisition
Tracking Form”
(DO
Form
1348)
, as
in effect in July
19911991.
referenced
in 35 Ill. Adm. Code
726.303.
“The
Signature and Tally Record”
(DD Form
1907),
as
in effect in November 2006,
referenced in 35 Ill. Adm. Code
726.303.
“Dangerous Goods Shipping
Paper/Declaration and Emergency Response
Information
for Hazardous Materials
Transported
by
Government Vehicles”
(DD
Form
836),
as in
effect in December
2007, referenced in 35 Ill. Adm. Code 726.303.
BOARD NOTE:
DOD 6055.09-STD is available on-line for
download in
pdf
format
from
http://www.ddesb.pentagon.mil. DD Form 1348, DO
Form 1907, DID Form 836,
and DOD
6055.09-STD are available on-line for download
in
pdf
format from
http://www.dtic.mil/whs/directives/
infomgt/forms/formsprogram.htm.
USEPA,
Office of Ground Water and Drinking Water.
Available from United States
Environmental
Protection Agency, Office of Drinking
Water,
State
Programs
Division, WH 550 E, Washington,
D.C.
20460:
“Inventory of
Injection
Wells,” USEPA Form
7520-16 (Revised
8-01),
referenced in
35 Iii. Adm.
Code
704.148 and 704.283.
‘Technical
Assistance
Document: Corrosion, Its Detection and
Control in
Injection
Wells,”
USEPA publication number EPA-570/9-87-002, August
1987,
referenced in 35
Ill. Adm. Code
730.165.
USEPA,
Receptor Analysis
Branch. Available from Receptor Analysis
Branch, USEPA
(MD-14),
Research Triangle
Park, NC 27711:
“Screening Procedures for
Estimating the Air Quality Impact of
Stationary
Sources,
Revised,
TT
October
1992, USEPA publication number
EPA-450/R-92-019,
USEPA-approved for
Appendix I
to
35 Ill. Adm. Code 726.
BOARD NOTE:
EPA-454/R-92-019 is also available for purchase
from NTIS
(see
above)
and on the
Internet for free download as a
WordPerfect document from the
USEPA website at
following Internet address:
www. epa.
gov/scramool/guidance/guide/scrng . wpd.
USEPA Region 6.
Available from United States
Environmental Protection Agency,
Region 6,
Multimedia Permitting and Planning
Division, 1445 Ross Avenue, Dallas,
TX 75202 (phone:
214-665-7430)
“EPA RCRA
Delisting Program - Guidance Manual for the
Petitioner,” March 23,
2000,
referenced
in Section 720.122.
USGSA. Available
from the United States Government
Services Administration:
Government Bill of
Lading
(GBL) (GSA
Standard Form 1103,
rev 9/2003,
supplemented as
necessary with GSA Standard Form 1109,
rev 09/1998), referenced
in
Section 726.303.
BOARD NOTE:
Available on-line for download in
various formats from
www. gsa.
gov/forms/forms . htm.
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 20.2006
(2007) (2008) (Transfer
for Disposal and
Manifests), referenced
in 35
Ill. Adm. Code
702.110, 726.425, and 726.450.
Table II,
column 2 in Appendix B to 10 CFR 20
(2007)
(2008)
(Water
Effluent
Concentrations),
referenced in 35 Ill. Adm. Code 702.110,
730.103, and 730.151.
Appendix
G to 10
CFR 20
(2007) (2008),
as amended at 73 Fed.
Reg. 30456 (May 28,
2008)
(Requirements
for Transfers of Low-Level
Radioactive Waste Intended for
Disposal at
Licensed Land Disposal Facilities and
Manifests),
referenced in
35
Ill. Adm. Code
726.440.
10
CFR 71
(2007) (2008),
as
amended
at 73
Fed. Reg. 30456 (May 28,
2008)
(Packaging and Transportation
of Radioactive
Material),
referenced generally in
35
Ill. Adm. Code
726.430.
10
CFR 71.5
(2007)
(2008)
(Transportation of Licensed
Material),
referenced in
35
Ill. Adm. Code
726.425.
33
CFR 153.203
(2007)
(2008) (Procedure
for the
Notice of Discharge),
referenced in 35
Ill.
Adm.
Code
723.130
and
739.143.
40 CFR 3.2 (2007)
(How
Does This Part
Provide
for Electronic Reporting?),
referenced in
Section
720.104.
40 CFR 3.3
(2007) (What
Definitions Are Applicable to This
Part?),
referenced in
Section
720.104.
40
CFR
3.10
(2007)
(What
Are the Requirements for Electronic Reporting to
EPA?),
referenced
in Section
720.104.
40
CFR 3.2000
(2007)
(What
Are the Requirements Authorized State,
Tribe, and
Local
Programs’
Reporting Systems Must
Meet?),
referenced in Section
720.104.
40 CFR
51.100(u) (2007)
(Definitions),
referenced in 35 Ill. Adm. Code 726.200.
Appendix W to
40 CFR 51 (2007) (Guideline
on Air Quality
Models),
referenced in
35 Ill.
Adm. Code 726.204.
BOARD NOTE:
Also available from
NTIS
(see
above for contact
information)
as
“Guideline
on Air Quality Models,”
Revised 1986, USEPA publication number EPA
450/12-78-027R,
NTIS document
numbers PB86-245248
(Guideline)
and PB88-150958
(Supplement)
Appendix
B
to
40 CFR 52.741
(2007)
(VOM
Measurement Techniques for
Capture
Efficiency),
referenced in 35
Ill. Adm.
Code
703.213, 703.352, 724.982,
724.984,
724.986,
724.989, 725.983, 725.985,
725.987, and 725.990.
40
CFR
60
(2007),
as
amended
at
72 Fed. Reg. 51365 (September 7,
2007),
72
Fed.
Reg.
51494
(September 7,
2007),
72 Fed. Reg. 55278 (September 28,
2007),
72
Fed.
Reg.
59190
(October 19,
2007),
72 Fed. Reg. 62414
(November
5,
2007),
72 Fed.
Reg.
64860
(November 16,
2007),
73 Fed. Reg. 3568
(January 18,
2008),
73 Fed.
Reg.
18162 (April 3,
2008), 73 Fed. Reg. 24870 (May 6,
2008),
73
Fed. Reg. 29691
(May
22,
2008),
73
Fed. Reg.
30308
(May 27,
2008),
73 Fed. Reg.
31368
(June
2,
2008),
73 Fed. Reg.
31372
(June
2,
2008),
and 73 Fed. Reg. 35838
(June
24,
2008)
(Standards of
Performance for New Stationary
Sources),
referenced
generally in
35
Iii. Adm. Code
724.964, 724.980, 725.964, and 725.980.
Subpart VV of 40
CFR
60
(2007),
as amended at 72 Fed.
Reg. 64860
(November
16,
2007)
(Standards of Performance for Equipment
Leaks of VOC in the Synthetic
Organic
Chemicals Manufacturing Industry),
referenced in
35
Iii. Adm. Code
724.989 and
725.990.
Appendix A to
40 CFR 60
(2007),
as amended at
72 Fed. Reg. 51365 (September 7,
2007),
72
Fed. Reg. 51494 (September 7,
2007),
72 Fed. Reg. 55278 (September 28,
2007),
73
Fed. Reg. 29691 (May 22,
2008)
(Test
Methods),
referenced generally
in 35
Ill. Adm. Code 726.205
(in
addition
to
the references cited below for
specific
methods)
Method 1 (Sample
and Velocity Traverses for Stationary
Sources),
referenced
in
35
Iii. Adm. Code
726.205.
Method 2
(Determination of Stack
Gas
Velocity and Volumetric Flow
Rate (Type
S
Pitot
Tube)),
referenced in 35 Ill. Adm. Code 724.933,
724.934, 725.933,
725.934, and
726.205.
Method 2A
(Direct
Measurement of Gas Volume
through Pipes
and
Small
Ducts),
referenced in 35
Iii. Adm. Code 724.933, 725.933, and 726.205.
Method 2B (Determination
of Exhaust
Gas
Volume Flow Rate from Gasoline
Vapor
Incinerators),
referenced in
35
Ill. Adm. Code 726.205.
Method 2C (Determination
of
Gas
Velocity and Volumetric Flow Rate in
Small
Stacks or Ducts
(Standard Pitot
Tube)),
referenced in 35 Ill. Adm. Code
724.933,
725.933, and 726.205.
Method
2D (Measurement
of
Gas
Volume Flow Rates in Small Pipes and
Ducts),
referenced in 35
Ill. Adm.
Code
724.933, 725.933, and 726.205.
Method
2E (Determination
of Landfill
Gas
Production Flow
Rate),
referenced in
35
Ill. Adm. Code
726.205.
Method 2F
(Determination of Stack
Gas
Velocity and Volumetric
Flow Rate with
Three-Dimensional
Probes),
referenced in 35 Iii. Adm. Code 726.205.
Method 2G
(Determination of Stack Gas Velocity and Volumetric
Flow Rate with
Two-Dimensional
Probes),
referenced in 35 Ill. Adm. Code
726.205.
Method 2H
(Determination of Stack Gas Velocity Taking
into Account Velocity
Decay Near
the Stack
Wall),
referenced in 35 Ill.
Adm.
Code
726.205.
Method 3
(Gas
Analysis for the Determination of Dry
Molecular Weight),
referenced in 35
Iii. Adm. Code 724.443 and 726.205.
Method 3A
(Determination of Oxygen and Carbon Dioxide
Concentrations in
Emissions from
Stationary Sources
(Instrumental
Analyzer
Procedure)),
referenced
in
35
Ill.
Adm.
Code
726.205.
Method 3B
(Gas
Analysis for the Determination of Emission
Rate Correction Factor
or
Excess
Air), referenced in 35 Ill. Adm. Code 726.205.
Method 3C
(Determination
of Carbon Dioxide, Methane,
Nitrogen, and Oxygen from
Stationary
Sources),
referenced in 35
Iii.
Adm. Code
726.205.
Method
4
(Determination
of
Moisture Content in Stack
Gases),
referenced in 35
Ill.
Adm. Code 726.205.
Method 5
(Determination
of
Particulate Matter Emissions from Stationary
Sources),
referenced in 35 Ill.
Adm.
Code
726.205.
Method 5A
(Determination of Particulate Matter Emissions from the
Asphalt
Processing and
Asphalt Roofing Industry), referenced in 35 Iii. Adm. Code
726.205.
Method 5B
(Determination of Nonsulfuric Acid Particulate Matter
Emissions
from
Stationary
Sources),
referenced in 35 Ill. Adm. Code 726.205.
Method SD
(Determination
of Particulate Matter
Emissions from Positive Pressure
Fabric
Filters),
referenced in 35 Ill.
Adm.
Code
726.205.
Method 5E
(Determination of Particulate Matter Emissions from the Wool
Fiberglass
Insulation Manufacturing Industry), referenced in 35 Ill.
Adm.
Code
726.205.
Method
SF
(Determination
of Nonsulfate Particulate
Matter Emissions
from
Stationary
Sources),
referenced in
35
Ill. Adm.
Code
726.205.
Method
5G
(Determination
of Particulate
Matter Emissions
from Wood
Heaters
(Dilution
Tunnel
Sampling Location)),
referenced
in 35 Ill. Adm.
Code 726.205.
Method
5H
(Determination
of
Particulate
Emissions from Wood
Heaters
from
a Stack
Location),
referenced
in
35 Ill. Adm.
Code 726.205.
Method 51
(Determination
of
Low Level Particulate
Matter
Emissions
from
Stationary
Sources),
referenced
in 35 Ill.
Adm. Code 726.205.
Method
18
(Measurement
of Gaseous
Organic
Compound
Emissions
by
Gas
Chromatography),
referenced
in 35
Ill. Adm. Code
724.933,
724.934,
725.933,
and
725.934.
Method
21
(Determination
of
Volatile Organic
Compound
Leaks),
referenced
in
35
Ill. Adm. Code
703.213,
724.934, 724.935,
724.963, 725.934,
725.935,
725.963,
and 725.984.
Method
22
(Visual
Determination
of Fugitive
Emissions from
Material
Sources and
Smoke
Emissions from
Flares),
referenced
in 35 Ill. Adm.
Code
724.933,
724.1101,
725.933,
725.1101,
and
727.900.
Method 25A
(Determination
of
Total Gaseous Organic
Concentration
Using
a Flame
Ionization
Analyzer),
referenced
in 35 Ill.
Adm. Code
724.934 and 725.985.
Method
25D
(Determination
of the Volatile
Organic
Concentration
of Waste
Samples),
referenced in
35 Iii.
Adm. Code 724.982,
725.983,
and 725.984.
Method 25E
(Determination
of
Vapor Phase Organic
Concentration
in Waste
Samples),
referenced
in 35
111. Adm. Code
725.984.
Method 27
(Determination
of
Vapor
Tightness of
Gasoline Delivery
Tank
Using
Pressure-Vacuum
Test),
referenced
in 35
Ill. Adm.
Code
724.987
and 725.987.
40 CFR
61
(2007),
as amended
at 73
Fed. Reg. 18162
(April 3,
2008)
and 73
Fed.
Reg.
24870
(May 6,
2008)
(National
Emission Standards
for Hazardous
Air
Pollutants),
referenced generally
in 35
Ill.
Adm. Code 725.933,
725.964,
and
725.980.
Subpart
V of 40
CFR 61
(2007)
(National
Emission
Standard for Equipment
Leaks
(Fugitive Emission
Sources)),
referenced in
35
Ill. Adm. Code 724.989
and
725 . 990.
Subpart
FF of 40
CFP.
61 (2007)
(National
Emission Standard
for Benzene
Waste
Operations),
referenced in
35 Ill.
Adm. Code 724.982
and 725.983.
40
CFR 63
(2007),
amended in
72 Fed. Reg.
36363 (July 3,
2007),
72
Fed. Reg.
38864
(July 16,
2007),
72 Fed.
Reg. 61060
(October
29, 2007),
72 Fed.
Reg.
73180
(December 26,
2007)
, 72 Fed.
Reg. 73611
(December
28,
2007)
, 72
Fed.
Reg.
74088
(December 28,
2007),
73 Fed.
Reg.
226 (January 2,
2008),
73
Fed. Reg.
1738
(January 9,
2008),
73
Fed.
Reg.
1916 (January
10,
2008),
73 Fed. Reg.
3568
(January
18,
2008),
73 Fed.
Reg. 7210
(February
7,
2008),
73 Fed. Reg.
12276
(March
7,
2008)
, 73 Fed. Reg. 17252
(April 1, 2008)
, 73
Fed. Reg.
18169
(April
3, 2008),
73
Fed. Reg. 18970
(April
8,
2008),
73 Fed. Reg. 21825
(April
23,
2008),
and
73
Fed. Reg.
24870 (May
6,
2008)
(National
Emission Standards
for
Hazardous Air Pollutants
for Source
Categories), referenced generally in 35 Iii.
Adm. Code 725.933,
725.964, and 725.980.
Subpart RR of 40 CFR 63
(2007) (National
Emission Standards for
Individual Drain
Systems), referenced
in 35 Ill. Adm.
Code 724.982, 724.984, 724.985, 725.983,
725.985, and 725.986.
Subpart EEE of 40 CFR 63
(2000) (National
Emission Standards for
Hazardous
Air
Pollutants from Hazardous
Waste
Combustors),
referenced in 35 Ill.
Adm.
Code
703.280.
Subpart
EEE of 40 CFR 63
(2007),
as amended at 73 Fed. Reg. 18970 (Apr.Aoril 8,
2008)
(National
Emission Standards for Hazardous Air Pollutants from Hazardous
Waste
Combustors) (includes
40 CFR 63.1206
(When
and How Must You
Comply
with
the
Standards and Operating Requirements?), 63.1215
(What
are the
Health-Based
Compliance
Alternatives for Total
Chlorine?),
63.1216
(What
are the Standards
for
Solid-Fuel Boilers that Burn Hazardous
Waste?),
63.1217
(What
are the
Standards
for Liquid-Fuel Boilers that Burn Hazardous
Waste?),
63.1218
(What
are
the
Standards for Hydrochloric Acid Production Furnaces that Burn Hazardous
Waste?), 63.1219
(What
are the Replacement Standards for Hazardous Waste
Incinerators?),
63.1220
(What
are the Replacement Standards for Hazardous Waste-
Burning
Cement
Kilns?),
and 63.1221
(What
are the Replacement Standards for
Hazardous Waste-Burning Lightweight Aggregate
Kilns?)),
referenced
in Appendix
A
to 35
Ill. Adm. Code 703 and 35 Ill. Adm. Code 703.155, 703.205,
703.208,
703.221, 703.232, 703.320, 703.280, 724.440, 724.701, 724.950,
725.440,
and
726.200.
Method 301
(Field
Validation of Pollutant Measurement
Methods from Various
Waste
Media)
in appendix A to 40 CFR 63
(2007) (Test Methods),
referenced in
35 Ill.
Adm.
Code
725.984.
Appendix
C
to 40 CFR 63
(2007) (Determination
of the
Fraction Biodegraded
(Fbio)
in a
Biological Treatment
Unit),
referenced in 35 111.
Adm.
Code
725.984.
Appendix D to 40
CFR
63
(2007)
(Test Methods),
referenced in
35
Ill. Adm.
Code
725.984.
40 CFR 136.3
(Identification
of Test
Procedures) (2007),
referenced in 35 Ill.
Adm. Code
702.110, 704.150, 704.187, and 730.103.
40 CFR 144.70
(2007)
(Wording of the
Instruments),
referenced in 35 111. Adm.
Code
704.240.
40 CFR
232.2
(2007) (Definitions),
referenced in 35 Ill. Adm. Code 721.104.
40 CFR 257
(2007) (Criteria
for Classification of Solid Waste Disposal
Facilities and
Practices),
referenced in 35 111. Adm. Code 739.181.
40
CFR
258
(2007) (Criteria
for Municipal Solid Waste
Landfills),
referenced in
35
Ill. Adm. Code 739.181.
40
CFR 260.21 (2007)
(Alternative
Equivalent Testing Methods), referenced
in
Section
720.121.
Appendix I
to
40 CFR 260
(2007) (Overview
of Subtitle
C
Regulations), referenced
in
Appendix A to 35 Ill. Adm. Code 720.
S
S
Appendix
III to
40 CFR 261
(2007) (Chemical
Analysis Test
Methods),
referenced
in 35
Ill. Adm. Code 704.150 and 704.187.
40
CFR 262.53
(2007) (Notification
of Intent to Export), referenced in 35 Ill.
Adm. Code
722.153.
40 CFR 262.54
(2007)
(Special Manifest Requirements), referenced in 35 Ill. Adm.
Code
722.154.
40 CFR 262.55
(2007)
(Exception Reports), referenced in 35 Ill. Adm. Code
722
. 155.
40 CFR 262.56
(2007) (Annual
Reports), referenced in 35 Ill. Adm. Code
722.156.
40 CFR 262.57
(2007)
(Recordkeeping),
referenced in 35 Ill. Adm. Code
722.157.
Appendix to 40 CFR
262
(2007) (Uniform
Hazardous Waste Manifest and
Instructions
(EPA
Forms 8700-22
and 8700-22A
and Their
Instructions)),
referenced in Appendix
A
to
35 Ill. Adm. Code
722 and
35 Ill. Adm. Code
724.986
and
725.987.
40 CFR 264.151 (2007)
(Wording
of the
Instruments),
referenced
in
35
Ill. Adm.
Code
724.251 and
727.240.
Appendix I to 40
CFR 264
(2007)
(Recordkeeping Instructions), referenced in
Appendix A to 35
Ill. Adm.
Code 724.
Appendix
IV
to
40 CFR 264
(2007) (Cochran’s
Approximation
to
the Behrens-Fisher
Students’
T-Test),
referenced in Appendix D
to 35
Ill. Adm. Code 724.
Appendix V to
40 CFR 264
(2007)
(Examples of Potentially Incompatible
Waste),
referenced
in Appendix E
to 35
Ill. Adm.
Code
724 and
35
Ill. Adm. Code 727.270.
Appendix VI
to
40 CFR 264
(2007) (Political
Jurisdictions in Which Compliance
with
§
264.18(a)
Must Be
Demonstrated),
referenced in 35 Ill. Adm. Code 703.306
and
724.118.
Appendix I to 40 CFR 265
(2007)
(Recordkeeping
Instructions),
referenced in
Appendix A to 35 Ill. Adm. Code 725.
Appendix III to 40 CFR 265
(2007) (EPA
Interim Primary Drinking Water
Standards),
referenced in Appendix C to 35 Ill. Adm. Code 725.
Appendix IV to 40
CFR
265
(2007)
(Tests
for
Significance),
referenced
in
Appendix D to 35
Ill. Adm.
Code 725.
Appendix
V
to
40 CFR 265 (2007) (Examples of Potentially Incompatible Waste),
referenced
in
35
Ill. Adm.
Code
725.277, 725.330, 725.357, 725.382, and 725.413
and
Appendix E
to
35 Ill. Adm.
Code
725.
Appendix IX
to
40 CFR 266
(2007) (Methods
Manual for Compliance with the BIF
Regulations), referenced generally in Appendix I to
35
Ill. Adm. Code 726.
Section 4.0
(Procedures
for
Estimating the Toxicity Equivalence of Chlorinated
Dibenzo-p-Dioxin
and Dibenzofuran
Congeners), referenced in 35 Ill. Adm. Code
726.200 and
726.204.
‘.
t
Section
5.0
(Hazardous
Waste Combustion Air Quality Screening
Procedure),
referenced in 35 Ill.
Adm.
Code
726.204.
Section 7.0
(Statistical
Methodology
for
Bevill
Residue
Determinations),
referenced in 35 Iii.
Adm.
Code
726.212.
BOARD NOTE: Also
available from NTIS
(see
above for contact
information)
as
TTMethods
Manual for Compliance with BIF Regulations: Burning Hazardous Waste in
Boilers and
Industrial Furnaces,” December 1990, USEPA publication number EPA
530/SW-91-0l0,
NTIS document number PB91-120006.
40 CFR 270.5
(2007)
(Noncompliance and Program Reporting by the
Director),
referenced in 35
Ill. Adm. Code 703.305.
40 CFR 761 (2007),
amended in 72 Fed. Reg. 53152 (September 18,
2007)
and 72
Fed. Reg. 57235
(October
9,
2007)
(Polychlorinated Biphenyls
(PCBs)
Manufacturing,
Processing, Distribution in Commerce, and
Use
Prohibitions),
referenced
generally in
35
Ill. Adm.
Code
728.145.
40 CFR 761.3
(2007)
(Definitions),
referenced in 35 Ill. Adm. Code 728.102 and
739.110.
40 CFR 761.60
(2007),
amended in 72 Fed. Reg. 57235
(October
9,
2007)
(Disposal
Requirements),
referenced in 35 Ill. Adm. Code 728.142.
40 CFR
761.65
(2007),
amended in 72 Fed. Reg. 57235
(October
9,
2007)
(Storage
for
Disposal), referenced in 35 Ill. Adm. Code 728.150.
40 CFR
761.70,761.70 (2007). amended in 72 Fed. Reg. 57235
(October
9,
2007)
(2007)
(Incineration),
referenced in 35 Ill. Adm. Code 728.142.
Subpart B of
49 CFR 107
(2007),
amended in 72 Fed. Reg. 55678
(October
1,
2007)
(Exemptions),
referenced generally in 35 Ill. Adm. Code 724.986 and 725.987.
49 CFR
171
(2007)
, amended in 72 Fed. Reg. 55678
(October
1,
2007),
73 Fed. Reg.
4699
(January 28,
2008),
and 73 Fed. Reg. 23362 (April 30,
2008)
(General
Information, Regulations, and
Definitions),
referenced
generally in
35
Ill.
Adm.
Code
733.118,
733.138, 733.152, and 739.143.
49 CFR 171.3
(2007) (Hazardous
Waste), referenced in
35
Ill. Adm.
Code
722.133.
49 CFR 171.8
(2007),
amended
in 72 Fed. Reg. 55678 (October 1,
2007),
73 Fed.
Reg. 4699
(January 28,
2008),
and 73 Fed. Reg. 23362 (April
30,
2008)
(Definitions
and
Abbreviations),
referenced in
35
Ill. Adm.
Code
733.118,
733.138,
733.152, 733.155, and 739.143.
49
CFR 171.15
(2007),
amended in 72 Fed. Reg. 55678
(October
1,
2007) (Immediate
Notice
of Certain Hazardous Materials
Incidents),
referenced in 35 Ill. Adm.
Code
723.130 and 739.143.
49 CFR
171.16
(2007) (Detailed
Hazardous Materials Incident Reports), referenced
in 35
Ill. Adm. Code 723.130 and 739.143.
49
CFR 172
(2007),
amended in 72 Fed. Reg. 55678
(October
1,
2007)
, 72 Fed.
Reg.
59146
(October
18,
2007),
73 Fed. Reg. 1089 (January 7,
2008),
73 Fed. Reg.
4699
(January 28,
2008),
and 73
Fed.
Reg. 20752 (April 16,
2008)
(Hazardous
Materials
Table, Special Provisions,
Hazardous Materials
Communications,
Emergency Response
Information, and Training Requirements),
referenced
generally
in 35 Iii.
Adm. Code
722.131, 722.132, 724.986,
725.987, 733.114,
733.118,
733.134,
733.138, 733.152,
733.155, and 739.143.
49 CFR
172.304
(2007),
amended
in 72 Fed. Reg.
55678
(October
1,
2007)
(Marking
Requirements),
referenced in 35
Ill. Adm.
Code 722.132.
Subpart F of 49
CFR 172
(2007),
amended in 72 Fed. Reg. 55678
(October
1,
2007)
(Placarding),
referenced in 35 Ill. Adm. Code 722.133.
49 CFR 173 (2007),
amended in 72 Fed. Reg. 55678
(October
1,
2007),
73
Fed.
Reg.
4699 (January
28,
2008),
and 73 Fed. Reg. 23362 (April 30,
2008)
(Shippers -
General
Requirements for Shipments and Packages) , referenced
generally in
35
Ill. Adm. Code
722.130, 724.986, 724.416, 725.987, 733.118, 733.138,
733.152,
and 739.143.
49 CFR
173.2
(2007) (Hazardous
Materials Classes and Index to Hazard
Class
Definitions),
referenced in 35 Ill. Adm. Code 733.152.
49 CFR
173.12
(2007),
amended in 73 Fed. Reg. 4699 (January 28,
2008)
(Exceptions
for Shipments of Waste
Materials),
referenced in 35 Ill.
Adm.
Code
724.416,
724.986, and 725.987.
49 CFR
173.28
(2007) (Reuse,
Reconditioning, and Remanufacture of Packagings),
referenced
in
35
111. Adm. Code 725.273.
49 CFR 173.50
(2007) (Class
1
- Definitions),
referenced in 35 Ill.
Adm.
Code
721.124.
49 CFR
173.54
(2006) (Forbidden
Explosives), referenced in 35
Ill. Adm.
Code
721.124.
49 CFR
173.115
(2007) (Class
2, Divisions 2.1, 2.2, and 2.3
- Definitions),
referenced in 35 Ill. Adm. Code 721.121.
49
CFR 174
(2007),
amended in 72 Fed. Reg. 55678
(October
1,
2007)
and 73 Fed.
Reg. 20752
(April 16,
2008)
(Carriage
by
Rail),
referenced generally in 35 Ill.
Adm. Code
733.118, 733.138, 733.152, and 739.143.
49
CFR 175
(2007),
amended in 72 Fed. Reg. 55678
(October
1,
2007),
73 Fed. Reg.
4699
(January 28,
2008)
, and 73 Fed. Reg. 23362 (April
30,
2008)
(Carriage
by
Aircraft),
referenced
generally
in 35
Ill. Adm.
Code
733.118, 733.138, 733.152,
and
739.143.
49
CFR 176
(2007),
amended in 72
Fed. Reg. 55678
(October
1,
2007)
and 73
Fed.
Reg.
4699 (January
28,
2008)
(Carriage
by
Vessel),
referenced generally in
35
Ill. Adm. Code
733.118, 733.138, 733.152, and 739.143.
49 CFR 177
(2007), amended in 73 Fed. Reg. 4699 (January 28,
2008)
(Carriage
by
Public
Highway), referenced generally in 35 Ill. Adm. Code 733.118, 733.138,
733.152,
and 739.143.
49
CFR 178
(2007),
amended in 72
Fed. Reg. 55678
(October
1,
2007) and 72
Fed.
Reg.
59146
(October
18,
2007)
(Specifications
for
Packagings),
referenced
generally in 35
Ill. Adm.
Code
722.130, 724.416,
724.986,
725.416, 725.987,
733.118, 733.138,
733.152, and 739.143.
49 CFR 179 (2007),
amended in 72 Fed. Reg. 55678
(October
1,
2007)
(Specifications
for Tank
Cars),
referenced in 35 Ill. Adm. Code
722.130,
724.416, 724.986,
725.416, 725.987, 733.118, 733.138, 733.152, and
739.143.
49
CFR 180
(200G)
(2007),
amended
in 72 Fed. Reg. 55678
(October
1,
2007)
and 73
Fed.
Reg. 4699
(January
28, 2008)
(Continuing
Qualification
and
Maintenance
of
Packagings),
referenced
generally
in 35 Ill. Adm. Code
724.986, 725.987,
733.118, 733.138,
733.152, and 739.143.
c)
Federal Statutes:
Section
11 of the
Atomic Energy
Act of 1954
(42
USC
2014),
as
amended through—
January 3, 2005
January
3, 2006, referenced in 35 Iii.
Adm.
Code
721.104 and
726.310.
Sections
201(v),
201(w),
and 512(j) of the Federal Food, Drug, and
Cosmetic
Act
(FFDCA; 21 USC
321(v), 321(w),
and 360b(j)), as amended
through January
3,
2005
January 3, 2006, referenced in Section 720.110 and 35
Ill. Adm.
Code
733.109.
Section
1412 of the Department of Defense
Authorization Act of 1986, Pub. L.
99-
145
(50
USC
1521(j)
(1)),
as amended through January 3,
2005 January 3, 2006,
referenced
in 35 Ill. Adm. Code 726.301.
d)
This Section incorporates no later
editions or amendments.
(Source:
Amended at 33
Ill.
Reg.
—,
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
Subpart D of
35
Ill. Adm.
Code
721 may file a
petition, as
specified in subsection
(n)
of this Section. The Board will grant
the
petition if
the following occur:
1)
The
petitioner demonstrates that the waste produced by a particular
generating
facility
does
not meet any of the criteria under which the waste was
listed as a
hazardous or
acute
hazardous waste; and
2)
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,
“EPA RCRA Delisting Program -—
Guidance Manual for the
Petitioner,”
incorporated
by
reference in Section
720.111(a).
A waste that is
so
excluded,
however, still may
be a
hazardous waste
by
operation of Subpart
C
of 35 Ill. Adm. Code
721.
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) (2) (C),
a waste that is
described in
these Sections and is either
a
waste listed in Subpart ID of 35 Ill.
Adm. Code
721, 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 must make the same demonstration as
required by
subsection
(a)
of this Section. Where the waste is a mixture of
a
c
‘,
•
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 that is so excluded
may
still be a
hazardous waste by operation of Subpart
C
of 35 Ill. Adm. Code
721.
c)
Ignitable,
corrosive, reactive and toxicity characteristic wastes.
If
the
waste is listed in codes
111,11 TTC,TT
T
R,” or “E” in Subpart ID of 35 Ill.
Adm.
Code
721, the following requirements apply:
1)
The
petitioner must demonstrate that the waste does not exhibit
the
relevant characteristic for which the waste was listed, as defined in 35
Ill.
Adm. Code
721.121, 721.122, 721.123, or 721.124, using any applicable methods
prescribed
in those Sections. The petitioner must 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; 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, “EPA RCRA Delisting
Program
-—
Guidance Manual for the Petitioner,
IT
incorporated by reference in
Section
720.111(a).
A waste that is so excluded, however, may still be a
hazardous waste by
operation of Subpart
C
of
35
111. Adm.
Code
721.
d)
Toxic waste.
If the waste is listed in
code
“T’
T in Subpart ID of 35 Ill.
Adm. Code
721, the following requirements apply:
1)
The petitioner must demonstrate that the waste fulfills the
following
criteria:
A)
It does
not contain the constituent or constituents
(as
defined in
Appendix G
of
35
Ill. Adm. Code
721)
that caused USEPA to list the waste; or
B)
Although containing one or more of the hazardous constituents
(as
defined
in
Appendix
G
of
35
Ill. Adm. Code
721)
that caused USEPA to list the waste, the
waste does
not meet the criterion of 35 Ill. Adm. Code
721.111(a) (3)
when
considering
the factors used in 35 111. Adm. Code
721.111(a) (3) (A)
through
(a) (3) (K)
under which the waste was listed as hazardous.
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 must 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
that is
so
excluded, however, may still
be a
hazardous waste
by
operation
of Subpart
C
of
35
111. Adm.
Code
721.
1)
e)
Acute hazardous
waste. If
the waste
is
listed with the code
HTT
j
Subpart D of 35 Ill.
Adm.
Code
721,
the
following
requirements
apply:
1)
The petitioner
must 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, “EPA RCPA Delisting
Program
-—
Guidance
Manual for the Petitioner,”
incorporated by
reference
in
Section 720.111
(a)
3)
The petitioner
must 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 that is so excluded, however, may still be a hazardous waste by
operation of Subpart C of 35 Ill. Adm. Code 721.
f)
This subsection
(f)
corresponds with 40 CFR
260.22(f),
which
USEPA
has
marked “reserved.” This
statement
maintains structural
consistency with
the
federal
regulations.
g)
This
subsection (g) corresponds with 40 CFR 260.22(g), which USEPA has
marked “reserved.”
This statement maintains structural consistency with
the
federal
regulations.
h)
Demonstration samples must consist of enough representative samples,
but
in no case
less than four samples, taken over
a
period of time sufficient
to
represent
the variability or the uniformity of the waste.
1)
Each petition must include, in addition to the information required
by
subsection
(n)
of this Section:
1)
The name
and address of the laboratory facility performing the sampling
or
tests of the
waste;
2)
The
names and qualifications of the persons 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 that 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;
‘..
I ,
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
techniques 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
T
s
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 that
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 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
EPA RCRA Delisting Program -—
Guidance Manual for the
Petitioner,TT
incorporated by reference in Section
720.111(a).
m)
Delisting of specific wastes from
specific sources
that have been adopted
by
USEPA may be proposed as State
regulations that are identical
in substance
pursuant to Section
720.120(a).
n)
Delistings that
have
not been adopted by
USEPA
may be proposed to the
Board pursuant to a
petition
for adjusted standard pursuant to Section 28.1 of
the
Act
[415
ILCS
5/28.11
and Subpart D of 35 Ill. Adm. Code 104. The
justification for
the
adjusted standard is as
specified
in subsections
(a)
through (g) of this Section, 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
101.304,
the petitioner
must
serve
copies of
the petition, and any
other
documents filed with the Board, on
USEPA
at
the
following addresses:
USE PA
Office of Solid Waste and Emergency Response
‘1
,
1200 Pennsylvania
Avenue,
NW
Washington, D.C.
20460
USEPA, Region 5
77 West
Jackson Boulevard
Chicago, IL
60604
2)
The Board
will mail copies
of
all opinions and orders
to
USEPA at the
above addresses.
3)
In
conjunction with the normal updating of the RCRA regulations, the Board
will maintain,
in Appendix I of
35
Iii. Adm.
Code
721,
a
listing of all adjusted
standards granted by
the Board.
o)
The
Agency may determine in
a
permit or a letter directed to a generator
that, based on 35
111. 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
will
not be
conclusive with reference
to
other
persons or the
Board.
p)
ny 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 that would render the Illinois RCRA
program less
stringent than if the decision were made
by
USEPA.
r)
Delistings
apply only within Illinois. Generators must comply with
35
Ill. Adm. Code
722 for waste that is hazardous in any
state to
which it is
to be
transported.
(Source:
Amended at 33 Iii. Reg.
, effective
ILLINOIS RECIS
POLLUTION
CONTROL EOD
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I
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
Purpose and
Scope
Definition
of Solid Waste
Definition
of Hazardous Waste
Exclusions
Special Requirements
for Hazardous Waste Generated
Requirements for Recyclable Materials
Residues of Hazardous Waste in Empty
Containers
PCB Wastes Regulated under TSCA
Requirements for Universal Waste
SUBPART B:
CRITERIA FOR IDENTIFYING THE
CHARACTERISTICS OF HAZARDOUS WASTE
AND FOR LISTING HAZARDOUS WASTES
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
721.135
Wood Preserving Wastes
SUBPART E:
EXCLUSIONS AND
EXEMPTIONS
Section
Comparable or Syngas
Fuel Exclusion
Conditional Exclusion
for Used, Broken CRTs and Processed CRT
Glass
Recycling
Conditional Exclusion for
Used,
Intact
CRTs Exported for Recycling
Notification
and Recordkeeping for
Used, Intact CRTs Exported for
SUBPART A:
GENERAL PROVISIONS
SEp,
42008
Section
721.101
721.102
721. 103
721. 104
721.105
Generators
721.106
721.107
721.108
721.109
$1L
rf9
by Small Quantity
Section
721.110
721.111
Criteria for Identifying the Characteristics of
Hazardous Waste
Criteria
for
Listing Hazardous Waste
Section
721.120
721.121
721.122
721.123
721.124
General
Characteristic of Ignitability
Characteristic of Corrosivity
Characteristic of Reactivity
Toxicity Characteristic
Section
721.130
721.131
721.132
721.133
721.138
721.139
Undergoing
721.140
721.141
Reuse
72l.Apped4*APPENDIX
A
Representative
Sampling
Methods
721.Appe4-iAPPENDIX
B
Method
1311 Toxicity Characteristic
Leaching
Procedure
(TCLP)
721.Apped-i*APPENDIX
C Chemical Analysis
Test
Methods
721.Tab1cIABIE
A Analytical
Characteristics
of
Organic
Chemicals (Repealed)
721.Tpb1cTABLE
B Analytical
Characteristics
of Inorganic Species
(Repealed)
721.T3b1cTABLE
C
Sample
Preparation/Sample
Introduction
Techniques
(Repealed)
72l.Apped4.PPEND1X
G Basis for
Listing Hazardous
Wastes
72l.Aped4EAEPEND1X
H Hazardous Constituents
721.Appe44EAPPENflIX
I Wastes Excluded
by
Administrative
Action
72l.TablcIAL
A Wastes
Excluded
by
USEPA
pursuant to
40 CFR
260.20
and
260.22
from
Non-Specific
Sources
721.Tab1cTABIE
B Wastes Excluded
by USEPA
pursuant to 40 CFR
260.20 and 260.22
from
Specific Sources
721.Tablc
C Wastes
Excluded
by USEPA pursuant
to
40
CFR 260.20
and 260.22
from
Commercial
Chemical
Products,
Off-Specification
Species, Container
Residues,
and
Soil Residues
Thereof
72l.TablcThL
0 Wastes Excluded
by the Board
by
Adjusted Standard
721.AppeAPENIX
J Method of Analysis
for
Chlorinated Dibenzo-p-Dioxins
and
Dibenzofurans
(Repealed)
72l.AppeEAPPEN0IX
Y Table
to Section 721.138
72l.Appe4APENIX
Z Table
to Section 721.102
AUTHORITY:
Implementing
Sections 7.2
and 22.4
and
authorized
by Section
27 of
the
Environmental
Protection
Act
[415
ILCS
5/7.2,
22.4 and
271
SOURCE: Adopted
in
R8l-22
at
5 Ill. Req. 9781,
effective May 17,
1982;
amended
and codified
in R8l-22
at 6 Ill.
Reg. 4828, effective
May 17, 1982;
amended
in
R82-l8
at
7
Ill. Req. 2518,
effective
February 22, 1983;
amended in R82-19
at 7
Ill.
Reg. 13999,
effective
October 12,
1983; amended in
R84-34, 61 at
8 Ill.
Req. 24562,
effective
December
11, 1984; amended
in
R84-9 at
9 Ill. Req.
11834,
effective July
24, 1985; amended
in R85-22
at 10 Iii.
Req. 998,
effective
January 2, 1986;
amended in R85-2
at 10 Ill.
Reg.
8112, effective May
2,
1986;
amended
in
R86-l
at
10 Ill. Reg. 14002,
effective August
12, 1986; amended
in
R86-l9
at
10
111. 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. Req.
16698,
effective
NovcmbcrSeterrther
30,
1987;
amended in
R87-5 at 11 Ill. Req.
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. Req.
12070, effective
July
12,
1988;
amended in
R87-39 at 12 Ill.
Req.
13006,
effective
July 29,
1988; amended
in R88-16 at
13 Ill.
Req. 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. Req.
7950,
effective
May 9, 1991;
amended
in
R90-ll
at
15 Ill. Req.
9332,
effective June
17, 1991;
amended
in
R91-l at 15 Ill.
Req. 14473,
effective NovcmbcrSeotember
30,
1991;
amended
in
R91-l2
at
16 Ill.
Reg. 2155,
effective January
27, 1992; amended
in
R91-26 at
16
Ill.
Req. 2600,
effective February
3,
1992; amended
in R9l-l3
at 16
Ill. Req. 9519,
effective
June
9, 1992; amended
in
R92-l at 16
Ill. Req. 17666,
effective
November
6,
1992;
amended
in R92-lO
at 17
Ill. Req. 5650,
effective
March
26, 1993;
amended in
R93-4
at
17 Ill. Reg. 20568,
effective November
22,
1993;
amended
in R93-16
at
18
Ill.
Reg.
6741, effective
April 26, 1994; amended
in
R94-7
at
18
Ill. Req. 12175,
effective
July 29, 1994; amended
in R94-l7
at 18
Ill. Req.
17490, effective
November
23, 1994;
amended in R95-6
at 19 Ill. Req.
9522,
effective June 27,
1995; amended
in R95-20
at
20
111.
Reg.
10963,
effective August 1, 1996; amended in R96-l0/R97-3/R97-5
at 22 Ill.
Reg. 275,
effective December 16, 1997; amended
in R98-12 at 22 Ill. Reg. 7615,
effective
April
15, 1998;
amended in R97-21/R98-3/R98-5
at 22 Ill. Reg.
17531, effective
September 28, 1998;
amended in R98-21/R99-2/R99-7
at
23 Ill.
Reg. 1718,
effective January
19, 1999; amended
in R99-l5
at
23 Ill.
Reg. 9135, effective
July 26, 1999;
amended in R00-l3
at 24 Ill. Reg. 9481,
effective June 20, 2000;
amended in R0l-3 at
25
Iii.
Reg.
1281, effective January
11, 2001; amended in
R0l-21/R0l-23 at 25
Ill. Reg.
9108, effective July
9,
2001;
amended in R02-
l/R02-12/R02-17 at
26 Ill. Reg.
6584, effective April 22, 2002;
amended in R03-
18 at 27
Ill. Reg. 12760, effective
July 17, 2003; amended in R04-16
at 28 Ill.
Reg. 10693,
effective July 19, 2004;
amended in R05-8
at
29 Ill. Reg.
6003,
effective April 13, 2005; amended in
R06-5/R06-6/R06-7 at
30
Ill. Reg.
2992,
effective February 23, 2006; amended
in R06-l6/R06-17/R06-l8
at
31 111.
Reg.
791, effective December 20, 2006; amended
in R07-5/R07-l4
at
32 111. Reg.
11786,
effective July 14, 2008; amended in R09-3
at 33 Iii. Reg.
, effective
SUBPART A:
GENERAL PROVISIONS
Section 721.102
Definition of Solid Waste
a)
Solid waste.
1)
A solid waste is any discarded
material that is not excluded
by Section
721.104(a)
or that is not excluded
pursuant to 35 111. Adm.
Code
720.130
and
720.131.
2)
A discarded
material
is any material that is described
as follows:
A)
Abandoned,
as
explained in
subsection
(b)
of this Section;
B)
Recycled,
as
explained
in subsection
(c)
of this Section;
C)
Considered inherently waste-like,
as explained in subsection
(d)
of
this
Section; or
D)
A military munition identified as
a
solid waste in
35 Ill. Adm. Code
726.302.
b)
A material is
a
solid waste
if it is abandoned in one of the following
ways:
1)
It is disposed of;
2)
It is burned or incinerated; or
3)
It is accumulated, stored,
or treated
(but
not recycled)
before or in lieu
of
being abandoned
by
being
disposed of, burned, or incinerated.
c)
A material is a solid waste
if it is recycled -— or accumulated,
stored,
or
treated before recycling
-— as specified in subsections
(c) (1)
through
(c)
(4)
of this Section, if one of the
following occurs with regard
to
the
material:
1)
The
material is
used in a manner constituting
disposal.
A)
A
material that is
noted with
a yes’ in column
1 of the
table in
Appendix
Z of
this
Part
is
a
solid waste
when
one
of the
following occurs
i)
The
material
is applied to or
placed on
the land
in
a
manner
that
constitutes
disposal;
or
ii)
The
material
is
used to
produce products
that are applied
to or placed on
the land
or are
otherwise
contained
in products that
are applied to
or placed on
the
land
(in
which
cases
the
product
itself remains
a
solid
waste)
B)
However,
a
commercial
chemical product
that
is
listed
in Section 721.133
is not
a
solid
waste
if
it is
applied
to
the land
and
that is its
ordinary
manner of
use.
2)
The
material is
burned for energy
recovery.
A)
A
material
that is noted
with
a “yes”
in column
2 of the
table in Appendix
Z of this
Part
is a solid waste
when one
of
the
following
occurs:
i)
It is
burned to
recover energy;
ii)
It is
used to produce a
fuel or is otherwise
contained in
fuels
(in
which
case the
fuel
itself remains a solid
waste)
iii)
It is
contained
in fuels
(in
which
case
the
fuel
itself
remains
a
solid
waste)
B)
However,
a commercial
chemical
product that
is
listed
in
Section
721.133
is
not a
solid waste if it
is itself
a fuel.
3)
Reclaimed.
A material noted
with
a
“yes” in column 3
of the
table in
Appendix Z
of this
Part is
a
solid
waste
when
reclaimed
(except
as provided
under Section
721.104
(a)
(17)).
A material noted
with a “ -—
“ in
column 3 of
Appendix
Z
of this Part is
not a solid
waste when
reclaimed.
4)
Accumulated
speculatively.
A material
noted
with
“yes”
in column 4 of
the
table in
Appendix
Z of this Part is
a solid waste
when
accumulated
speculatively.
d)
Inherently
waste-like materials.
The following
materials
are solid wastes
when they
are recycled
in any manner:
1)
Hazardous waste
numbers F020, F021
(unless
used
as
an ingredient
to make a
product
at
the site of generation),
F022,
F023, F026,
and F028.
2)
A
secondary
material fed to
a
halogen
acid
furnace that exhibits
a
characteristic
of
a hazardous waste
or which is listed
as a hazardous
waste,
as
defined
in Subpart C or
ID of this Part,
except
for
brominated
material that
meets
the
following
criteria:
A)
The material
must
contain
a bromine concentration
of at least
45 percent;
B)
The
material
must contain
less than
a total of
one percent
of toxic
organic
compounds
listed in Appendix
H of
this Part;
and
C)
The material is
processed continually
on-site
in
the
halogen acid furnace
via
direct
conveyance
(hard
piping).
3)
The following criteria are used to add wastes
to
the list:
A)
Disposal method or toxicity.
i)
The material is ordinarily disposed of, burned, or incinerated;
or
ii)
The material contains toxic constituents listed in Appendix
H of this Part
and these
constituents are not ordinarily found in raw materials
or products for
which the
material substitutes
(or
are found in raw materials
or products in
smaller
concentrations)
and is not
used or reused during the recycling process;
and
B)
The
material may
pose a
substantial hazard
to human health and the
environment when recycled.
e)
Materials that are not solid waste when recycled.
1)
A material
is not
asolid
a—waste when it can be shown to be recycled
by
fulfilling one
of the following
conditions:
A)
It is used
or reused
as
an ingredient
in an industrial process to make
a
product,
provided the material is not
being reclaimed; or
B)
It is used or reused as effective substitutes for commercial products; or
C)
It is
returned
to the original process from which it is generated, without
first being reclaimed or land disposed. The material must be returned as
a
substitute for feedstock materials. In cases where the original process
to
which the material is returned is a secondary process, the material must
be
managed in
such
a
manner
that there is no placement on the land. In cases where
the material is
generated and reclaimed
within the primary mineral processing
industry, the
conditions of
the
exclusion
found at Section 721.104
(a) (17)
apply
rather than this
provision.
2)
The
following materials are solid wastes, even
if the recycling involves
use,
reuse, or return to the original process
(described
in subsections
Ce)
(1) (A)
through
Ce) (1) (C)
of this
Section)
A)
A material used in a manner constituting disposal or
used to
produce
a
product that is applied to the land; or
B)
A material burned for energy recovery,
used to
produce
a
fuel, or
contained in fuels; or
C)
A material accumulated speculatively; or
D)
A material
listed
in subsections
Cd) (1)
and
Cd) (2)
of this Section.
f)
Documentation of claims that
a material is not a solid waste or is
conditionally exempt from regulation. A respondent
in an action to enforce
regulations implementing Subtitle
C
of RCPA
or Section 21 of the Environmental
Protection Act that raises
a
claim that
a
certain
material is not a solid waste
or
that the material is conditionally exempt from
regulation must demonstrate
that there is a known market or disposition for the material and that the
material meets
the
terms of the exclusion or exemption. In doing
so,
the
person
must
provide appropriate
documentation
(such
as contracts showing that
a second
person uses
the material as
an ingredient
in
a
production
process) to
demonstrate that the
material is
not a waste or that
the
material
is exempt from
regulation. In
addition, an owner
or operator of
a
facility claiming
that it
actually is recycling a
material must
show that it has the necessary
equipment
to
recycle that
material.
(Source:
Amended at 33
Ill. Reg.
—,
effective
Section
721.104
Exclusions
a)
Materials that are not solid wastes.
The following materials are not
solid wastes for the purpose of this Part:
1)
Sewage.
A)
Domestic
sewage
(untreated
sanitary wastes that pass through a sewer
system); and
B)
Any
mixture of domestic sewage
and other waste that passes through
a
sewer
system to
publicly-owned treatment
works for treatment.
2)
Industrial wastewater discharges
that are point source discharges with
National
Pollutant Discharge Elimination
System
(NPDES)
permits issued by the
Agency
pursuant
to
Section 12(f)
of the Environmental Protection Act
[415
ILCS
5/12(f)] and 35
Iii. Adm.
Code 309.
BOARD NOTE: This exclusion applies
only to the actual point source
discharge. It
does
not exclude industrial wastewaters
while they are being
collected, stored, or treated before discharge,
nor does it exclude sludges that
are
generated
by
industrial wastewater treatment.
3)
Irrigation return flows.
4)
Source, by-product, or special nuclear material,
as
defined
by section 11
of the Atomic Energy Act of 1954, as amended
(42
USC
2014),
incorporated
by
reference in 35 Ill. Adm. Code
720.111(b).
5)
Materials subjected to in-situ mining techniques that are not removed
from
the
ground as part of the extraction process.
6)
Pulping liquors
(i.e.,
black liquors) that are reclaimed in
a
pulping
liquor recovery furnace and then reused in the pulping process, unless it
is
accumulated speculatively, as defined in Section
721.101(c)
7)
Spent sulfuric acid used to produce virgin sulfuric acid, unless it
is
accumulated
speculatively,
as defined in Section
721.101(c).
8)
Secondary materials
that are reclaimed and returned to the original
process or
processes in which
they were generated, where they are reused in
the
production process, provided
that the following is true:
A)
Only tank storage is involved,
and the entire process through completion
of
reclamation is closed
by being entirely connected with pipes or other
comparable
enclosed means of conveyance;
B)
Reclamation does not involve controlled flame
combustion
(such
as occurs
in
boilers, industrial furnaces, or incinerators);
C)
The
secondary materials are
never accumulated in
such tanks for over 12
months without
being reclaimed;
and
D)
The
reclaimed material is not
used to produce a fuel
or used to produce
products
that are used in a manner
constituting disposal.
9)
Wood preserving wastes.
A)
Spent wood preserving solutions
that have been used and which are
reclaimed and reused for their original
intended purpose;
B)
Wastewaters from the wood preserving
process that have been reclaimed
and
which
are
reused to treat wood; and
C)
Prior
to
reuse, the wood preserving
wastewaters and spent wood
preserving
solutions
described in subsections
(a) (9) (A)
and
(a) (9) (B)
of this Section,
so
long as they
meet all of the following
conditions:
i)
The wood preserving wastewaters
and spent wood preserving solutions are
reused on-site at water-borne plants
in the production process for their
original intended purpose;
ii)
Prior to reuse, the wastewaters and
spent wood preserving solutions are
managed
to
prevent release
to
either land
or groundwater or both;
iii)
Any unit used to manage wastewaters
or spent wood preserving solutions
prior
to
reuse can be visually or otherwise
determined to prevent such releases;
iv)
Any drip pad used to manage the wastewaters
or spent wood preserving
solutions prior to
reuse
complies with the standards in
Subpart W of 35 Ill.
Adm. Code 725,
regardless
of whether the plant generates
a total of less than
100 kg/month of
hazardous
waste; and
v)
Prior to
operating
pursuant to this exclusion, the
plant owner or operator
prepares a
one-time notification
to the Agency stating that
the plant intends
to
claim the
exclusion, giving
the date on which the plant intends
to begin
operating
under the exclusion,
and containing the following language: “I
have
read the
applicable regulation
establishing an exclusion for wood preserving
wastewaters and
spent
wood
preserving solutions and understand it requires
me to
comply at
all times with
the conditions set
out
in the regulation.’
The plant
must
maintain
a copy
of
that document in its on-site records until
closure of
the
facility. The exclusion
applies only so long as the plant meets
all of the
conditions. If the plant
goes out of compliance with any condition,
it
may
apply to
the Agency for reinstatement.
The Agency must reinstate
the exclusion
in
writing if it finds that
the plant has returned to compliance with
all
conditions and that the violations
are not likely to recur. If the Agency
denies an application, it must
transmit to the applicant specific, detailed
statements in writing
as to
the reasons
it denied the application. The
applicant under this subsection
(a) (9) (C) (v)
may appeal the Agency’s
determination to deny the reinstatement,
to grant the reinstatement with
conditions, or to terminate a reinstatement
before the Board pursuant
to Section
40 of the Act
[415
ILCS
5/401
10)
Hazardous waste numbers
1(060, 1(087, K141, K142, 1(143, 1(144,
1(145, 1(147,
and
1(148, and any wastes from the
coke by-products processes that are
hazardous
only because they exhibit the toxicity
characteristic specified in Section
721.124, when subsequent to generation
these materials are recycled
to coke
ovens,
to
the tar recovery process
as a feedstock
to
produce coal tar,
or are
mixed with coal tar prior to the
tarTs
sale or refining. This
exclusion is
conditioned
on
there being no land
disposal of the waste from
the point it is
generated
to
the point it is recycled
to coke ovens,
to
tar recovery,
to the tar
refining processes, or prior
to when it is mixed with coal.
11)
Nonwastewater splash condenser
dross residue from
the
treatment
of
hazardous waste number K061 in
high temperature metals recovery
units, provided
it
is shipped in
drums
(if
shipped)
and not land disposed
before recovery.
12)
Certain oil-bearing hazardous
secondary materials
and recovered oil, as
follows:
A)
Oil-bearing
hazardous
secondary materials
(i.e.,
sludges, by-products, or
spent
materials)
that are
generated at a petroleum refinery
(standard
industrial
classification
(SIC)
code
2911)
and are inserted into the
petroleum refining
process
(SIC
code
2911: including,
but not limited
to,
distillation,
catalytic
cracking, fractionation, gasification
(as
defined in
35
Ill. Adm.
Code
720.110),
or thermal cracking units
(i.e.,
cokers)),
unless the material is placed
on the
land, or speculatively accumulated
before being so recycled. Materials inserted
into thermal cracking units are excluded
under this subsection
(a) (12),
provided
that the coke product also
does
not
exhibit a characteristic of hazardous
waste.
Oil-bearing hazardous secondary materials may
be inserted into the same
petroleum refinery where they are generated
or sent directly
to
another
petroleum refinery and still
be
excluded
under this provision. Except
as
provided in subsection
(a) (12) (B)
of this
Section, oil-bearing hazardous
secondary materials generated elsewhere
in the petroleum industry
(i.e.,
from
sources other than petroleum refineries)
are not excluded under this Section.
Residuals generated from processing or recycling
materials excluded under
this
subsection
(a) (12) (A),
where such materials
as generated would have otherwise
met a listing under Subpart ID of this Part, are
designated as USEPA hazardous
waste number F037 listed wastes when disposed of
or intended for disposal.
B)
Recovered oil that is recycled in the same manner
and with the same
conditions as
described
in subsection
(a) (12) (A)
of
this Section. Recovered
oil
is oil that has
been
reclaimed from secondary materials
(including wastewater)
generated from normal petroleum industry practices, including
refining,
exploration and production,
bulk storage, and transportation
incident thereto
(SIC
codes
1311, 1321,
1381, 1382, 1389, 2911, 4612, 4613,
4922, 4923, 4789,
5171,
and 5172) . Recovered
oil does not include oil-bearing
hazardous wastes
listed
in Subpart ID
of this Part; however, oil recovered
from such wastes may
be
considered recovered
oil. Recovered oil does not include
used oil, as defined
in 35
Ill. Adm.
Code 739.100.
13)
Excluded scrap metal (processed
scrap metal, unprocessed
home scrap metal,
and
unprocessed prompt scrap metal)
being recycled.
14)
Shredded circuit boards being recycled,
provided that they meet the
following conditions:
A)
The circuit boards are stored in containers
sufficient to prevent a
release to the
environment
prior to recovery; and
B)
The circuit boards are free
of mercury switches, mercury
relays, nickel
cadmium batteries, and lithium
batteries.
15)
Condensates
derived
from the overhead
gases
from
kraft
mill
steam
strippers
that
are
used to
comply with
federal Clean
Air Act
regulation
40 CFR
63.446
Ce).
The
exemption applies
only
to combustion at
the
mill
generating
the
condensates.
16)
Comparable
fuels
or comparable
syngas fuels
(i.e.,
comparable
or syngas
fuels)
that
meet the requirements
of
Section 721.138.
17)
Spent
materials
(as
defined
in
Section
721.101)
(other
than hazardous
wastes listed
in Subpart
D of this
Part) generated within
the primary
mineral
processing
industry from
which minerals,
acids,
cyanide,
water, or other
values
are recovered
by mineral
processing or
by benefication,
provided
that the
following
is
true:
A)
The
spent material
is legitimately
recycled
to
recover minerals,
acids,
cyanide,
water, or other
values;
B)
The spent
material is not
accumulated speculatively;
C)
Except
as provided
in subsection
(a) (17) CD)
of
this Section, the
spent
material is
stored in
tanks, containers,
or
buildings
that
meet the following
minimum
integrity
standards:
a building must
be an
engineered
structure with
a
floor,
walls,
and a roof all
of which are made
of
non-earthen materials
providing
structural
support (except
that smelter
buildings may have
partially
earthen
floors, provided
that the spent
material
is
stored on the non-earthen
portion),
and have a
roof suitable for
diverting rainwater
away from the
foundation;
a tank must
be
free standing,
not be a
surface
impoundment
(as
defined
in
35 Ill. Adm.
Code
720.110),
and
be
manufactured of a
material
suitable
for
containment
of its
contents;
a container
must be free
standing
and
be
manufactured of
a material suitable
for containment
of its contents.
If a
tank or
container contains
any particulate
that
may
be subject
to wind
dispersal,
the owner or operator
must operate
the
unit in a
manner that
controls
fugitive
dust.
A tank, container,
or building
must
be designed,
constructed,
and operated
to
prevent significant
releases
to the
environment of
these
materials.
D)
The
Agency must allow
by permit that
solid mineral processing
spent
materials
only
may be placed
on pads, rather than
in tanks, containers,
or
buildings if the
facility
owner
or operator can demonstrate
the
following:
the
solid
mineral
processing
secondary
materials do not contain
any free
liquid;
the
pads
are designed,
constructed,
and operated
to prevent
significant
releases
of
the
spent
material
into the
environment; and
the
pads
provide the
same degree
of
containment
afforded
by
the
non-RCRA tanks, containers,
and buildings
eligible
for exclusion.
i)
The
Agency
must also consider
whether
storage on
pads
poses
the
potential
for
significant
releases via groundwater,
surface
water, and air exposure
pathways.
Factors
to
be
considered
for
assessing
the
groundwater, surface
water, and
air exposure
pathways must include
the
following:
the volume
and
physical
and
chemical properties
of the
spent
material, including
its
potential
for
migration
off the pad; the
potential for
human or
environmental
exposure
to
hazardous
constituents
migrating
from the
pad
via
each exposure pathway;
and
the
possibility
and extent
of harm
to
human
and environmental
receptors via
each
exposure
pathway.
ii)
Pads
must
meet
the following
minimum standards:
they must
be designed
of
non-earthen
material
that is
compatible
with the
chemical nature of
the mineral
processing
spent
material; they
must
be
capable
of withstanding
physical
stresses
associated
with placement
and removal;
they must have
runon and
runoff
controls;
they
must be
operated
in
a
manner
that
controls fugitive
dust; and
they must
have
integrity
assurance
through inspections
and maintenance
programs.
iii)
Before
making a
determination
under
this subsection
(a) (17)
(D),
the Agency
must
provide
notice
and the
opportunity for comment
to all persons
potentially
interested
in
the
determination.
This can
be
accomplished
by placing
notice
of
this action
in
major local
newspapers,
or broadcasting
notice over local
radio
stations.
BOARD
NOTE:
See Subpart
D of
35
Ill. Adm.
Code
703 for the
RCRA Subtitle
C permit
public
notice
requirements.
E)
The
owner or
operator
provides
a
notice
to
the
Agency,
providing the
following
information: the
types of materials
to be
recycled,
the type and
location
of
the storage units
and recycling processes,
and the
annual quantities
expected
to
be
placed
in
non-land-based
units. This
notification must
be
updated when
there
is
a change in the
type
of materials
recycled or the
location
of the
recycling process.
F)
For
purposes
of
subsection
(b) (7)
of this
Section, mineral
processing
spent
materials
must be the result
of mineral processing
and may not
include
any
listed
hazardous wastes.
Listed hazardous
wastes and
characteristic hazardous
wastes
generated by
non-mineral
processing
industries are
not eligible for
the
conditional
exclusion from
the definition
of solid waste.
18)
petrochemical
recovered
oil
from an associated
organic chemical
manufacturing
facility,
where the oil
is
to be
inserted
into the petroleum
refining
process
(SIC
code
2911)
along
with normal petroleum
refinery process
streams,
provided
that both
of the following
conditions
are
true of the oil:
A)
The oil
is hazardous
only
because it exhibits
the
characteristic
of
ignitability
(as
defined
in Section
721.121)
or
toxicity for
benzene
(Section
721.124,
USEPA
hazardous waste
code
D0l8);
B)
The
oil generated
by
the organic
chemical
manufacturing
facility
is
not
placed on
the land, or
speculatively
accumulated
before
being recycled into
the
petroleum
refining process.
An ‘associated
organic
chemical
manufacturing
facility”
is
a facility for
which all of
the following
is true:
its primary
SIC
code
is
2869,
but
its operations
may also
include SIC
codes 2821, 2822,
and
2865; it is
physically
co-located with
a petroleum
refinery;
and the
petroleum
refinery to
which the
oil being recycled
is returned
also
provides hydrocarbon
feedstocks
to the organic
chemical manufacturing
facility.
“Petrochemical
recovered
oil”
is oil that has
been reclaimed
from
secondary materials
(i.e.,
sludges,
by-products,
or
spent
materials,
including
wastewater)
from
normal
organic
chemical manufacturing
operations,
as
well as
oil recovered from
organic
chemical
manufacturing
processes.
19)
Spent
caustic solutions
from petroleum
refining
liquid treating
processes
used as
a
feedstock
to produce cresylic
or naphthenic
acid, unless
the material
is placed
on
the land or
accumulated
speculatively, as
defined in Section
721.101(c).
20)
Hazardous secondary
materials
used to make
zinc
fertilizers, provided
that
the following
conditions
are satisfied:
44
A)
Hazardous
secondary materials
used
to make zinc
micronutrient
fertilizers
must
not
be
accumulated
speculatively,
as
defined in
Section 721.101
Cc) (8).
B)
A
generator or
intermediate
handler
of zinc-bearing
hazardous secondary
materials
that are to be
incorporated into
zinc fertilizers
must fulfill
the
following
conditions:
i)
It
must submit
a one-time notice
to
the Agency
that contains the
name,
address,
and USEPA
identification
number
of
the
generator
or intermediate
handler
facility,
that
provides
a brief description
of the
secondary material
that
will
be
subject to the
exclusion, and which
identifies when
the
manufacturer intends
to begin managing
excluded zinc-bearing
hazardous
secondary
materials
under the
conditions specified
in this subsection
(a) (20)
ii)
It
must store
the
excluded
secondary
material
in
tanks,
containers,
or
buildings
that
are
constructed
and maintained
in a way
that prevents
releases
of
the
secondary
materials
into the
environment.
At a
minimum, any building
used
for
this
purpose
must
be an engineered
structure
made
of non-earthen materials
that
provide
structural
support, and it
must have
a
floor,
walls, and
a
roof
that prevent
wind
dispersal
and contact with
rainwater. A tank
used for
this
purpose must
be
structurally
sound and, if outdoors,
it must have
a roof or
cover that
prevents contact
with
wind and rain.
A container used
for this
purpose
must be
kept closed,
except
when it is necessary
to add or remove
material,
and
it must
be in sound condition.
Containers
that are stored
outdoors
must be
managed within
storage areas
that fulfill the
conditions of
subsection
(a) (20) (F)
of this
Section:
iii)
With
each off-site
shipment
of
excluded hazardous
secondary materials,
it
must
provide
written notice
to the receiving
facility
that
the material is
subject
to
the
conditions of this
subsection
(a) (20)
iv)
It
must maintain
records
at
the
generator’s
or
intermediate
handler’s
facility
for
no less than
three years
of all shipments
of excluded
hazardous
secondary
materials.
For each
shipment
these records
must,
at a minimum,
contain
the
information
specified
in
subsection
(a) (20)
(G)
of
this Section.
C)
A
manufacturer of
zinc fertilizers
or zinc
fertilizer
ingredients
made
from
excluded
hazardous secondary
materials
must
fulfill the
following
conditions:
i)
It
must store
excluded hazardous
secondary
materials
in
accordance
with
the storage
requirements
for generators
and
intermediate
handlers,
as specified
in
subsection
(a) (20) (B) (ii)
of this Section.
ii)
It must
submit
a one-time
notification
to
the
Agency that, at
a minimum,
specifies
the
name, address,
and USEPA
identification
number of the
manufacturing
facility and
which identifies
when the manufacturer
intends
to
begin managing
excluded zinc-bearing
hazardous
secondary materials
under the
conditions
specified
in this
subsection
(a) (20)
iii)
It
must maintain for
a
minimum
of three years
records
of all shipments
of
excluded
hazardous
secondary
materials
received by the
manufacturer,
which
must
at
a minimum
identify
for each shipment
the
name and
address
of the generating
facility,
the name
of transporter,
and
the date
on
which
the materials
were
received,
the quantity
received, and
a brief description
of the industrial
process
that
generated the
material.
iv)
It must submit an annual
report to the Agency that identifies
the total
quantities of all excluded
hazardous secondary materials
that were used
to
manufacture zinc fertilizers
or zinc fertilizer ingredients
in the previous
year,
the
name and address
of each generating facility,
and the industrial
processes from which the hazardous
secondary materials were
generated.
D)
Nothing in this Section preempts,
overrides, or otherwise
negates the
provision in
35
Iii. Adm.
Code 722.111 that requires any person
who generates
a
solid waste
to
determine if
that waste is a hazardous waste.
E)
Interim
status
and permitted
storage units that have
been used to store
only zinc-bearing hazardous wastes
prior to the submission of the
one-time
notice described in subsection
(a)
(20) (B) (1)
of this Section, and
that afterward
will
be used
only
to
store hazardous
secondary materials excluded under
this
subsection
(a) (20),
are not
subject to the closure requirements of
35
Ill.
Adm.
Code 724 and 725.
F)
A container used to store excluded
secondary material must fulfill
the
following conditions:
i)
It must have containment structures
or systems sufficiently impervious
to
contain leaks, spills, and accumulated precipitation;
ii)
It must provide for effective drainage
and removal of leaks, spills,
and
accumulated precipitation; and
iii)
It must prevent run-on into the
containment system.
BOARD NOTE:
Subsections
(a) (20) (F)
(i)
through
(a) (20) (F) (iii)
are derived
from
40 CFR
261.4(a) (20) (ii) (B) (1)
through
(a) (20) (ii) (B) (3).
The Board
added the
preamble to these federal paragraphs
as subsection
(a) (20) (F)
to
comport
with
Illinois Administrative
Code
codification
requirements.
G)
Required records of shipments of excluded
hazardous secondary materials
must, at a minimum, contain the following information:
i)
The name of the transporter
and date of the shipment;
ii)
The name and address
of the facility that received
the excluded material,
along with documentation confirming
receipt of the shipment; and
iii)
The
type
and quantity of excluded
secondary material in
each shipment.
BOARD NOTE:
Subsections
(a) (20)
(G) (i)
through
(a) (20) (G) (iii)
are
derived from
40
CFR
261.4(a) (20) (ii) (D) (1)
through
(a) (20) (ii) (D) (3).
The Board
added the
preamble
to
these federal paragraphs
as subsection
(a) (20)
(G)
to comport with
Illinois Administrative
Code
codification
requirements.
21)
Zinc fertilizers made from hazardous
wastes or hazardous
secondary
materials that are excluded under
subsection
(a) (20)
of this
Section, provided
that the following conditions are fulfilled:
A)
The fertilizers meet the following
contaminant limits:
i)
For metal contaminants:
ConstituentMaximum
Allowable Total
Concentration
in
Fertilizer,
per Unit
(l%i
of
Zinc
(ppm)Arsenico
. 3Cadmiuml
.4Chromiumo
. 6Lead2 . SMercury0
.3
ii)
For dioxin
contaminants,
the fertilizer
must contain
no
more
than
eight
parts
per
trillion
of dioxin,
measured
as toxic equivalent
(TEQ)
B)
The manufacturer
performs sampling
and analysis
of the
fertilizer
product
to determine
compliance
with the contaminant
limits
for
metals no
less
frequently
than once every
six months,
and for dioxins
no less
frequently
than
once
every
12 months. Testing
must
also
be performed
whenever
changes occur
to
manufacturing
processes or ingredients
that
could significantly
affect the
amounts of
contaminants
in the fertilizer
product.
The
manufacturer
may
use any
reliable
analytical method
to demonstrate
that no
constituent of concern
is
present
in
the product at
concentrations
above the applicable
limits.
It is
the
responsibility
of the manufacturer
to ensure
that the
sampling
and analysis
are
unbiased,
precise,
and representative
of the
products
introduced
into commerce.
C)
The
manufacturer
maintains for
no less than
three
years
records
of all
sampling
and
analyses performed
for
purposes of determining
compliance
with
subsection
(a)
(21) (B)
of this
Section.
Such records
must
at a minimum include
the
following:
i)
The dates
and times
product
samples were taken,
and
the dates
the samples
were
analyzed;
ii)
The
names
and qualifications
of the persons
taking the
samples;
iii)
A
description of
the methods and
equipment
used
to
take the samples;
iv)
The
name
and address of
the laboratory
facility
at which
analyses
of
the
samples
were
performed;
v)
A description
of
the analytical methods
used,
including
any cleanup
and
sample preparation
methods;
and
vi)
All laboratory
analytical
results used
to
determine
compliance
with
the
contaminant
limits
specified in this
subsection
(a)
(21)
22)
Used
CRTs.
A)
Used,
intact
CRT5, as defined
in
35
Iii.
Adm.
Code 720.110, are
not
solid
waste within
the United
States, unless
they
are
disposed
of or speculatively
accumulated,
as defined
in Section 721.101(c)
(8),
by
a CRT
collector or
glass
processor.
B)
Used,
intact CRT5,
as defined
in 35 Ill. Adm.
Code 720.110, are
not
solid
waste
when exported
for recycling,
provided that they
meet the requirements
of
Section
721.140.
C)
Used,
broken
CRTs,
as
defined
in 35 Ill.
Adm. Code 720.110,
are not solid
waste,
provided that they
meet the requirements
of
Section
721.139.
D)
Glass
removed
from
CRT5
is not
a
solid waste
provided that
it meets
the
requirements
of Section
721.139(c).
b)
Solid
wastes that are
not hazardous
wastes. The following
solid wastes
are not
hazardous
wastes:
1)
Household waste,
including
household waste
that has been collected,
transported,
stored,
treated,
disposed of, recovered
(e.g., refuse-derived
fuel), or reused.
“Household
waste” means any waste
material (including
garbage, trash, and sanitary wastes in septic
tanks)
derived from households
(including
single
and multiple
residences, hotels,
and motels, bunkhouses,
ranger
stations,
crew
quarters, campgrounds,
picnic grounds, and
day-use
recreation
areas)
. A resource
recovery facility
managing municipal solid waste
must
not be deemed to be treating, storing, disposing
of, or otherwise managing
hazardous
wastes
for the
purposes of regulation
under this Part, if the
following describe
the
facility:
A)
The facility receives and burns only
the following waste:
i)
Household waste
(from
single and multiple
dwellings, hotels, motels,
and
other residential
sources)
;
or
ii)
Solid waste from
commercial or industrial
sources that does not contain
hazardous waste; and
B)
The facility
does
not
accept hazardous waste
and the owner or operator
of
such facility has established
contractual requirements
or other appropriate
notification or inspection
procedures to assure that hazardous
wastes are not
received
at
or burned in
such facility.
BOARD NOTE:
The
U.S. Supreme Court determined, in
City of Chicago v.
Environmental Defense Fund, Inc.,
511 U.S. 328, 114
5. Ct. 1588, 128 L. Ed. 2d
302
(1994),
that this exclusion
and RCRA section 3001(i)
(42
USC
6921(i))
do not
exclude the ash from facilities
covered by this
subsection
(b) (1)
from
regulation
as a
hazardous waste.
At 59 Fed. Reg. 29372
(June
7,
1994),
USEPA
granted facilities managing
ash from such facilities
that is determined a
hazardous
waste under
Subpart C of this Part until December
7, 1994 to file
a
Part A
permit application
pursuant to
35
Ill. Adm.
Code 703.181. At 60 Fed.
Reg. 6666
(Feb.
3,
1995),
USEPA stated that it interpreted
that the point
at
which ash becomes
subject to RCRA Subtitle C regulation
is when that material
leaves the combustion building
(including connected air
pollution control
equipment).
2)
Solid wastes generated
by
any
of the following that are returned
to the
soil as fertilizers:
A)
The growing and harvesting of agricultural
crops, or
B)
The raising of animals,
including animal manures.
3)
Mining overburden returned
to the mine site.
4)
Fly ash waste, bottom
ash waste, slag waste,
and flue gas emission control
waste
generated primarily from
the combustion of coal
or other fossil fuels,
except
as provided in
35
Ill.
Adm. Code 726.212 for facilities
that burn or
process
hazardous waste.
5)
Drilling fluids, produced
waters, and other wastes
associated with the
exploration, development, or
production of crude oil,
natural gas, or geothermal
energy.
6)
Chromium wastes.
A)
Wastes
that fail the test
for
the
toxicity characteristic
(Section
721.124
and
Appendix
B
to this Part)
because chromium
is present or
which are listed
in
Subpart D of
this
Part due
to
the
presence of
chromium, that do
not fail the
test for
the toxicity
characteristic
for any other
constituent or
which are
not
listed
due
to the presence
of any
other
constituent,
and that do not fail
the
test
for any
other characteristic,
if the
waste generator
shows the following:
i)
The
chromium
in the
waste is
exclusively
(or
nearly
exclusively)
trivalent
chromium;
ii)
The waste
is
generated
from an industrial
process that
uses
trivalent
chromium exclusively
(or
nearly
exclusively)
and the
process
does
not
generate
hexavalent
chromium; and
iii)
The
waste
is typically
and frequently
managed
in
non-oxidizing
environments.
B)
The following
are
specific wastes
that meet
the
standard in
subsection
(b)
(6) (A)
of
this Section
(so
long
as
they
do not
fail the
test
for the
toxicity
characteristic
for any
other
constituent and
do not
exhibit
any other
characteristic)
i)
Chrome
(blue)
trimmings generated
by the
following subcategories
of the
leather
tanning and finishing
industry:
hair
pulp/chrome
tan/retan/wet
finish,
hair
save/chrome
tan/retan/wet
finish, retan/wet
finish, no
beamhouse,
through-
the-blue,
and
shearling;
ii)
Chrome
(blue)
shavings generated
by
the
following
subcategories
of the
leather
tanning and finishing
industry:
hair pulp/chrome
tan/retan/wet
finish,
hair save/chrome
tan/retan/wet
finish, retan/wet
finish, no
beamhouse, through-
the-blue, and
shearling;
iii)
Buffing
dust generated
by
the
following subcategories
of the leather
tanning
and
finishing industry:
hair
pulp/chrome
tan/retan/wet
finish, hair
save/chrome
tan/retan/wet
finish,
retan/wet
finish, no beamhouse,
through-the-
blue;
iv)
Sewer
screenings generated
by
the
following
subcategories
of the
leather
tanning
and
finishing industry:
hair
pulp/chrome
tan/retan/wet
finish, hair
save/chrome
tan/retan/wet
finish,
retan/wet
finish, no
beamhouse,
through-the-
blue, and
shearling;
v)
Wastewater
treatment
sludges
generated
by the
following
subcategories
of
the
leather
tanning and finishing
industry:
hair pulp/chrome
tan/retan/wet
finish,
hair
save/chrome
tan/retan/wet
finish,
retan/wet finish,
no beamhouse,
through-the-blue,
and shearling;
vi)
Wastewater
treatment
sludges generated
by the
following
subcategories
of
the
leather
tanning and finishing
industry:
hair
pulp/chrome
tan/retan/wet
finish, hair
save/chrome
tan/retan/wet
finish,
and
through-the-blue;
vii)
Waste
scrap leather
from the leather
tanning industry,
the shoe
manufacturing
industry,
and
other leather
product manufacturing
industries;
and
viii)
Wastewater treatment
sludges
from the production
of titanium
dioxide
pigment
using chromium-bearing
ores
by the chloride
process.
7)
Solid
waste
from the extraction,
beneficiation,
and processing
of ores
and
minerals
(including coal,
phosphate
rock, and overburden
from the mining
of
uranium
ore),
except as provided
by
35 Ill. Adm.
Code
726.212 for
facilities
that
burn or
process hazardous
waste.
A)
For purposes
of this
subsection
(b) (7),
beneficiation of
ores and
minerals
is restricted
to
the
following
activities:
crushing;
grinding; washing;
dissolution;
crystallization;
filtration;
sorting; sizing;
drying; sintering;
pelletizing;
briquetting; calcining
to
remove water or carbon
dioxide;
roasting;
autoclaving
or
chlorination in
preparation
for
leaching
(except
where
the
roasting
(or
autoclaving
or
chlorination)
and
leaching
sequence
produces
a
final
or intermediate
product
that does
not undergo
further
beneficiation
or
processing);
gravity concentration;
magnetic
separation;
electrostatic
separation;
floatation;
ion exchange; solvent
extraction;
electrowinning;
precipitation;
amalgamation;
and heap, dump,
vat tank,
and
in situ
leaching.
B)
For
the
purposes
of this subsection
(b) (7),
solid
waste from
the
processing
of ores and
minerals includes
only
the
following
wastes
as generated:
i)
Slag
from
primary
copper
processing;
ii)
Slag
from primary
lead
processing;
iii)
Red and
brown muds from
bauxite refining;
iv)
Phosphogypsum
from phosphoric
acid production;
v)
Slag
from elemental
phosphorus
production;
vi)
Gasifier
ash from coal
gasification;
vii)
Process
wastewater
from
coal
gasification;
viii)
Calcium
sulfate wastewater
treatment
plant sludge
from primary
copper
processing;
ix)
Slag tailings
from
primary
copper processing;
x)
Fluorogypsum
from hydrofluoric
acid
production;
xi)
Process wastewater
from hydrofluoric
acid
production;
xii)
Air
pollution control
dust
or
sludge from iron
blast
furnaces;
xiii)
Iron blast
furnace
slag;
xiv)
Treated
residue from
roasting and
leaching
of
chrome
ore;
xv)
Process
wastewater
from
primary magnesium
processing by the
anhydrous
process;
xvi)
Process
wastewater from
phosphoric
acid production;
xvii)
Basic
oxygen
furnace and
open hearth furnace
air pollution
control
dust
or
sludge from
carbon steel
production;
xviii)
Basic
oxygen
furnace and
open hearth
furnace slag from
carbon steel
production;
xix)
Chloride
processing waste
solids
from titanium
tetrachioride
production;
and
xx)
Slag
from primary
zinc production.
C)
A
residue
derived from
co-processing
mineral processing
secondary
materials
with
normal beneficiation
raw materials
or
with
normal
mineral
processing
raw materials
remains excluded
under
this subsection
(b)
if the
following
conditions
are fulfilled:
i)
The owner
or
operator
processes
at
least
50
percent
by
weight
normal
beneficiation
raw materials
or normal
mineral processing
raw materials;
and
ii)
The owner
or operator
legitimately
reclaims the secondary
mineral
processing
materials.
8)
Cement
kiln
dust
waste,
except
as provided
by
35 Ill. Adm.
Code
726.212
for
facilities
that burn
or
process
hazardous waste.
9)
Solid
waste
that consists
of discarded
arsenical-treated
wood or wood
products that
fails
the
test
for the toxicity
characteristic for
hazardous
waste
codes
0004 through
D017
and which
is not
a
hazardous
waste for any
other
reason
if the
waste is
generated
by persons
that utilize
the
arsenical-treated
wood
and
wood
products
for these
materials!
intended
end
use.
10)
petroleum-contaminated
media and debris
that
fail the
test
for
the
toxicity
characteristic
of Section
721.124
(hazardous
waste
codes
0018
through
0043
only) and
which
are subject to
corrective action
regulations under
35 Ill.
Adm.
Code
731.
11)
This
subsection
(b)(ll)
corresponds with
40 CFR
261.4(b) (11),
which
expired
by
its
own terms
on January
25, 1993. This
statement maintains
structural
parity with USEPA
regulations.
12)
Used
chlorofluorocarbon
refrigerants
from totally
enclosed
heat transfer
equipment,
including
mobile air conditioning
systems,
mobile refrigeration,
and
commercial
and industrial
air conditioning
and
refrigeration
systems,
that
use
chiorofluorocarbons
as the
heat transfer
fluid in a
refrigeration
cycle,
provided
the
refrigerant is
reclaimed
for
further use.
13)
Non-terne plated
used oil filters
that are
not
mixed with
wastes listed in
Subpart 0 of
this Part,
if these oil filters
have
been gravity
hot-drained
using
one
of the
following methods:
A)
Puncturing
the filter anti-drain
back
valve or
the filter
dome end and
hot - draining;
B)
Hot-draining
and crushing;
C)
Dismantling
and
hot-draining;
or
D)
Any
other
equivalent hot-draining
method that
will
remove used oil.
14)
Used
oil re-refining distillation
bottoms
that
are
used as feedstock
to
manufacture asphalt
products.
15)
Leachate or gas
condensate
collected
from landfills
where certain
solid
wastes
have been
disposed
of, under the following
circumstances:
A)
The
following
conditions
must
be
fulfilled:
i)
The solid
wastes disposed
of would
meet one
or
more
of the listing
descriptions
for
the following
USEPA hazardous
waste numbers
that are generated
after the
effective
date listed
for the waste:
USEPA
Hazardous
Waste
NumbcrzLiotingNumbersListin
Effective
DateKl69,
1(170,
1(171, and
Kl72February
8,
19991(174 and Kl7SMay
7, 20011(176,
1(177,
and
Kl78May 20,
2002Kl8lAugust
23,
2005
ii)
The solid
wastes
described
in subsection
(b) (15)
(A)
(i)
of this
Section
were
disposed
of prior
to
the
effective
date of the
listing
(as
set forth
in
that
subsection);
iii)
The leachate
or
gas
condensate
does not
exhibit any characteristic
of
hazardous waste
nor is
derived
from
any other listed
hazardous
waste;
and
iv)
Discharge
of the leachate
or gas
condensate,
including
leachate or
gas
condensate
transferred
from the
landfill to
a POTW
by
truck,
rail, or dedicated
pipe, is subject
to
regulation
under section
307(b)
or 402 of the
federal Clean
Water Act.
B)
Leachate
or gas condensate
derived
from 1(169,
1(170, 1(171,
1(172, 1(176,
1(177, or
1(178 waste
will no longer
be
exempt
if it is
stored or managed
in
a
surface
impoundment
prior to discharge.
After February
26, 2007, leachate
or
gas
condensate derived
from 1(181 waste
will
no longer
be
exempt if it is
stored
or
managed
in a surface impoundment
prior
to
discharge. There
is one
exception:
if the
surface
impoundment is
used to temporarily
store leachate
or
gas
condensate in
response
to an emergency
situation
(e.g.,
shutdown of
wastewater
treatment
system),
provided the impoundment
has
a
double
liner, and provided
the
leachate
or gas condensate
is removed from
the impoundment
and continues
to be
managed
in
compliance with
the conditions
of
this
subsection
(b)
(15)
after
the
emergency
ends.
c)
Hazardous wastes
that are exempted
from
certain
regulations. A
hazardous
waste
that is generated
in a product or
raw material storage
tank,
a
product
or
raw
material
transport
vehicle
or vessel,
a
product or raw material
pipeline,
or
in a
manufacturing
process unit,
or an associated
non-waste-treatment
manufacturing
unit, is
not subject
to regulation
under 35 Ill. Adm.
Code
702,
703,
and 722
through
728 or to the
notification requirements
of section
3010 of
RCRA
until it
exits the
unit in which it
was generated,
unless the unit is
a
surface
impoundment,
or
unless
the hazardous
waste remains in
the unit more
than
90
days
after the
unit
ceases
to be operated for
manufacturing
or for storage
or
transportation
of product
or raw
materials.
d)
Samples.
1)
Except as
provided
in subsection
(d) (2)
of this
Section,
a
sample
of solid
waste
or
a
sample of water,
soil, or air
that
is
collected
for the sole
purpose
of
testing
to
determine
its
characteristics
or composition is
not
subject
to any
requirements
of this Part or
35
Iii.
Adm.
Code
702,
703,
and 722
through 728.
The sample qualifies
when it
fulfills one
of the
following conditions:
A)
The sample is being
transported
to
a laboratory for
the
purpose
of
testing;
B)
The sample
is being
transported back
to the
sample collector
after
testing;
C)
The sample
is being stored
by the sample collector
before
transport
to
a
laboratory
for testing;
D)
The sample
is being
stored in
a
laboratory
before
testing;
E)
The
sample is
being stored
in a laboratory
for testing
but before
it
is
returned to
the
sample
collector; or
F)
The sample is
being
stored temporarily
in the laboratory
after testing
for
a specific
purpose
(for
example,
until
conclusion of a court
case or enforcement
action where
further testing
of
the sample
may be necessary)
2)
In order
to qualify
for the exemption
in subsection
(d) (1) (A)
or
(d) (1) (B)
of
this Section, a
sample
collector shipping
samples
to a laboratory
and
a
laboratory
returning
samples
to a sample collector
must
do the
following:
A)
Comply
with
U.S.
Department of
Transportation
(USDOT),
U.S.
Postal Service
(USPS),
or any other applicable
shipping
requirements;
or
B)
Comply
with the following
requirements if
the sample
collector
determines
that USDOT, USPS,
or other shipping
requirements
do
not
apply
to the
shipment
of
the
sample:
i)
Assure
that the following
information
accompanies the
sample: The sample
collectorTs
name, mailing address,
and telephone
number; the laboratory
T
s name,
mailing address,
and telephone
number;
the quantity
of the
sample;
the date
of
the
shipment; and
a description of
the sample; and
ii)
Package
the sample
so
that
it
does not
leak, spill, or
vaporize from its
packaging.
3)
This exemption
does
not
apply if
the laboratory
determines that
the waste
is hazardous
but the laboratory
is no
longer
meeting any
of the conditions
stated in
subsection
(d) (1)
of this
Section.
e)
Treatability
study
samples.
1)
Except as is provided
in
subsection
(e) (2)
of this
Section,
a
person
that
generates
or
collects samples
for
the purpose
of conducting
treatability
studies,
as
defined
in 35
Ill. Adm.
Code
720.110,
are not subject
to
any
requirement
of
35
Ill.
Adm. Code 721 through
723
or to the notification
requirements
of section 3010
of the Resource
Conservation
and Recovery
Act.
Nor
are
such samples
included in
the quantity determinations
of Section
721.105
and
35
Ill. Adm. Code
722.134(d)
when:
A)
The sample is being
collected and
prepared for transportation
by
the
generator
or sample
collector;
B)
The
sample
is
being
accumulated
or
stored
by the
generator
or sample
collector
prior to
transportation
to a
laboratory
or
testing facility;
or
C)
The
sample is being
transported
to the laboratory
or
testing facility
for
the
purpose
of conducting a
treatability
study.
2)
The exemption
in subsection
(e) (1)
of this
Section
is
applicable
to
samples of
hazardous
waste being
collected and shipped
for
the
purpose
of
conducting
treatability studies
provided
that the following
conditions
are
fulfilled:
A)
The generator
or sample collector
uses
(in
“treatability
studiesT)
no more
than 10,000
kg of media
contaminated
with non-acute
hazardous
waste,
1,000 kg
of
non-acute
hazardous
waste
other
than
contaminated media,
1 kg of acute
hazardous
waste,
or 2,500
kg of media
contaminated
with
acute
hazardous
waste for each
process
being
evaluated for each
generated
waste stream;
B)
The mass
of each
shipment
does not exceed 10,000
kg;
the
10,000
kg
quantity
may be
all media
contaminated
with non-acute
hazardous
waste,
or may
include
2,500
kg of media contaminated
with acute hazardous
waste,
1,000
kg of
hazardous
waste,
and 1 kg of acute
hazardous
waste;
C)
The
sample must
be packaged
so
that
it does
not
leak,
spill, or vaporize
from
its
packaging during
shipment and the
requirements of
subsection
(e) (2) (C)
Ci)
or
(e) (2) (C) (ii)
of this Section
are met.
i)
The
transportation
of each sample
shipment complies
with
U.S.
Department
of
Transportation
(USDOT),
U.S. Postal
Service
CUSPS),
or
any other applicable
shipping
requirements; or
ii)
If
the
USDOT,
USPS, or other
shipping requirements
do not apply
to the
shipment of
the sample,
the following
information must
accompany the sample:
The name,
mailing address,
and telephone
number
of
the originator
of the
sample;
the
name,
address, and telephone
number of
the facility that
will perform
the
treatability
study; the quantity
of the sample;
the date of the
shipment; and,
a
description
of the
sample, including
its USEPA hazardous
waste number;
D)
The
sample
is shipped
to a laboratory
or testing
facility
that is exempt
under subsection
(f)
of this
Section, or has
an
appropriate
RCRA
permit or
interim
status;
E)
The
generator or sample
collector
maintains the
following
records for
a
period
ending
three years after
completion
of the
treatability
study:
i)
Copies
of the
shipping documents;
ii)
A copy
of the contract
with the facility
conducting the
treatability
study;
and
iii)
Documentation
showing the following:
The amount
of waste shipped
under
this
exemption;
the
name,
address, and
USEPA identification
number of the
laboratory
or
testing
facility
that received
the waste; the
date the shipment
was
made; and
whether
or not
unused samples and
residues
were
returned
to the
generator;
and
F)
The
generator
reports the
information
required
in subsection
Ce)
(2) CE)
(iii)
of this Section in
its report
under 35
Ill. Adm.
Code
722.141.
3)
The
Agency
may grant requests
on a case-by-case
basis for
up to an
additional
two years
for treatability
studies
involving
bioremediation.
The
Agency may
grant requests,
on a
case-by-case basis,
for quantity limits
in
excess of those
specified
in
subsections
(e) (2) (A) , (e) (2)
(B)
, and
(f) (4)
of
this
Section,
for
up
to an
additional 5,000
kg of media
contaminated with
non-
acute hazardous
waste,
500
kg of non-acute
hazardous
waste,
2,500 kg of media
contaminated
with
acute hazardous
waste, and 1
kg of acute hazardous
waste under
the
circumstances set
forth in
either
subsection
(e)
(3)
(A)
or
(e) (3) (B)
of this
Section, subject to
the limitations
of subsection
(e)
(3)
(C)
of
this Section:
A)
In
response
to requests for
authorization
to ship,
store,
and conduct
further
treatability
studies on
additional quantities
in advance
of commencing
treatability
studies.
Factors
to
be considered in
reviewing such
requests
include
the nature of the
technology,
the type of process
(e.g.,
batch
versus
continuous),
the size of the
unit
undergoing
testing
(particularly
in relation
to scale-up
considerations),
the
time or quantity
of
material required
to reach
steady-state
operating
conditions,
or
test design
considerations,
such
as mass
balance
calculations.
B)
In
response
to requests
for
authorization
to ship,
store,
and
conduct
treatability
studies
on additional
quantities
after
initiation or
completion
of
initial
treatability
studies when
the following
occurs:
There has
been an
equipment or
mechanical
failure
during the conduct
of
the
treatability
study,
there
is need
to verify the
results
of a previously-conducted
treatability
study,
there
is a need
to study
and
analyze
alternative
techniques
within
a
previously-evaluated
treatment process,
or
there is a
need
to
do
further
evaluation
of an ongoing
treatability
study to
determine
final specifications
for
treatment.
C)
The
additional
quantities
allowed
and timeframes
allowed
in
subsections
(e) (3) (A)
and
(e) (3)
(B)
of this
Section are
subject
to all the provisions
in
subsections
(e) (1)
and
(e) (2) (B)
through
(e)
(2) (F)
of
this Section. The
generator or
sample collector
must apply
to
the
Agency
and
provide in writing
the
following
information:
1)
The
reason
why the generator
or sample
collector
requires additional
time
or quantity
of sample
for the treatability
study
evaluation
and the additional
time
or quantity
needed;
ii)
Documentation
accounting
for all samples
of hazardous
waste
from the waste
stream that
have
been sent for or
undergone treatability
studies, including
the
date
each
previous
sample from the
waste stream was shipped,
the quantity
of
each
previous
shipment,
the laboratory
or testing facility
to which it was
shipped,
what
treatability
study processes
were conducted on
each sample
shipped,
and
the available
results
of each treatability
study;
iii)
A
description of the
technical
modifications or
change
in
specifications
that
will be
evaluated and the
expected
results;
iv)
If
such further
study is being
required
due to
equipment or mechanical
failure, the
applicant
must include information
regarding
the reason for
the
failure
or
breakdown and
also include what
procedures
or equipment
improvements
have
been made
to
protect
against
further breakdowns;
and
v)
Such other
information
as the
Agency determines
is necessary.
4)
Final Agency
determinations
pursuant
to
this
subsection
(e)
may
be
appealed
to
the
Board.
f)
Samples
undergoing
treatability
studies
at
laboratories or
testing
facilities.
Samples
undergoing
treatability
studies
and the laboratory
or
testing facility
conducting
such treatability
studies
(to
the extent
such
facilities
are not otherwise
subject to
RCRA requirements)
are not
subject to
any requirement
of this Part,
or of 35 Ill.
Adm.
Code
702,
703, 722 through
726,
and 728 or
to
the
notification
requirements of
Section 3010 of
the Resource
Conservation
and Recovery
Act,
provided
that the
requirements of subsections
(f) (1)
through
(f) (11)
of
this Section
are met.
A
mobile
treatment unit
may
qualify
as a
testing
facility subject
to subsections
(f) (1)
through
(f)
(11)
of
this Section.
Where
a
group
of mobile treatment
units are
located
at
the
same
site, the
limitations
specified
in subsections
(f) (1)
through
(f) (11)
of
this
Section apply
to
the
entire
group
of mobile
treatment
units collectively
as if
the
group
were
one
mobile
treatment
unit.
1)
No
less
than
45
days
before conducting
treatability studies,
the
facility
notifies the
Agency
in writing
that it intends
to
conduct treatability
studies
under this subsection
(f)
2)
The
laboratory
or
testing facility
conducting the
treatability
study has a
USEPA
identification
number.
3)
No
more than a total
of 10,000
kg of “as received”
media contaminated
with
non-acute
hazardous waste,
2,500
kg
of media contaminated
with acute hazardous
waste,
or
250
kg of other
“as
received”
hazardous waste
is subject to initiation
of treatment
in
all treatability
studies in
any single day.
“As received”
waste
refers to
the waste
as received in
the shipment
from
the
generator
or sample
collector.
4)
The
quantity
of “as received”
hazardous
waste stored
at the facility
for
the purpose
of
evaluation in treatability
studies does
not
exceed
10,000 kg,
the
total of
which can
include 10,000 kg
of media
contaminated
with
non-acute
hazardous
waste, 2,500
kg of media
contaminated with
acute
hazardous
waste,
1,000
kg
of non-acute hazardous
wastes other
than
contaminated
media,
and 1 kg
of acute
hazardous
waste.
This
quantity limitation
does not include
treatment
materials
(including
non-hazardous
solid
waste)
added
to “as received”
hazardous
waste.
5)
No
more
than
90 days
have elapsed since
the treatability
study
for
the
sample was
completed,
or
no more
than one year
(two
years for treatability
studies
involving
bioremediation)
has elapsed since
the generator or
sample
collector
shipped the sample
to the
laboratory or testing
facility, whichever
date
first
occurs.
Up
to 500 kg of treated
material from
a particular waste
stream from
treatability
studies may be archived
for future
evaluation
up to
five years
from the
date
of initial
receipt.
Quantities of materials
archived
are counted
against the
total
storage
limit for the
facility.
6)
The
treatability
study does not involve
the placement
of hazardous waste
on the land
or
open burning of
hazardous waste.
7)
The
facility maintains
records for
three years
following
completion
of
each
study
that
show
compliance
with the
treatment
rate limits
and the
storage
time and
quantity
limits.
The
following
specific
information must
be
included
for each
treatability
study conducted:
A)
The name, address,
and USEPA
identification
number of the generator or
sample collector of
each waste
sample;
B)
The date the
shipment was
received;
C)
The quantity of
waste
accepted;
D)
The quantity of ‘as
receivedlT
waste in storage each
day;
E)
The date the treatment study was initiated
and the amount of “as received”
waste introduced to treatment each day;
F)
The date the treatability study was concluded;
G)
The date any unused
sample
or residues generated from the treatability
study were
returned
to the generator or sample collector or, if sent
to a
designated
facility, the name of
the facility and the USEPA identification
number.
8)
The
facility keeps, on-site,
a copy of the treatability
study contract and
all shipping
papers associated with
the transport of treatability
study samples
to and
from the facility for
a
period
ending three years from the completion
date of
each treatability
study.
9)
The
facility prepares and
submits a report to the Agency,
by
March
15 of
each year,
that includes the
following information for the previous calendar
year:
A)
The name, address, and USEPA
identification number of the facility
conducting the treatability studies;
B)
The
types (by
process) of treatability
studies conducted;
C)
The names and addresses of persons
for whom studies have been conducted
(including their USEPA identification
numbers);
U)
The total quantity of waste
in storage each day;
E)
The quantity and
types
of waste
subjected to treatability studies;
F)
When each treatability
study
was
conducted; and
G)
The final disposition of residues
and unused sample from each treatability
study.
10)
The facility determines whether any unused sample or residues
generated
by
the
treatability
study are hazardous waste under Section 721.103 and, if
so, are
subject to 35
Ill. Adm.
Code 702, 703, and 721 through 728, unless
the residues
and unused
samples are returned
to the sample originator under the exemption
of
subsection
Ce)
of this
Section.
11)
The facility notifies the Agency
by letter when the facility is no longer
planning to conduct any treatability studies
at the site.
g)
Dredged material that is not
a
hazardous waste.
Dredged material that
is
subject to the requirements of a permit that has
been issued under section 404
of the Federal
Water
Pollution Control Act
(33
USC
1344)
is not a hazardous
waste. For the purposes of this
subsection (g), the following definitions
apply:
‘Dredged
material
has the meaning
ascribed it in 40 CFR 232.2
(Definitions),
incorporated by reference
in 35 Ill. Adm. Code
720.111(b).
“Permit” means any of the following:
A permit issued by the U.S. Army Corps
of Engineers (Army Corps) under
section 404 of the Federal Water Pollution Control
Act
(33
USC 1344);
A permit issued by the Army Corps under
section 103 of the Marine
Protection, Research, and Sanctuaries Act
of 1972
(33
USC 1413); or
In the case of Army Corps civil works
projects, the administrative
equivalent of the permits referred
to
in
the preceding two paragraphs of this
definition, as provided for in Army Corps regulations
(for
example,
see 33 CFR
336.1, 336.2, and
337.6)
(Source:
Amended at 33 Ill. Reg.
—,
effective
SUBPART C:
CHARACTERISTICS
OF HAZARDOUS WASTE
Section 721.123
Characteristic of Reactivity
a)
A solid waste
exhibits
the characteristic of reactivity
if a
representative sample
of the waste has any of the following
properties:
1)
It is
normally
unstable and readily undergoes violent
change without
detonating.
2)
It reacts
violently
with water.
3)
It forms
potentially
explosive mixtures with water.
4)
When
mixed with water,
it generates toxic gases, vapors, or fumes in
a
quantity
sufficient
to present a danger to human health or the environment.
5)
It
is
a
cyanide
or sulfide bearing waste which, when exposed
to
pH
conditions between 2 and 12.5 can
generate toxic gases, vapors, or fumes
in a
quantity sufficient
to
present
a
danger
to human health or the environment.
6)
It is capable of detonation or explosive
reaction if it is subjected
to a
strong initiating source or if heated under confinement.
7)
It is
readily
capable of detonation or explosive
decomposition or reaction
at standard
temperature
and pressure.
8)
It is
a
forbidden
explosive, as defined in federal 49
CFR 173.54
(Forbidden Explosives)
or a Division 1.1, 1.2, or 1.3 explosive,
as defined in
49
CFR 173.50
(Class
1
-—Definitions),
each incorporated
by
reference
in 35
Ill. Adm.
Code
720.111(b).
BOARD NOTE: Corresponding 40
CFR 261.23 cites to 49 CFR 173.51 for
a definition
of
“forbidden explosive,”
to
49
CFR 173.53 for a definition of “Class A
explosive,” and to 49 CFR 173.88
for a definition of “Class B explosive.”
49
CFR 173.54 now sets forth the
definition of “forbidden explosive,” and 49
CFR
173.53
explains that
what were once
Class A explosives
and Class
B explosives
are
now classified
as
Division 1.1, Division
1.2,
and Division 1.3
materials.
The Board
has updated
the
Illinois provision
to correspond
with the current
USDOT regulations.
b)
A
solid waste
that exhibits the
characteristic
of reactivity
has
the
USEPA
hazardous
waste number
of D003.
(Source:
Amended at
33 Iii.
Reg.
—,
effective
SUBPART
U:
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 of
this Part.
USEPA Hazardous
Waste No.Industry
and Hazardous
WasteHazard CodeFOOlThe
following
spent
halogenated solvents
used in degreasing:
tetrachloroethylene,
trichioroethylene,
methylene chloride,
1,1, 1-trichloroethane,
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.
(T)FOO2The
following
spent
halogenated
solvents: tetrachloroethylene,
methylene
chloride,
trichioroethylene,
1,1, 1-trichioroethane,
chlorobenzene,
1,1,2-
trichloro-1,
2, 2-trifluoroethane,
orthodichlorobenzene,
trichiorofluoromethane,
and
1,1,2-trichioroethane;
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.
(T)FOO3The
following
spent
non-halogenated
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.
(I)FOO4The following
spent
non-halogenated
solvents:
cresols
and
cresylic
acid
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.
(T)FOO5The following
spent
non-halogenated
solvents: toluene,
methyl
ethyl
ketone,
carbon disulfide,
isobutanol,
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.
(I,
T)FoO6Wastewater
treatment
sludges
from 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.
(T)FOO7Spent cyanide
plating
bath solutions from electroplating operations.
CR,
T)FOO8Plating
bath residues
from the bottom of plating baths from
electroplating
operations where
cyanides
are
used in the process.
CR,
T)FoO9Spent
stripping and cleaning bath
solutions from electroplating
operations where
cyanides are
used in the process.
CR,
T)FoloQuenching
bath residues
from oil baths from metal heat-treating
operations where
cyanides
are used in the process.
CR,
T)FOllSpent
cyanide solutions
from salt bath pot cleaning from metal heat-
treating
operations.
CR,
T)Fol2Quenching wastewater treatment
sludges from metal heat-treating
operations
where cyanides are
used in the process.
CT)Fol9Wastewater treatment sludges from
the chemical conversion coating of
aluminum except
from zirconium phosphating
in aluminum can washing when
such
phosphating is
an exclusive conversion
coating process.
J,Wastewater
treatment
sludge from the manufacturing of motor vehicles
using a
zinc phosphating
process will
not be subject to this listing at the point
of
generation if
the waste
is not
placed
outside on the land prior to shipment
to a
landfill for
disposal and it is
disposed of in a regulated landfill that
fulfills
either of the following
conditions:
It is located
in Illinois,
and it is one of the following types of landfills:
It is a
landfill that is
a
hazardous
waste management unit, as defined in
35
Ill. Adm. Code
720.110;
It is a
municipal solid waste landfill,
as defined in 35 Ill. Adm. Code
810.103;
or
It is a
putrescible or chemical waste landfill
that is subject to the
requirements of Subpart
C
of 35 Iii. Adm.
Code 811.
It is
located outside Illinois, and it is one
of the following types of
landfills:
It is
a
RCRA Subtitle D municipal solid waste or industrial solid waste
landfill
unit that is equipped with a single clay liner and which is permitted,
licensed
or otherwise authorized by the state; or
It is a landfill
unit
that is subject to or which otherwise meets the landfill
requirements in 40 CFR 258.40, 264.301 or 265.301.
For the purposes
of
this hazardous waste listing, ‘motor vehicle manufacturing”
is defined in subsection
(b) (4) (A)
of this Section, and subsection
(b) (4)
(B)
of
this Section describes the recordkeeping requirements for motor vehicle
manufacturing
facilities.+T-)-
FO2OWastes (except
wastewater
and spent carbon from hydrogen chloride
purification) from the production or manufacturing use
(as
a
reactant, chemical
intermediate or component in a formulating process) of tn- or tetrachlorophenol
or of intermediates used to produce their pesticide derivatives.
(This
listing
does not include wastes from the production of hexachlorophene from highly
purified
2,4, 5-trichlorophenol.)
CI-I)FO2lWastes (except wastewater and spent
carbon from hydrogen chloride
purification) from the production or manufacturing
use
(as
a reactant, chemical
intermediate or component in
a
formulating
process) of pentachiorophenol or
of
intermediates used to produce its derivatives.
CH)FO22Wastes
(except wastewater and spent 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.
(H)FO23Wastes (except wastewater
and spent carbon from hydrogen chloride
purification) from the production of
materials on equipment previously used
for
the
production or manufacturing
use
(as
a reactant, chemical intermediate
or
component in
a
formulating process) of
tn- and tetrachlorophenols.
(This
listing
does
not
include wastes
from equipment
used
only for
the production
or
use of hexachlorophene
from highly
purified 2,4,5-trichlorophenol.)
(H)FO24Process
wastes,
including
but not 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 in Section
721.132-)
(T)FO25Condensed
light ends,
spent filters
and filter aids,
and spent desiccant
wastes from
the
production
of
certain chlorinated
aliphatic hydrocarbons
by free
radical catalyzed
processes.
These
chlorinated aliphatic
hydrocarbons
are
those
having
carbon chain
lengths
ranging
from one
to
and
including five, with
varying
amounts and
positions
of chlorine substitution.
(T)FO26Wastes
(except
wastewater
and spent
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.
(H)FO27Discarded
unused formulations
containing
tn-,
tetra-
or
pentachlorophenol
or discarded unused
formulations
containing compounds
derived
from these
chiorophenols.
(This
listing
does not
include
formulations
containing
hexachlorophene
synthesized
from prepurified
2,4,5-trichlorophenol
as
the
sole
component.)
(H)FO28Residues
resulting from the
incineration
or
thermal treatment
of soil
contaminated
with
hazardous waste
numbers F020,
F02l,
F022,
F023,
F026, and
F027.
(T)FO32Wastewaters
(except
those
that
have not come
into
contact with
process
contaminants),
process residuals,
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
chlorophenolic
formulations)
. This listing
does not
include
KOOl bottom
sediment
sludge
from the treatment
of wastewater
from
wood
preserving
processes
that use
creosote
or pentachlorophenol.-(--)
FO34Wastewaters
(except
those that have
not
come
into
contact
with
process
contaminants)
, process residuals,
preservative
drippage, and
spent
formulations
from
wood
preserving
processes
generated
at
plants
that use creosote
formulations.
This
listing does
not include KOOl
bottom sediment
sludge from
the
treatment
of wastewater
from wood
preserving processes
that use creosote
or
pentachlorophenol.
(T)FO35Wastewaters,
(except
those that have
not come
into
contact
with process
contaminants)
, process
residuals,
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.
(T)Fo37petroleum
refinery
primary
oil/water/solids
separation sludge
- any
sludge
generated
from
the gravitational
separation
of oil/water/solids
during
the
storage
or treatment
of process
wastewaters and oily
cooling wastewaters
from
petroleum
refineries.
Such sludges
include,
but
are
not limited to,
those
generated
in:
oil/water/solids
separators;
tanks and
impoundments;
ditches and
other
conveyances;
sumps; and
stormwater units
receiving
dry
weather
flow.
Sludge
generated in stormwater
units
that do not
receive
dry
weather
flow,
sludge
generated
from non-contact
once-through
cooling
Iwaters
segregated
for
treatment from
other
process or
oily
cooling
waters,
sludge generated
in
aggressive
biological
treatment
units as defined
in subsection
(b)
(2)
of this
Section
(including sludge
generated
in one or more
additional units
after
wastewaters
have been treated
in
aggressive
biological
treatment
units)
, and
1(051
wastes
are not included
in
this listing.
This
listing
does include
residuals
generated
from processing
or recycling
oil-bearing
hazardous
secondary
materials
excluded
under Section
721.104
(a) (12) (A)
if
those residuals
are to
be
disposed
of.-(--)
Fo38Petroleum
refinery
secondary
(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
limited
to,
all
sludges
and
floats
generated
in
the following
types
of
units:
induced
air floatation
(IAF) units,
tanks
and
impoundments,
and all
sludges generated
in dissolved
air
flotation
(DAF)
units.
Sludges
generated in stormwater
units that
do
not
receive dry
weather flow,
sludges
generated from
non-contact once-through
cooling
waters
segregated
for treatment
from
other
process
or oily cooling
waters,
sludges
and floats
generated in
aggressive biological
treatment units
as
defined
in
subsection
(b) (2)
of this Section
(including
sludges
and floats
generated in
one or
more
additional
units after
wastewaters have
been treated
in
aggressive
biological
treatment
units),
F037, 1(048,
and 1(051 wastes
are not
included
in
this listing.
(T)Fo39Leachate
(liquids
that have percolated
through
land
disposed wastes)
resulting
from the disposal
of more than one
restricted waste
classified
as
hazardous
under
Subpart ID.
(Leachate
resulting
from
the disposal
of one
or
more
of the
following
USEPA hazardous
wastes and no
other
hazardous wastes
[Ml]
retains its
USEPA
hazardous waste
number(s)
:
F020,
F021,
F022, F026,
F027,
or
F028.)
(T)
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.
“(I, T)”
should
be used to
specify mixtures
that are
ignitable and contain
toxic constituents.
b)
Listing-specific
definitions.
1)
For
the purpose
of the F037 and F038
listings,
oil/water/solids
is
defined
as
oil or water or
solids.
2)
For
the purposes
of the F037
and F038
listings,
the following
apply:
A)
‘Aggressive biological
treatment
units”
are
defined
as
units that
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.
“Highrate
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
the
following
is
true:
i)
The
units
employ a minimum
of six horsepower
per
million gallons
of
treatment
volume;
and
either
ii)
The
hydraulic
retention
time of the unit
is no longer
than five 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 must
maintain,
in
their operating
or other
on site
records, documents
and data sufficient
to prove
the following:
i)
The
unit
is an aggressive
biological
treatment unit, as
defined in this
subsection;
and
ii)
The sludges
sought
to be exempted
from F037
or
F038 were actually
generated
in
the aggressive
biological
treatment
unit.
3)
Time
of
generation.
For
the purposes
of the
designated waste,
the
time
of generation
is defined as follows:
A)
For
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)
For 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.
4)
For the
purposes
of the F0l9
hazardous waste
listing,
the following
apply
to
wastewater
treatment sludges
from
the manufacturing
of motor
vehicles
using a
zinc
phosphating
process:
A)
‘Motor
vehicle
manufacturing”
is
defined
to
include the manufacture
of
automobiles
and light
trucks or utility
vehicles
(including light duty
vans,
pick-up
trucks,
minivans,
and sport
utility
vehicles)
. A faciliy owner
or
operator
must
be engaged in
manufacturing
complete vehicles
(body and chassis
or
unibody)
or
chassis
only; and
B)
The
generator must
maintain in its
on-site
records
documentation
and
information
sufficient to
prove that the wastewater
treatment
sludge
to
be
exempted
from
the F019 listing
meets the
conditions
of the listing.
These
records
must
include
the following
information:
the
volumes of waste
generated
and disposed
of off
site; documentation
showing when
the waste volumes
were
generated
and
sent
off
site; the name and
address
of
the
receiving facility;
and
documentation
confirming
receipt of the waste
by the
receiving
facility.
The
generator must
maintain
these
documents on site
for no less than
three years.
The
retention period for
the
documentation
is automatically
extended
during
the
pendency
of
any enforcement
action
or as requested
by
USEPA or by the
Agency
in
writing.
(Source:
Amended
at 33 Ill. Reg.
,
effective
Section
721.133
Discarded
Commercial
Chemical Products,
Off-Specification
Species,
Container
Residues,
and
Spill
Residues Thereof
The
following
materials
or items are
hazardous
wastes
if and when
they are
discarded
or
intended
to be discarded,
as described
in Section
721.102
(a) (2)
(A);
when they are mixed with
waste
oil or used oil
or other material and
applied to
the land for
dust
suppression or road treatment;
when they are otherwise
applied
to the land
in lieu of their original intended
use or when they are contained
in
products
that
are applied to land in lieu
of their original intended
use; or
when,
in lieu of
their original intended
use, they are produced for
use as
(or
as a component
of)
a
fuel, distributed
for use
as a
fuel, or burned
as a fuel.
a)
Any
commercial chemical product
or manufacturing chemical intermediate
having the generic
name listed in
subsection
(e)
or
(f)
of this Section.
b)
Any
off-specification commercial
chemical product or manufacturing
chemical
intermediate that, if
it met specifications, would have the
generic
name
listed
in subsection
(e)
or
(f)
of this Section.
c)
Any residue remaining in
a
container
or inner liner removed from
a
container that has held any commercial chemical
product or manufacturing
chemical intermediate having the generic name
listed in subsection
(e)
or (f)
of
this Section, unless the container is empty,
as defined in Section
721.107(b) (3).
BOARD NOTE: Unless the residue is being beneficially
used or reused;
legitimately recycled or reclaimed; or accumulated,
stored, transported, or
treated prior to such use, reuse, recycling,
or reclamation, the Board considers
the residue
to
be intended for discard, and
thus a hazardous waste. An example
of a
legitimate reuse of the residue
would be where the residue remains in
the
container and the container is
used to hold the same commercial chemical
product
or
manufacturing chemical intermediate
it previously held. An example of
the
discard of the residue would
be
where
the drum is sent to
a
drum reconditioner
that
reconditions the drum
but
discards
the residue.
d)
Any residue or contaminated soil,
water, or other debris resulting from
the cleanup of
a
spill into or on any land
or water of any commercial chemical
product or manufacturing chemical intermediate having
the generic name listed
in
subsection
(e)
or
(f)
of this Section or any residue
or contaminated soil,
water, or other debris resulting from the cleanup of
a spill into or on any land
or water of any off-specification chemical product or manufacturing
chemical
intermediate that, if it met
specifications, would have the generic name
listed
in
subsection
(e)
or
(f)
of this
Section.
BOARD NOTE: The phrase
ITcommercial
chemical product or manufacturing chemical
intermediate having the generic
name listed in .
..“
refers
to a
chemical
substance that is manufactured
or formulated for commercial or manufacturing
use
that
consists of the commercially
pure grade of the chemical, any technical
grades
of the chemical
that are produced or marketed, and all formulations
in
which the chemical is the
sole active ingredient. It
does
not refer
to a
material, such
as a
manufacturing
process waste, that contains any of
the
substances listed in
subsection
(e)
or
(f)
of this Section. Where
a
manufacturing process waste
is deemed to be a hazardous waste
because
it
contains
a
substance listed in
subsection
(e)
or
(f)
of this Section,
such waste
will be listed in either Sections 721.131
or 721.132 or will
be
identified
as a
hazardous waste by the characteristics
set forth in Subpart C of this Part.
e)
The commercial chemical products, manufacturing
chemical intermediates, or
off-specification commercial
chemical products or manufacturing
chemical
intermediates referred
to in subsections
(a)
through
(d)
of this
Section are
identified as acute hazardous
waste
(H)
and are subject
to
the small
quantity
exclusion defined in Section 721.105(e). These
wastes and their corresponding
USEPA hazardous waste numbers are the following:
BOARD NOTE: For the convenience of the regulated
community, the primary
hazardous properties
of
these materials have been
indicated by the letters T
(Toxicity), and R (Reactivity) . The absence of
a letter indicates that the
compound is only
listed for
acute toxicity. Wastes are first
listed in
alphabetical order by substance and then listed again in numerical
order by
USEPA hazardous waste number.
Alphabetical Listing
USEPA Hazardous Waste No.Chemical Ahstracts No.
(CAS
NojSubotancc
PSubstancePO23lO7-20-OAcetaldehyde,
chloro-P002591-08-2Acetamide,
N
(aminothioxomethyl) P057640-19-7Acetamide,
2-fluoro-P05862-74-8Acetic acid,
fluoro-, sodium
saltPOO259l-08-21-Acetyl-2-thioureaPoo3lo7-02-SAcroleinPO7Oll6-
06-3AldicarbP2O3l646-88-4Aldicarb sulfonePOO43O9-00-2AldrinPOO5lO7-18-6Allyl
alcoholPOO62O859-73-SAluminum phosphide
(R,
T)P0072763-96-45-(Aminomethyl)-3-
isoxazoloiPOO85O4-24-54-AminopyridinePoo9l3l-74-8Ammonium
picrate
(R)
P1197803-
55-6Ammonium vanadatePo995o6-6l-6Argentate(l-),
bis(cyano-C)-,
potassiumPolo7778-39-4Arsenic acid H3AsO4P0121327-53
-3Arsenic oxide
As2O3POlll3O3 -28-2Arsenic oxide As2O5P0l11303
-28-2Arsenic pentoxidePol2l327-53-
3Arsenic trioxidePo38692-42-2Arsine, diethyi-P036696-28-6Arsonous
dichloride,
phenyl-P054151-56-4AziridinePO6775-55-BAziridine,
2-methylPOl3542-62-iBarium
cyanidePo24lo6-47- 8Benzenamine, 4-chloro-P077100-
01-6Benzenamine, 4-nitro-
P028l00-44-7Benzene, (chloromethyl)-P04251-43-41,2-Benzenediol,
4-(l-hydroxy-2-
(methylamino)ethyi)
-, (R)
-P046122-09-8Benzeneethanamine,
?,
?-dimethyi-P014l08-
98-5BenzenethiolPl27l563-66-27-Benzofuranol,
2,3-dihydro-2,2-dimethyl-,
methylcarbamatePl88s7-64-7Benzoic
acid, 2-hydroxy-, compound with (3aS-cis)-
l,2,3,3a,8,8a-hexahydro-1,3a,8-trimethylpyrrolo(2,3-b)
indol-5-yi
methylcarbamate
ester
4-hydroxy-3-(3-
oxo-l-phenylbutyl)--, and salts, when present at concentrations greater
than 0.3
percentPo28loo-44
-7Benzyl
chloridePOl5744O-4i- 7Beryllium powderPOi7S9B-31-
2BromoacetonePol8357-57-3BrucinePO4539i96-l8-62-Butanone,
3,
3-dimethyl-l-
(methylthio) -, 0-
((methylamino)carbonyl)
oximePO2l592-0l-8Calcium
cyanidePo2l592-01-8Caicium cyanide
Ca(CN)2P18955285-14-8Carbamic
acid,
((dibutylamino) -thio)methyl-,
2, 3-dihydro-2, 2-dimethyl-7-benzofuranyl
esterPl9l644-64-4Carbamic
acid, dimethyl-,
1-C
(dimethyl-amino)carbonyl)
-5-
methyl-1H-pyrazol-3-yl
esterPl92ll9-38-OCarbamic acid, dimethyl-, 3-methyl-l-(l-
methylethyl) -1H-pyrazol-5-yl
esterPl9Oll29-41-SCarbamic acid, methyl-,
3-
methyiphenyl esterPl27l563
-66-2CarbofuranP02275-15-OCarbon disulfidePo9575-44-
5Carbonic
dichloridePi89S528S-14-8CarbosuifanPO23lO7-20-
OChloroacetaldehydePo24lo6-47-8p-ChloroanilinePo26s344
-82-li-
(o
Chlorophenyl)thioureaPo27542-76-73-ChloropropionitrilePo29544-92-3Copper
cyanidePO29544-92-3Copper cyanide CuCNP2O264-00-6m-Cumenyl
methyicarbamatePo3oCyanides
(soluble
cyanide
salts),
not otherwise
specifiedPo3l46o-19-5CyanogenPO335O6-77-4Cyanogen
chloridePO335O6-77-4Cyanogen
chloride CNC1PO34131-89-52-Cyclohexyl-4, 6-dinitrophenolPol6542-88-
lD±chloromethyl etherPO36696-28-6DichiorophenylarsinePo376o-57-lDieldrinPO38692-
42-2DiethylarsinePo4i3il-45-5Diethyl-p-nitrophenyi phosphatePo4o297-97-20,
0-
Diethyl
0-pyrazinyl
phosphorothioatePo4355-9l-4Diisopropylfluorophosphate
(DFP)Pl91644-64-4DimetilanPOO43O9-00-21,4,5,8-Dimethanonaphthalene,
i,2,3,4,lO,10-hexachloro-1,4,4a,5,8,8a-hexahydro-,
(i?,4?,4a?,5?,8?,8a?)-
P060465-73-61,4,5,8-Dimethanonaphthalene,
l,2,3,4,lO,l0-hexachioro-
l,4,4a,5,8,8a-hexahydro-,
(l?,4?,4a?,5?,8?,Sa?)-P03760-57-l2,7:3,6-
Dimethanonaphth(2,3-b)oxirene,
3,4,5,6,9,9-hexachloro-la,2,2a,3,6,6a,7,7a-
octahydro-,
(la?,2?,2a?,3?,6?,6a?,7?,7a?)_P05172_20_8*2,7:3,6_
Dimethanonaphth(2,3-b)oxirene,
3,4,5,6,9,
9-hexachloro-la,2,2a,3,6,6a,7,7a-
octahydro-,
(la?,2?,2a?,3?,6?,6a?,7?,7a?)-,
and metabolitesPO446O-51-
5DimethoatePO46l22-09-8?,
?Dimethy1phenethy1amineP047534521*4,
6-Dinitro-o-
cresol
and
saltsPO48Sl-28-52,
4-DinitrophenolPo2o88-85-7DinosebPOSSlS2-16-
9Diphosphoramide,
octamethyl-P111107-49-3Diphosphoric
acid, tetraethyl
esterPO39298-04-4DisulfotonPO4954l-53-7DithiobiuretPlBS2G4l9-73-81,3-Dithiolane-
2-carboxaldehyde,
2,4-dimethyl-,
0-
((methylamino) - carbonyl)oximePo5oll5-29-
7EndosulfanPOBBl4S-73-3EndothallPO5l72-20-
8EndrinPO5l72-20-SEndrin,
and
metabolitesP0425l-43
-4EpinephrinePo3l46o-
19-
5EthanedinitrilePl9423l35-22
-
OEthanimidothioic
acid,
2- (dimethylamino)
-N-
(C
(methylamino)carbonyl)oxy)
-2-oxo-
methyl esterP06616752-77-SEthanim±dothioic
acid, N
(((methylamino)carbonyl)oxy)
-, methyl
esterPlOllO7-l2-OEthyl
cyanidePC54l5l-56-
4EthyleniminePo9752-85-
7FamphurPO567782-41-4FluorinePO5764O-19-
7FluoroacetamideP05862-74-8Fluoroacetic
acid,
sodium
sa1tP19823422-53-
9Formetanate
hydrochloridePl97l77o2-57-7FormparanatePo6s628-86-4Fulminic
acid,
mercury
(2+)
salt
(R,
T)P05976-44-8HeptachlorPO62757-58-4Hexaethyl
tetraphosphatePll679-19-6HydrazinecarbothioamidePo686o-34-4Hydrazine,
methyl
P06374-90-8Hydrocyanic
acidPO6374-90-8Hydrogen
cyanidePO9678O3-51-2Hydrogen
phosphidePo6o465-73-6IsodrinPl92ll9-38-OIsolanP2O264-0O-63-Isopropylphenyl-N-
methylcarbamatePoo72763-96-43(2H)-Isoxazolone,
5-(am±nomethyl)-P19615339-36-
3Manganese,
bis(dimethylcarbamodithioato-S,S
)
-P196l5339-36-3Manganese
dimethyldithiocarbamatePo9262-38-4Mercury,
(acetato-0)phenyl-P065628-86-4Mercury
fulminate
(R,
T)
P08262-75-9Methanamine,
N-methyl-N-nitroso-P064624-83-9Methane,
isocyanato-P016542-88-lMethane,
oxybis(chloro-P112509-14-8Methane,
tetranitro
(R)
P11875-70-7Methanethiol,
trichloro-P19823422-53-9Methanimidamide,
N,N
dimethyl-N’
-(3-
( (
(methylamino)
-carbonyl)oxy)phenyl)-,
monohydrochloridePl97l7702-57-7Methanimidamide,
N,N-dimethyl-N’
- (2-methyl-4-
(Umethylamino)
carbonyl)oxy)phenyl)
-P1992032-65-7MethiocarbP0s0lls-29-76,
9-
Methano-2,4,3-benzodioxathiepen,
6,7,8,9,10,
10-hexachloro-l,5,5a,6,
9, 9a-
hexahydro-,
3-oxidePO5976-44-84,7-Methano-lH-indene,
l,4,5,6,7,8,8-heptachloro-
3a,4,7,7a-tetrahydro-P066l6752-77-SMethomylPO686O-34-4Methyl
hydrazineP064624—
83-9Methyl
isocyanatePo6975-86-52-MethyllactonitrilePo7l298-00-OMethyl
parathionPl9oll29-41-5MetolcarbPl29Pl283l5
8
NaphthylthioureaP073l3463-39-3Nickel
carbonylPO73l3463-39-3Nickel
carbonyl
Ni(C0)4,
(T-4)-P074557-19-7Nickel
cyanidePO74557-19-7N±ckel
cyanide
Ni(CN)2P07554_1l_5*Nicotine,
and saltsPO76lOlO2-43-9Nitric
oxidePO77lOO-0l-6p-
NitroanilinePO7BlOlO2-44-ONitrogen
dioxidePO76lOlO2-43-9Nitrogen
oxide
N0P07810102-44-ONitrogen
oxide
N02P08155-63-ONitroglycerine
CR)
P08262-75-9N-
NitrosodimethylaminePo844s49-40-ON-NitrosomethylvinylaminePO8sl52-16-
9octamethylpyrophosphoramidePo872o8l6-12-Oosmium
oxide
0s04,
(T-4)
-P08720816-12-
Oosmium
tetroxidePo88l45-73-37-Oxabicyclo(2.2.l)heptane-2,3-dicarboxylic
acidP19423l35-22
- OOxamylPO8956-38-2ParathionPO34l3l-89-SPhenol,
2-cyclohexyl-
4,
6-dinitro-P128315-18-4Phenol,
4-
(dimethylamino)-3,5-dimethyl-,
methylcarbamate
(ester)P1992032-65-7Phenol,
(3,5-dimethyl-4-(methylthio)-,
methylcarbamatePo485l-28-5Phenol,
2,4dinitroP04753452l*Pheno1,
2-methyl-4,6-
dinitro-,
and
saltsP2O264-00-6Phenol,
3-
(1-methylethyl)
-, methyl
carbamateP2ol263l-37-OPhenol,
3-methyl-5-
(1-methylethyl)-,
methyl
carbamatePo2o88-85-7Phenol,
2-(l-methylpropyl)-4,6-dinitro-P009l31-74-8Phenol,
2,4,6-trinitro-,
ammonium
salt (R)P09262-38-4Phenylmercury
acetatePO93lO3-85-
5PhenylthioureaPo9429a-02-2PhoratePO9575-44-5PhosgenePO9678O3-51-
2PhosphinePO4l3ll-45-5Phosphoric
acid, diethyl
4-nitrophenyl esterPO39298-04-
4Phosphorodithioic
acid, 0,0-diethyl
S-
(2-
(ethylthio)ethyl)
esterPO94298-02-
2Phosphorodithioic
acid, 0,0-diethyl
S- ((ethylthio)methyl)
esterPO446O-51-
SPhosphorodithioic
acid,
0,0-dimethyl S-
(2-
(methylamino)-2-oxoethyl)
esterPO4355-91-4Phosphorofluoridic
acid, bis
(l-methylethyl)esterPOB9S6-38-
2Phosphorothioic
acid,
0,0-diethyl
0- (4-nitrophenyl)
esterPO4O297-97-
2Phosphorothioic acid, 0,0-diethyl 0-pyrazinyl
esterPO9752-85-7Phosphorothioic
acid,
0-
(4—
(
(dimethylaminoLsulfonyl))
phenyl)
0,0-dimethyl esterPO7l298-OO-
OPhosphorothioic acid, 0,0-dimethyl
0-
(4-nitrophenyl)
esterP2O457-47-
6PhysostigminePl8857-64-7Physostigmine salicylatePllO78-OO-2Plumbane,
tetraethyl-P098151-5O-SPotassium cyanidePO98l5l-50-8Potassium
cyanide
KCNP099506-61-6Potassium silver cyanideP2Ol263l-37-
OPromecarbP2O3l64G-88-
4Propanal, 2-methyl-2- (methyl-sulfonyl)
-, 0- ((methylamino)carbonyl)
oximePO7Oll6-06-3Propanal, 2-methyl-2-(methylthio)-,
0-
((methylamino)carbonyl)oximePlOllO7-12-OPropanenitrilePO27s42-76-
7Propanenitrile, 3-chloro-P06975-86-5Propanenitrile, 2-hydroxy-2-methyl-P08155-
63-01,2,3-Propanetriol,
trinitrate- (R)P017598-31-22-Propanone, l-bromo-Pl02107-
l9-7Propargyl
alcoholPOO3lO7-02-82-PropenalPOO5lO7-18-62-Propen-l-olP06775-55-
81,2-PropyleniminePlo2lo7-19-72-Propyn-l-olP008504-24-54-Pyrid±naminePO7S54-ll-
5*Pyridine,
3-(l-methyl-2-pyrrolidinyl)-,
(S)-
and saltsP2O457-47-6Pyrrolo(2,3-
b)indol-5-ol,
l,2,3,3a,8,8a-hexahydro-l,3a,8-trimethyl-,
methylcarbamate
(ester), (3aS-cis)-P11412039-.52-OSelenious
acid, dithallium
(1+)
saltPl0363O-10-
4SelenoureaPlO45OE-64-9Silver cyanidePlO45O6-64 - 9Silver
cyanide AgCNP10526628-
22-8Sodium azidePlOGl43-33-9Sodium cyanidePlo6l43-33-9Sodium cyanide
NaCNP1O857-
249*Strychnidinl0one,
and saltsPOl8357-57-3Strychnidin-l0-one,
2,3-dimethoxy-
Pl0857249*Strychnine
and saltsPll57446-18-6Sulfuric
acid, dithallium
(1+)
saltPl093689-24-5TetraethyldithiopyrophosphatePllo78-
00-2Tetraethyl leadPllll07-
49-3TetraethylpyrophosphatePll25o9-l4-8Tetranitromethane
(R)P062757-58-
4Tetraphosphoric acid, hexaethyl esterPll3l3l4-32-5Thallic
oxidePll3l3l4-32-
5Thallium oxide T1203P11412039-52- OThallium
(I)
selenitePllS7446-18-EThallium
(I)
sulfatePlO93689-24-5Thiodiphosphoric acid, tetraethyl
esterP04539l96-18-
4ThiofanoxPO4954l-53-7Thioimidodicarbonic diamide
(
(H2N)C(S))
2NHPO141O8-98-
5ThiophenolPll679-l9-6ThiosemicarbazidePo265344-82-lThiourea,
(2-chlorophenyl)-
P07286-88-4Thiourea, l-naphthalenyl-P093l03-85-5Thiourea, phenyl-Pl23800l-35-
2ToxaphenePl85264l9-73-8TirpatePll875-70-7TrichloromethanethiolPll978o3-55-
6Vanadic acid, ammonium saltPl2Ol3l4-62-lVanadium oxide V205P1201314-62-
lVanadium pentoxidePo844549-40-OVinylamine, N-methyl-N-nitroso-P00l81-8l-
2*Warfarin,
and salts, when present at concentrations greater than
0.3
percentPl2l557-21-lZinc cyanidePl2lss7-21-lZinc cyanide
Zn(CN)2P205l37-30-4Zinc,
bis(dimethylcarbamodithioatoS,ST)Pl2213l4847Zinc
phosphide Zn3P2, when
present at concentrations greater than 10 percent
(R, T)P205l37-30-4Ziram
Numerical
Listing
USEPA Hazardous
Waste No.Chemical Abstracts
No.
(CAS No.)Substance
4-hydroxy-3-(3-oxo-l-phenylbutyl)-, and
salts, when
present
at
concentrations
greater than 0.3 percentPool8l-81-
2*Warfarin,
and salts,
when present
at concentrations greater than 0.3
percentPOO259l-08-2Acetamide, N- (aminothioxomethyl)
P002591-08-21-Acetyl-2-
thioureaPoo3lo7-02-8AcroleinPOO3lO7-02-82-PropenalPOO43O9-00-2AldrinPOO43O9-00-
2l,4,5,8-Dimethanonaphthalene,
l,2,3,4,10,l0-hexachloro-l,4,4a,5,8,8a-hexahydro-
(1?,4?,4a?,5?,8?,8a?)-P005107-18-6Allyl alcoholPOO5lO7-l8-62-Propen-l-
o1P00620859-73-BAluminum phosphide
(R,
T)P0072763-96-45-(Aminomethyl)-3-
isoxazololPOO72763-96-43(2H)-Isoxazolone,
5-(aminomethyl)-P008504-24-54-
AminopyridinePoo85o4-24-54-PyridinaminePoo9l3l-74-8Ammonium
picrate
(R)P009131-
74-8Phenol, 2,4,6-trinitro-, ammonium salt
(R)P0107778-39-4Arsenic
acid
H3As04P0111303 -28-2Arsenic oxide A5205P0111303 -28-2Arsenic
pentoxidePol2l327-53-
3Arsenic oxide As203P0l2l327-53-3Arsenic trioxidePol3542-62-lBarium
cyanidePol4los-98-5BenzenethiolPOl4lO8-98-5ThiophenolPOl5744O-4l-7Beryllium
powderPOl6542-88-l]Jichloromethyl etherPOl6542-88-lMethane, oxybis(chloro
P017598-31-2BromoacetonePol7598-3l-22-Propanone,
l-bromo-P018357-57-
3BrucinePOl8357-57-3Strychnidin-l0-one,
2, 3-dimethoxy-P02088-85-7DinosebPO2O88-
85-7Phenol, 2-(1-methylpropyl)-4,6-dinitro-P021592-01-BCalcium cyanidePo2l592-
0l-8Calcium
cyanide
Ca(CN)2P02275-15-OCarbon
disulfidePO23lO7-20-OAcetaldehyde,
chloro-P023l07-20-
OChloroacetaldehydePO24lO6-47-8Benzenamine,
4-chloro-P024106-
47-8p-ChloroanilinePO265344-82-ll-
(o-Chlorophenyl)
thioureaPO265344-82-lThiourea,
(2-chiorophenyl)
-P027542-76-73-ChloropropionitrilePO27542-76-7Propanenitrile,
3-
chloro-P028l00-44-7Benzene,
(chioromethyl) -P028100-44-7Benzyl
chloridePO29544-
92-3Copper
cyanidePO29544-92-3Copper
cyanide
CuCNPO3OCyanides
(soluble
cyanide
salts),
not
otherwise
specifiedPO3l46O-19-5CyanogenPO3l46O-19-
5EthanedinitrilePo335O6-77-4Cyanogen
chloridePO335OG-77-4Cyanogen
chloride
CNClPO34l3l-89-52-Cyclohexyl-4,
6-dinitrophenolPO34l3l-89-5Phenol,
2-cyclohexyl-
4,6-dinitro-P036696-28-6Arsonous
dichioride,
phenyl—P036696-28-
6DichlorophenylarsinePO376O-57-lDieldrinPO37GO-57-12,
7:3, 6-Dimethanonaphth(2,3-
b)oxirene,
3,4,5,6,9,9-hexachloro-la,2,2a,3,6,Ea,7,7a-octahydro-,
(la?,2?,2a?,3?,6?,Ga?,7?,7a?)-P038692-42-2Arsine,
diethyl-P038692-42-
2DiethylarsinePO39298-04-4DisulfotonPO39298-04-4Phosphorodithioic
acid,
0,0-
diethyl
S-
(2-
(ethylthio)ethyl)
esterPO4O297-97-20,0-Diethyl
0-pyrazinyl
phosphorothioatePo4o297-97-2Phosphorothioic
acid, 0,0-diethyl
0-pyrazinyl
esterPO4l3ll-45-
5Diethyl-p-nitrophenyl
phosphatePo4l3ll-45-5Phosphoric
acid,
diethyl
4-nitrophenyl
esterPO42Sl-43-4l,2-Benzenediol,
4-
(1-hydroxy-2-
(methylamino)
ethyl)
-, (R)
-P04251-43-4EpinephrinePo4355-91-
4Diisopropylfluorophosphate
(DFP)P04355-91-4Phosphorofluoridic
acid,
bis(1-
methylethyl)esterPO446O-51-5DimethoatePO446O-51-5Phosphorodithioic
acid,
0,0-
dimethyl
S-(2-(methylamino)-2-oxoethyl)
esterP04539l96-18-62-Butanone,
3,3-
dimethyl-l-
(methylthio)-,
0- ((methylamino)carbonyl)
oximePO4539l96-18-
4ThiofanoxPO4Gl22-09-8Benzeneethanamine,
?,?-dimethyl-P046l22-09-8?,?-
DimethylphenethylamineP047534521*4,
6-Dinitro-o-cresol
and sa1tsP047534-52-
1*Phenol,
2-methyl-4,6-dinitro-,
and saltsPO485l-28-52,4-DinitrophenolPo485l-28-
5Phenol,
2,4-dinitro-P049541-53-7Dithiobiuretp04954l-53-7Thioimidodicarbonic
diamide
((I-{2N)C(S))2NHPO5O115-29-7EndosulfanPO5Oll5-29-76,9-Methano-2,4,3-
benzodioxathiepen,
6,7,8,9,l0,l0-hexachloro-1,5,5a,6,9,9a-hexahydro-,
3-
oxideP05l72208*2,7:3,6Dimethanonaphth(2,3b)oxirene,
3,4,5,6,9,9-hexachloro-
la,2,2a,3,6,Ea,7,7a-octahydro-,
(la?,2?,2a?,3?,6?,6a?,7?,7a?)-,
and
metabolitesP05l72-20-BEndrinPOEl72-20-BEndrin,
and metabolitesPo54l5l-56-
4AziridinePO54l5l-
56-4EthyleniminePO5G7782-41-4FluorinePO5764O-
19- 7Acetamide,
2-
fluoro-P057640-l9-7FluoroacetamideP05862-74-BAcetic
acid, fluoro-,
sodium
saltP05862
- 74-BFluoroacetic
acid, sodium saltP05976-44-8HeptachlorPO5976-44-
84,7-Methano-1H-indene,
l,4,5,6,7,8,8-heptachloro-3a,4,7,7a-tetrahydro-P060465-
73-61,4,5,
8-Dimethanonaphthalene,
1,2,3,4,10,
10-hexachloro-l,4,4a,5,8,
8a-
hexahydro-,
(l?,4?,4a?,5?,8?,8a?)-P060465-73-6IsodrinPO62757-58-4Hexaethyl
tetraphosphatePo62757-58-4Tetraphosphoric
acid,
hexaethyl
esterPO6374-90-
8Hydrocyanic
acidPO6374-90-8Hydrogen
cyanidePO64G24-83-9Methane,
isocyanato
P064624-83-9Methyl
isocyanatePo65628-86-4Fulminic
acid,
mercury
(2+)
salt
(R,
T)P065628-86-4Mercury
fulminate
(R, T)P06616752-77-5Ethanimidothioic
acid,
N
(Umethylamino)carbonyl)oxy)-,
methyl esterP06616752-77-5MethomylPO6775-55-
SAziridine,
2-methylPO6775-55-81,
2-PropyleniminePo6s6o-34-4Hydrazine,
methyl
P06860-34-4Methyl
hydrazinePo6975-86-52-MethyllactonitrilePo6975-86-
5Propanenitrile,
2
-hydroxy-2-methyl-P0701l6-
06-3AldicarbPO7Oll6-06-3Propanal,
2-
methyl-2-
(methylthio)-, 0-
(
(methylamino)carbonyl)oximePO7l298-00-OMethyl
parathionPo7l298-00-OPhosphorothioic
acid, 0,0-dimethyl
0- (4-nitrophenyl)
esterPO7286-88-4?-NaphthylthioureaPo7286-88-4Thiourea,
1-naphthalenyl-P07313463-
39-3Nickel
carbonylP073l3463-39-3Nickel
carbonyl
Ni(C0)4,
(T-4)-P074557-19-
7Nickel
cyanidePO74SS7-19-7Nickel
cyanide
Ni(CN)2P07554115*Nicotine,
and
saltsP0755411_5*Pyridine,
3-(1-methyl-2-pyrrolidinyl)-,
(S)-
and
saltsPO76lOlO2-43
-9Nitric
oxidePO76lOlO2-43
- 9Nitrogen
oxide N0P077100-01-
6Benzenamine,
4-nitro-P077100-
Ol-6p-NitroanilinePo78lolo2-44-
ONitrogen
dioxidePO78lOlO2-44-ONitrogen
oxide
N02P08155-63-ONitroglycerine
(R)
P08155-63-
01,2,3-Propanetriol,
trinitrate-
(R)P08262-75-9Methanamine,
N-methyl-N-nitroso
P08262-75-9N-NitrosodimethylaminePo844549-40-ON-NitrosomethylvinylaminePo844549-
40-OVinylamine,
N-methyl-N-nitroso-P085152-16-9Diphosphoramide,
octamethyl
P085152-l6-9OctamethylpyrophosphoramidePO872O8l6-12-OOsmium
oxide
0s04,
(T-4) -
P08720816-l2-OOsmium
tetroxidepO88l45-73-3EndothallpO88l4E-73-37-
Oxabicyclo(2.2.1)heptane-2,3-dicarboxylic
acidPO8956-38-2ParathionPO895E-38-
2Phosphorothioic
acid,
0,0-diethyl
0-
(4-nitrophenyl)
esterPO9262-38-4Mercury,
(acetato-0)phenyl-P09262-38
-4Phenylmercury
acetatePo93lO3-85-
5PhenylthioureaPO93lO3
- 85-5Thiourea,
phenyl-P094298-02-2PhoratePO9429S-
02-
2Phosphorodithioic
acid,
0,0-diethyl
S-
(
(ethylthio)methyl)
esterPO9575-44-
5Carbonic dichloridePo9575-44-5PhosgenePO9678O3-51-2Hydrogen
phosphidePo9678o3-
51-2PhosphinePO9752-85-7FamphurPO9752-85-7Phosphorothioic
acid,
0-
(4-
((dimethy1amino)su1fony1)
)phenyl)
0,0-dimethyl
esterPO9Bl5l-50-8Potassium
cyanidePO98l5l-.50-BPotassium
cyanide
KCNP099506-61-6Argentate(1-),
bis(cyano-C)--
potassiumPo995o6-61-6Potassium
silver
cyanidePlollo7-12-OEthyl
cyanidePlOllO7-
12-OPropanenitrilePlo2lo7-19-7Propargyl
alcoholPlO2lO7-19-72-Propyn-l-olPl03630-
10-4SelenoureaPlO45O6-
64-
9Silver
cyanidePlO45O6-64-
9Silver cyanide
AgCNP10526628-22-
8Sodium
azidePlOEl43-33
-9Sodium
cyanidePl06l43-33
-9Sodium
cyanide
NaCNPl0857249*Strychnidinl0one,
and
saltsPl0857249*Strychnine
and
sa1tsP1093689-24-5TetraethyldithiopyrophosphatePlo93689-24-5Thiodiphosphoric
acid,
tetraethyl
esterPll078-00-2Plumbane,
tetraethyl-Pll078-00-2Tetraethyl
leadPllllo7-49-3Diphosphoric
acid,
tetraethyl esterPllllo7-49-
3TetraethylpyrophosphatePll25o9-l4-8Methane,
tetranitro-
(R)Pll2509-l4-
8Tetranitromethane
(R)
Pll3l3l4-32-5Thallic
oxidePll3l3l4-32-5Thallium
oxide
T1203P11412039-52-
OSelenious
acid, dithallium
(1+)
saltPll4l2039-52-OThallium
(I)
selenitePll57446-l8-6Sulfuric
acid, dithallium
(1+)
saltP1157446-18-
6Thallium
(I)
sulfatePll679-l9-6HydrazinecarbothioamidePll679--l9-
6ThiosemicarbazidePll875-70-7Methanethiol,
trichloro-P11875-70-
7TrichloromethanethiolPll978o3-55-6Ammonium
vanadatePll97803-55-6Vanadic
acid,
ammonium
saltPl2Ol3l4-62-lVanadium
oxide V205P1201314-62-lVanadium
pentoxidePl2l557-21-lZinc
cyanidePl2l557-21-lZinc
cyanide
Zn(CN)2Pl22l3l4-84-
7Zinc
phosphide Zn3P2,
when present
at concentrations
greater than
10
percent
(R,
T)P1238001-35-2ToxaphenePl27l563-66-27-Benzofuranol,
2,3-dihydro-2,2-
dimethyl-,
methylcarbamatePl27l563-66-2CarbofuranPl283lS-l8-4Phenol,
4-
(dimethylamino)-3,5-dimethyl-,
methylcarbamate
(ester)Pl29Pl283l5
B 4315-18-
4MexacarbatePl8s264l9-73-81,3-]Jithiolane-2-carboxaldehyde,
2,4-dimethyl-,
0-
((methylamino)
-
carbonyl)oximePl8526419-73-8TirpatePlBBS7-64-7Benzoic
acid,
2-
hydroxy-,
compound with
(3aS-cis)-1,2,3,3a,8,8a-hexahydro-l,3a,8-
trimethylpyrrolo(2,3-b)indol-5-yl
methylcarbamate
ester
(l:l)P18857-64-
7Physostigmine
salicylatePl8955285-14-8Carbamic
acid, ((dibutylamino)
-
thio)methyl-,
2, 3-dihydro-2,2-dimethyl-7-benzofuranyl
esterPl8955285-14-
8CarbosulfanPl9oll29-41-5Carbamic
acid,
methyl-,
3-methylphenyl esterPl90ll29-
4l-5MetolcarbPl9l644-64-4Carbamic
acid,
dimethyl-,
1-C
(dimethyl-amino)carbonyl)
5-methyl-1H-pyrazol-3-yl
esterPl9l644-64-4DimetilanPl92ll9-38-OCarbamic
acid,
dimethyl-,
3-methyl-l--
(l-methylethyl)-1H-pyrazol-5-yl
esterPl92ll9-38-
01so1anP19423l35-22-OEthanimidothioic
acid, 2- (dimethylamirio)
-N
(((methylamino)carbonyl)oxy)-2-oxo-,
methyl
esterPl9423l3S-22-00xamy1Pl9615339-
36-3Manganese,
bis(dimethylcarbamodithioato-S,S’)
-P19615339-36-3Manganese
dimethyldithiocarbamatePl97l77o2
-57- 7Formparanatepl97l77o2-
57-
7Methanimidamide,
N,N-dimethyl-N’
- (2-methyl-4-
(C
(methylamino)carbonyl)oxy)phenyl)
-P19823422-53-
9Formetanate
hydrochloridePl9823422-53-9Methanimidamide,
N,NdimethylNT
.(3
(((methylamino)
-carbonyl)oxy)phenyl)
-,
monohydrochloridePl992o32-65-
7MethiocarbPl992O32-65-7Phenol,
(3,5-dirnethyl-4-(methylthio)-,
methylcarbamateP2ol263l-37-OPhenol,
3-methyl-5-
(1-methylethyl)-,
methyl
carbamateP2ol263l-37-OPromecarbP2O264-00-6m-Cumenyl
methylcarbamateP2o264-00-63-
Isopropylphenyl-N-methylcarbamateP2o264-00-6Phenol,
3-
(1-methylethyl) -,
methyl
carbamateP2o3l646-88-4Aldicarb
sulfoneP2O3l646-88-4Propanal,
2-methyl-2- (methyl
sulfonyl)
-, 0-
(
(methylamino)carbonyl)
oximeP2O457-47-6PhysostigmineP2o457-47-
6Pyrrolo(2,3-b)indol-5-ol,
l,2,3,3a,8,8a-hexahydro-l,3a,8-trimethyl-,
methylcarbamate
(ester),
(3aS-cis)-P205l37-30-4Zinc,
bis
(dimethylcarbamodithioato-S,
S
T
)
-P205l37-30-4Ziram
BOARD
NOTE: An
asterisk
(*)
following
the CAS number
indicates
that
the CAS
number
is given
for the
parent
compound only.
f)
The commercial
chemical
products,
manufacturing
chemical
intermediates,
or
off-specification
commercial
chemical
products
referred to
in
subsections
(a)
through
(d)
of this Section,
are identified
as toxic
wastes
(T)
unless
otherwise
designated
and
are
subject
to the small
quantity
exclusion defined
in
Section
721.105(a)
and (g).
These
wastes
and their corresponding
USEPA
hazardous
waste
numbers are
the following:
BOARD
NOTE:
For the convenience
of the
regulated community,
the primary
hazardous
properties of these
materials
have been
indicated
by the letters
T
(Toxicity),
R
(Reactivity),
I (Ignitability),
and
C
(Corrosivity)
. The absence
of
a
letter
indicates
that the compound
is
only
listed
for toxicity.
Wastes
are
first
listed
in alphabetical
order
by substance
and
then
listed
again in
numerical
order by USEPA
hazardous waste
number.
USEPA Hazardous
Waste
No.Chemical
Abstracts
No.
(CAS
No.)
SubctanccUSubstanceU3943oss8-43-1A22l3UOOl75-07-cAcetaldehyde
(I)U03475-87-
GAcetaldehyde,
trichloro-U18762-44-2Acetamide,
N-
(4-ethoxyphenyl)-U00553-96-
3Acetamide,
N-9H-fluoren-2-yl-U240P
94-75-7Acetic
acid,
(2,4-dichiorophenoxy)-,
salts and estersUll2l4l-78-6Acetic
acid,
ethyl ester
(I)Ul4430l-04-2Acetic
acid,
lead
(2+)
saltU2l4563-68-8Acetic
acid, thallium
(1+)
saltSee
F02793-76-5Acetic
acid,
(2,4,5-trichlorophenoxy)-U00267-64-lAcetone
(I)U00375-05-8Acetonitrile
(I,
T)U00498-86-2AcetophenoneUoo5s3-96-32-AcetylaminofluoreneUoo67s-36-SAcetyl
chloride
(C,
R,
T)U00779-06-lAcrylamideUOO87B-10-7Acrylic
acid
(I)U009107-13-
lAcrylonitrileUoll6l-82-SAmitroleUOl262-53-3Aniline
(I,
T)Ul3675-60-SArsinic
acid, dimethyl-U0l4492-S0-BAuramineUOl5ll5-
02- 6AzaserineU0l050-
07-
7Azirino(2’
,3’:3
,4)pyrrolo(1,
2-a)
indole-4,
7-dione, 6-amino-8-
(((aminocarbonyl)oxy)methyl)-l,
la,2, 8, Ba,
8b-hexahydro-8a-methoxy-5-methyl-,
(la
S-(la?,8?,8a?,8b?))-U280l01-27-9BarbanU27822781-23-3BendiocarbU3642296l-82-
GBendiocarb
phenolU27ll78O4-35-2BenomylUl5756-49-5Benz(j)aceanthrylene,
1,2-
dihydro-3-methyl-U016225-5l-4Benz
(c)
acridineUol798-87-3Benzal
chlorideUl922395o-
58-SBenzamide,
3,5-dichloro-N-(l,1-dimethyl-2-propynyl)-U01856-55-
3Benz(a)anthraceneUo9457-97-6Benz(a)anthracene,
7,l2-dimethyl-U0l262-53-
3Benzenamine
(I, T)U014492-80-8Benzenamine, 4,4’ -carbonimidoylbis(N,N-dimethyl
U0493l65-93-3Benzenamine,
4-chloro-2-methyl-,
hydrochlorideU09360-11-
7Benzenamine,
N,N-dimethyl-4-
(phenylazo)
-U32895-53-4Benzenamine,
2-methyl-
U353106-49-OBenzenamine,
4-methyl-U158101-14-4Benzenamine,
4,4’-methylenebis(2-
chloro-U222636-2l-5Benzenamine,
2-methyl-,
hydrochlorideUl8l99-55-BBenzenamine,
2-methyl-5-nitro-U0197l-43-2Benzene
(I, T)U038510-15-6Benzeneacetic
acid, 4-
chloro-?-(4-chlorophenyl)-?-hydroxy-,
ethyl esterUO3olol-55-3Benzene,
1-bromo-4-
phenoxy-U035305-03-3Benzenebutanoic
acid,
4-(bis(2-chloroethyl)amino)-U037l08-
90-7Benzene,
chloro-U22l25376-45-8Benzenediamine,
ar-methyl-U0281l7-81-7l,
2-
Benzenedicarboxylic
acid, bis(2-ethylhexyl)
esterUO69B4-74-21,2-
Benzenedicarboxylic
acid, dibutyl
esterUOS884-66-2l,2-Benzenedicarboxylic
acid,
diethyl
esterUlO2l3l-11-31,2-Benzenedicarboxylic
acid,
dimethyl
esterUlO7ll7-84-
01,2-Benzenedicarboxylic
acid,
dioctyl
esterUO7O9S-50-lBenzene,
1,2-dichloro-
U07154l-73-lBenzene,
1,
3-dichloro-U072106-46-7Benzene,
1, 4-dichloro-U06072-54-
BBenzene, 1,1’-(2,2-dichloroethylidene)bis(4-chloro-U01798-87-3Benzene,
(dichloromethyl)-U22326471-62-5Benzene,
l,3-diisocyanatomethyl-
(R, T)U239l330-
20-7Benzene,
dimethyl-
(I, T)U201108-46-31,3-BenzenediolUl27llB-74-lBenzene,
hexachloro-U056110-82-7Benzene,
hexahydro-
(I)U220108-88-3Benzene,
methyl
Ul05121-14-2Benzene,
1-methyl-2,
4-dinitro-U106606-20-2Benzene,
2-methyl-l,
3-
dinitro-U05598-82-8Benzene,
(1-methylethyl)-
(I)Ul6998—95-3Benzene,
nitro
U183608-
93
-5Benzene,
pentachloro-U18582-
68-BBenzene,
pentachloronitro-U02098-09-
9Benzenesulfonic
acid
chloride
(C,
R)U02098-09-9Benzenesulfonyl
chloride
(C,
R)U20795-94-3Benzene,
l,2,4,5-tetrachloro-U06l50-29-3Benzene,
l,1’-(2,2,2-
trichloroethylidene)bis(4-chloro-U24772-43-5Benzene,
l,l’-(2,2,2-
trichloroethylidene)bis(4-methoxy-U02398-07-7Benzene,
(trichloromethyl)-U23499-
35-4Benzene,
l,3,5-trinitro-U02192-87-5BenzideneU202P
8l-07-21,2-Benzisothiazol-
3
(2H)
-one,
1,1-dioxide,
and
saltsU2O394-59-71,3-Benzodioxole,
5-
(2-propenyl)-
U141120-58-11,3-Benzodioxole,
5-(l-propenyl)-U09094-58-61,3-Benzodioxole,
5-
propyl-U27822781-23-31,3-Benzodioxol-4-ol,
2,2-dimethyl-,
methyl
carbamateU3642296l-82-61,
3-Benzodioxol-4-ol,
2,
2-dimethyl-U3671563-38-87-
Benzofuranol,
2,3-dihydro-2,2-dimethyl-U064189-55-9Benzo(rst)pentapheneU248P
81-
81-22H-1-Benzopyran-2-one,
4-hydroxy-3-(3-oxo-1-phenylbutyl)-,
and
salts, when
present
at concentrations
of
0.3 percent
or
lessUO225O-32-
BBenzo(a)pyreneUl97lo6-51-4p-BenzoquinoneUo2398-07-7Benzotrichloride
(C,
R,
T)U0851464-53-52,
2
‘ -BioxiraneUo2l92-87-5
(1,
1’ -Biphenyl)
-4,4’ -diamineUo739l-94-
1(1,1’-Biphenyl)-4,4’-diamine,
3,3’-dichloro-U09l119-90-4(1,1’-Biphenyl)-4,4’-
diamine,
3,3’dimethoxy-U0951l9-937(1,1’Bipheny1)-4,4’-diamine,
3,3’-dimethyl-
U22575-25-2BromoformU030lOl-55-34-Bromophenyl
phenyl
etherUl2887-68-31,
3-
Butadiene,
1,1,2,3,4,4-hexachloro-U172924-16-31-Butanamine,
N-butyl-N-nitroso
U03171-36-31-Butanol
(I)U15978-93-32-Butanone
(I,
T)U1601338-23-42-Butanone,
peroxide
(R,
T)U0534170-30-32-ButenalUO74764-41-02-Butene,
1,
4-dichloro-
(I,
T)U143303-34-42-Butenoic acid,
2-methyl-,
7-((2,3-dihydroxy-2-(1-methoxyethyl)-
3-methyl-1-oxobutoxy)methyl)-2,3,5,7a-tetrahydro-1H-pyrrolizin-l-yl
ester,
(is
(1?(z),
7(2S*,3R*),
7a?))-U03171-36-3n-Butyl
alcohol
(I)U13675-60-SCacodylic
acidtJ03213765-19-OCalcium
chromateU372lO6OS-21-7Carbamic
acid,
1H-benzimidazol-
2-yl,
methyl
esterU27ll78O4-35-2Carbamic
acid,
(l-((butyiamino)carbonyl)-1H-
benzimidazol-2-yl)-, methyl
esterU28OlOl-27-9Carbamic
acid,
(3-chiorophenyl)-,
4-chloro-2-butynyl
esterU238Si-
79-
GCarbamic
acid,
ethyl
esterUi7B6l5-53-
2Carbamic
acid,
methylnitroso-,
ethyl
esterU373l22-42-9Carbamic acid,
phenyl-,
1-methylethyl
esterU40923564-05-8Carbamic
acid,
(1,2-
phenylenebis
(iminocarbonothioyl)
)bis-,
dimethyl
esterUO9779-44-7Carbamic
chloride,
dimethyi-U114P
lli-54-6Carbamodithioic
acid,
i,2-ethanediylbis-,
salts
and
estersUO6223O3-l6-4Carbamothioic
acid,
bis(1-methylethyi)-,
S-(2,3-dichloro-
2-propenyl)
esterU3892303-l7-BCarbamothioic
acid,
bis(l-methylethyl)-,
S-(2,3,3-
trichloro-2-propenyi) esterU38752888-80-9Carbamothioic
acid,
dipropyl-,
S
(phenylmethyl)
esterU279G3
-25-2CarbarylU372lOEOS-2l-7CarbendazimtJ367ls63-38-
BCarbofuran
phenoiU2i56533-73-9Carbonic
acid,
dithallium
(1+)
salttJ033353-50-
4Carbonic
difluorideul5679-22-lCarbonochioridic
acid, methyl
ester
(I,
T)U033353-50-4Carbon oxyfluoride
(R,
T)U2l156-23-5Carbon
tetrachlorideUo347s-87-
SChloralUO353O5-03-3ChlorambucilUO36S7-74-9Chlordane,
?
and ?
isomersUO26494-03-
lChiornaphazinUO37lo8 -90- 7ChlorobenzeneUo3
8510-
15- 6Chlorobenzilatelio3959-
50-
7p-
Chloro-m-cresolU042llo-75-82-Chloroethyl
vinyl
ethertJO4467-66-
3ChloroformUo46lo7-30-2Chloromethyi
methyl
etherUO479l-58-7?-
ChloronaphthaleneUo489s-57-8o-ChlorophenolUO493l65-93-34-Chioro-o-toluidine,
hydrochlorideUo32l3765-19-OChromic
acid H2CrO4,
calcium
saitUO5O2l8-0l-
9ChryseneUo5lCreosoteUos2l3l9-77-3Cresoi
(Cresylic
acid)U0534l70-30-
3CrotonaldehydeU05598-82-SCumcmc
Cumene
(I)U246506-68-3Cyanogen
bromide
CNBrU1971O6-5l-42,5-Cyclohexadiene-l,4-dioneUOS6liO-82-7Cyclohexane
(I)U12958-
89-9Cyclohexane,
1,2,3,4,5,6-hexachloro-,
(1?,2?,3?,4?,5?,6?)-U057108-94-
lCyciohexanone
(I)U13077-47-4l,3-Cyclopentadiene,
l,2,3,4,5,5-hexachloro-U05850-
18-OCyciophosphamideu24oP 94-75-72,4-D,
salts and
estersUO592O83O-8l-
3DaunomycinUo6o72-54-8DDDUO615O-29-3DDTU0622303-16-4DiaiiateUO6353-70-
3Dibenz(a,h)anthraceneUo64l89-55-9Dibenzo(a,i)pyreneUO6696-12-81,2-Dibromo-3-
chloropropaneUo6984-74-2Dibutyl
phthalateUo7o95-50-lo-Dichiorobenzeneuo7l54l-73-
lm-DichlorobenzeneUo72i06-46-7p-DichlorobenzeneUo739l-94-13,3
‘
-
DichlorobenzidineUo74764-4l-0l,
4-Dichloro-2-butene
(I, T)U07575-71-
8DichlorodifluoromethaneUO7875-35-41,l-DichloroethyleneUO79l56-60-51,2-
DichloroethyleneUO25lll-44-4Dichloroethyl
etherUO27lO8-60-lDichloroisopropyl
etherUO24lll-91-lDichloromethoxy
ethaneUO8ll2O-83-22
,
4-DichlorophenolUO8287-65-
02,6-DichlorophenolUO84542-75-61,3-DichloroproperieuO85l464-53-51,2:3,4-
Diepoxybutane
(I,
T)U3955952-26-lDiethylene
glycol,
dicarbamateUlO8l23-91-1l,4-
DiethyleneoxideuO28ll7-81-7Diethylhexyl
phthalateUO8Gl6lS-BO-1N,N’
-
DiethylhydrazineuOs73288-58-20,O-Diethyl
S-methyl dithiophosphateUOB884-66-
2Diethyl phthalateuO8956-53-lDiethylstilbestrolUO9O94-58-GDihydrosafroleUO9lll9-
90-43,3’-DimethoxybenzidineUO92l24-40--3Dimethylamine
(I)U09360-11-7p-
DimethylaminoazobenzeneUO9457-97-67,12-Dimethylbenz(a)anthraceneUO95ll9-93-
73,3’
-DimethylbenzidineUO96so-15-9?,
?-Dimethylbenzylhydroperoxide
(R)U09779-44-
7Dimethylcarbamoyl
chlorideUO9857-14-71,
1-DimethylhydrazineUO9954O-73-81,2-
DimethylhydrazineUlOllO5-67-92,4-DimethylphenolUlo2l3l-11-3Dimethyl
phthalateUlO377-78-lDimethyl
sulfateUlO5l2l-14-22,
4-DinitrotolueneUlO66O6-20-
22,
6-DinitrotolueneUlO7ll7-84-ODi-n-octyl
phthalateUlO8l23-91-ll,4-
DioxaneUlO9l22-66-71,2-DiphenylhydrazineUllOl42-84-7Dipropylamine
(I)U111621-64-
7Di-n-propylnitrosamineUO4llO6-89-BEpichlorohydrinuOOl75-07-OEthanal
(I)U404121-
44-8Ethanamine,
N,N-diethyl-U17455-18-5Ethanamine,
N-ethyl-N-nitroso-U15591-80-
51,2-Ethanediamine,
N,N-dimethyl-N’-2-pyridinyl-N’-(2-thienylmethyl)-U067106-93-
4Ethane,
l,2-dibromo-U07675-34-3Ethane,
l,l-dichloro-U077107-06-2Ethane,
1,2-
dichloro-U13167-72-lEthane,
hexachloro-U024111-91-lEthane,
1,1’-
(methylenebis(oxyHbis(2-chloro-U11760-29-7Ethane,
l,1’-oxybis--
(I)U025111-44-
4Ethane,
l,l’-oxybis(2-chloro-tfl8476-O1-7Ethane,
pentachloro-U208630-20-6Ethane,
l,l,1,2-tetrachloro-U20979-34-5Ethane,
1,l,2,2-tetrachloro-U21862-55-
5EthanethioamideU2267l-55-6Ethane,
1,1,l-trichloro-U22779-00-5Ethane,
1,1,2-
trichloro-U41059669-26-OEthanimidoth±oic
acid, N,N’ -
(thiobis(
(methylimino)carbonyloxyHbis-,
dimethyl
esterU39430558-43-
lEthanimidothioic
acid,
2- (dimethylamino)
-N-hydroxy-2-oxo-,
methyl
esterU3S9llO-
S0-5Ethanol, 2-ethoxy-U1731116-54-7Ethanol,
2,2’-(nitrosoimino)bis-U3955952-26-
lEthanol,
2,2-oxybis-,
dicarbamateUoo498-86-2Ethanone,
1-phenyl-U04375-01-
4Ethene,
chloro-U042110-75-8Ethene,
(2-chloroethoxy)-U07875-35-4Ethene,
1,1-
dichloro-U079156-60-SEthene,
1.2-dichioro-,
(E)-U210127-18-4Ethene,
tetrachioro
U22879-01-6Ethene,
trichloro-U1l2141-78-GEthyl
acetate (I)U113140-88-5Ethyl
acrylate
(I)U23851-79-6Ethyl
carbamate
(urethane)U11760-29-7Ethyl
etherUll4P
lll-54-6Ethylenebisdithiocarbamic
acid,
salts and estersUOG7lOG-93-4Ethylene
dibromideUo77l07-06-2Ethylene
dichlorideU359llo-80-5Ethylene
glycol monoethyl
etherUll575-21-8Ethylene
oxide
(I,
T)U11696-45-7EthylenethioureaUo7675-34-
3Ethylidene
dichlorideUll897-63-2Ethyl
methacrylateUll962-50-OEthyl
methanesulfonateUl2o2o6-44-OFluorantheneUl225o-00-OFormaldehydeUl2364-18-6Formic
acid
(C,
T)U124110-00-9Furan
(I)U12598-01-12-Furancarboxaldehyde
(I)U147108-31-
62,5-Furandioneu2l3l09-99-9Furan,
tetrahydro-
(I)U12598-01-lFurfural
(I)U124110-
O0-9Furfuran
(I)U20618883-66-4Glucopyranose,
2-deoxy-2-
(3-methyl-3-
nitrosoureido)
-, D-U20618883-66-4D-Glucose,
2-deoxy-2-
(((methylnitrosoamino)
carbonyl)amino)
-U126765-34-4GlycidylaldehydeUl637o-25-7Guanidine,
N-methyl-N
T
-
nitro-N-nitroso-U127l18-74-lHexachlorobenzeneUl2887-68-
3HexachlorobutadieneUl3
077-47
-4HexachlorocyclopentadieneUl3
167-72-
lHexachloroethaneUl3270
-3 0-4HexachloropheneU243l888
-71-
7HexachloropropeneUl333o2-0l-2Hydrazine
(R,
T)U0861615-S0-lHydrazine,
1,2-
diethyl-U09857-14-7Hydrazine,
1, l-dimethyl-U099540-73-8Hydrazine,
1, 2-dimethyl-
U109122-66-7Hydrazine,
1,
2-diphenyl-U1347664-39-3Hydrofluoric
acid
(C,
T)U1347664-39-3Hydrogen
fluoride
(C,
T)U1357783-06-4Hydrogen
sulfideUl357783-06-
4Hydrogen
sulfide
H25U09680-15-9Hydroperoxide,
1-methyl-l-phenylethyl-
(R)Ul1696-45-72-Imidazolidinethioneul37l93-39-5lndeno(1,2,3-cd)pyreneUl9O85-44-
91,3-Isobenzofurandioneul4o78-83-llsobutyl
alcohol
(I,
T)Ul4ll2O-58-
llsosafroleUl42l43-50-OKeponeUl433O3-34-4LasiocarpeneUl443ol-04-2Lead
acetateUl46l335-32-6Lead,
bis(acetato-O)tetrahydroxytri-Ul457446-27-7Lead
phosphateul46l335-32-ELead
subacetateUl2958-89-9LindaneUl637O-25-7MNNGU1471O8-
31-6Maleic
anhydrideUl48l23-33-lMaleic
hydrazideUl49lO9-77-
3MalononitrileUl5Ol4S-82-3MelphalanUl5l7439-97-6MercuryUl52l26-98-
7Methacrylonitrile
(I, T)U092124-40-3Methanamine,
N-methyl- (I)U02974-83-
9Methane,
bromo-U04574-87-3Methane,
chioro-
(I,
T)U046107-30-2Methane,
chloromethoxy-U06874-95-3Methane,
dibromo-U08075-09-2Methane,
dichloro-U07575-
71- 8Methane,
dichlorodifluoro-U13874-88-4Methane,
iodo-U11962-50-
OMethanesulfonic
acid, ethyl
esterU2ll5G-23-5Methane,
tetrachloro-U15374-93-
lMethanethiol
(I,
T)U22575-25-2Methane,
tribromo-U04467-66-3Methane,
trichloro
Ul2175-69-4Methane,
trichlorofluoro-U03657-74-94,
7-Methano-1H-indene,
l,2,4,5,6,7,8,8-octachloro-2,3,3a,4,7,7a-hexahydro-U15467-56-lMethanol
(I)U15591-80-5MethapyrileneUl42l43-50-Ol,3,4-Metheno-2H-cyclobuta(cd)pentalen-2-
one,
l,la,3,3a,4,5,5,5a,5b,6-decachlorooctahydro-U24772-43-5MethoxychlorUl5467-
56-iMethyl
alcohol
(I)U02974-83-9Methyl
bromideUl8G5O4-60-91-Methylbutadiene
(I)U04574-87-3Methyl
chloride
(I,
T)Ul5679-22-lMethyl
chlorocarbonate
(I,
T)U22671-55-GMethylchloroformUl5756-49-53-MethylcholanthreneUl58lOl-14-44,
4’-
Methylenebis(2-chloroaniline)U06874-95-3Methylene
bromideUO8O75-09-2Methylene
chlorideUl5978-93-3Methyl
ethyl
ketone
(MEK)
(I,
T)U1601338-23-4Methyl
ethyl
ketone peroxide
(R,
T)U13874-88-4Methyl
iodideUl6llOB-1O-lMethyl
isobutyl
ketone
(I)U16280-62-6Methyl
methacrylate
(I,
T)Ul6l108-lO-l4-Methyl-2-pentanone
(I)Ul6456-04-2MethylthiouraciluOlO5O-07-7Mitomycin
CU05920830-Bl-35,
12-
Naphthacenedione,
8-acetyl-lO-
((3-amino-2,3,
6-trideoxy-?-L-lyxo-
hexapyranosyl)oxyl)-7,8,9,lO-tetrahydro-6,8,ll-trihydroxy-l-methoxy-,
(8S-cis)-
Ul67134-32-7l-Naphthalenamineul6s9l-59-82-NaphthalenamineUO26494-03-
lNaphthaleneamine,
N,N’ -bis (2-chloroethyl)
-Ul6591-20-3NaphthaleneUO479l-58-
7Naphthalene,
2-chloro-U166130-l5-41,
4-NaphthalenedioneU23672-57-12,
7-
Naphthalenedisulfonic
acid,
3,3’-((3,3’-dimethyl-(l,l’-biphenyl)-4,4’-
diyl)bis(azo)bis(5-amino-4-hydroxy)
-, tetrasodium
saltU27963-25-21-Naphthalenol,
methylcarbamateul66l3a-l5-4l,4-NaphthoquinoneUl67l34-32-7?-Naphthylamineul6s9l-
59-
8?-NaphthylamineU2l7lolO2-45-lNitric
acid,
thallium
(1+)
saltUl6998-
95-
3Nitrobenzene
(I,
T)U170100-02-7p-Nitrophenolul7l79-46-92-Nitropropane
(I,
T)U172924-l6-3N-Nitrosodi-n-butylamineUl73lll6-54-7N-
NitrosodiethanolamineUl745s-lS-5N-NitrosodiethylaminetJl767s9-73-9N-Nitroso-N-
ethylureaUl776B4-93-5N-Nitroso-N-methylureaul786l5-53-2N-Nitroso-N-
methylurethaneUl79lOO
- 75-4N-Nitrosopiperidineul8O93
0-
55-2N-
NitrosopyrrolidineUl8l99-55-85-Nitro-o-toluidineUl93ll2O-71-41,2-Oxathiolane,
2,2-dioxideU05850-18-02H-l,3,2-Oxazaphosphorin-2-amine,
N,N-bis(2-
chloroethyl)tetrahydro-,
2-oxideUlls7s-21-SOxirane
(I,
T)U126765-34-
4OxiranecarboxyaldehydeUo4llo6-89-8Oxirane,
(chioromethyl)
-Ul82123-63-
7ParaldehydeUl836O8-93-5Pentachlorobenzeneul8476-Ol-7PentachloroethaneUl8582-68-
8Pentachloronitrobenzene
(PCNB)See
F02787-86-5PentachlorophenolUl6llo8-l0-
lpentanol,
4-methyl-U186504-60-91,
3-Pentadiene
(I)U18762-44-2PhenacetinUl8BlO8-
95-2PhenolUO4895-57-8Phenol,
2-chloro-U03959-50-
7Phenol,
4-chloro-3
-methyl
U081120-83-2Phenol,
2,4-dichloro-U08287-65-OPhenol,
2,
6-dichloro-U08956-53-
iPhenol,
4,4’-(1,2-diethyl-l,2-ethenediyl)bis-, (E)-tJlOllOS-67-9Phenol,
2,4-
dimethyl-U0521319-77-3Phenol,
methyl-U13270-30-4Phenol,
2,2’ -methylenebis(3,4,6-
trichloro-U41l1l4-26-lPhenol,
2-
(1-methylethoxy)
-, methylcarbamateUl7oloO-02-
7Phenol,
4-nitro-See
F02787-86-5Phenol,
pentachloro-See
F02758-90-2Phenol,
2,3,4,6-tetrachioro-See
F02795-95-4Phenol,
2,4,5-trichioro-See
F02788-06-
2phenol,
2,4,6-trichloro-U150148-82-3L-Phenylalanine, 4- (bis(2-
chloroethyl)amino)-U1457446-27-7Phosphoric
acid, lead
(2+)
salt
(2:3)U0873288-
58-2Phosphorodithioic
acid, 0,0-diethyl
S-methyl
esterUl89l3l4-80-3Phosphorus
sulfide
(R)U19085-44-9Phthalic
anhydrideUl9llo9-06-82-PicolineUl79loo-75-
4Piperidine,
1-nitroso-Ul9223950-58-5PronamideUl94lO7-l0-81-Propanamine
(I,
T)U111621-64-71-Propanamine,
N-nitroso-N-propyl-U110142-84-71-Propanamine,
N
propyl-
(I)U06696-12-SPropane,
l,2-dibromo-3-chloro-U08378-87-5Propane,
1,2-
dichloro-U149109-77-3PropanedinitrileUl7l79-46-9Propane,
2-nitro-
(I,
T)U027108-
60-lPropane,
2,2’-oxybis(2-chloro-See
F02793-72-lPropanoic
acid,
2-(2,4,5-
trichlorophenoxy)-U1931120-71-41,3-Propane
sultoneU23Sl26-72-71-Propanol,
2,3-
dibromo-,
phosphate (3:l)U14078-83-1l-Propanol,
2-methyl-
(I, T)U00267-64-12-
Propanone
(I)U00779-O6-12-PropenamideUO84542-75-61-Propene,
1, 3-dichioro-
U2431888-71-71-Propene,
1,
1,2,3,3,3-hexachloro-U009107-13-l2-
PropenenitrileUl52l26-98-72-Propenenitrile,
2-methyl-
(I,
T)U00879-1O-72-
Propenoic
acid (I)U113l40-88-52-Propenoic
acid, ethyl
ester
(I)U11897-63-22-
Propenoic
acid, 2-methyl-,
ethyl
esterUl62BO-62-62-Propenoic
acid, 2-methyl-,
methyl
ester
(I,
T)U373122-42-9ProphamU4llll4-26-lPropoxurSee
F02793-72-
iPropionic acid,
2-
(2,4,
5-trichlorophenoxy)
-U194107-lO-8n-Propylamine
(I,
T)U08378-87-5Propylene
dichlorideU38752888-80-9ProsulfocarbUl4Bl23-33-13,
6-
Pyridazinedione,
1, 2-dihydro-U196110-86-lPyridineUl9llO9-06-8Pyridine,
2-methyl-
U23766-75-12,4-(1H,3H)-Pyrimidinedione,
5-(bisC2-chloroethyl)
amino)-U16458-04-
24(1H)-Pyrimidinone,
2,3-dihydro-6-methyl-2-thioxo-U180930-55-2Pyrrolidine,
1-
nitroso-U20050-55-5ReserpineU2OllO8-46-3ResorcinolU2O2P
81-
07-2Saccharin and
saltsU2O394-59- 7SafroleU2O47783
- 00-8Selenious
acidU2047783-00-8Selenium
dioxideU2O57488-56-4Selenium
sulfideU2O57488-56-4Selenium
sulfide
SeS2
CR,
T)U015115-02-6L-Serine,
diazoacetate
(ester)See
F02793-72-lSilvex
(2,4,5-
TP)U20618883-66-4StreptozotocinUlo377-78-lSulfuric
acid,
dimethyl esterUl89l3l4-
80-3Sulfur
phosphide
CR)See
F02793-76-52,4,
5-TU20795-94-3l,2,4,
5-
TetrachlorobenzeneU20863o-20-61,l,l,2-TetrachloroethaneU20979-34-51,l,2,2-
Tetrachloroethaneu2l0l27-18-4TetrachloroethyleneSee F02758-90--22,3,4,
6-
TetrachlorophenolU2l3lo9-99-9Tetrahydrofuran
(I)U2l4563-68-8Thallium
(I)
acetateU2l56533
-73 -9Thallium
(I)
carbonateU2l6779l-12
- OThallium
(I)
chlorideU2lE779l-l2-
OThallium chloride
TlC1U21710102
-45-lThallium
(I)
nitrateU2l862-55-5ThioacetamideU4lo59669-26-OThiodicarbul5374-93-lThiomethanol
(I,
T)U244137-26-8Thioperoxydicarbonic
diamide ((H2N)C(S)
)2S2,
tetramethyl
U40923564-05-SThiophanate-methylU2l962-56-6ThioureaU244l37-26-8ThiramU22OlO8-88-
3TolueneU22l25376-45-8ToluenediamineU2232647l-62-5Toluene
diisocyanate
CR,
T)U32895-53-4o-ToluidineU353lO6-49-Op-ToluidineU222636-21-So-Toluidine
hydrochlorideU38923o3-17-STriallateUOll6l-82-51H-1,2,4-Triazol-3-amineU22779-00-
5Ethanc,
1,1,2
trichioro U22779
00 51,l,2-TrichloroethaneU22879-01-
6TrichloroethyleneUl2l75-69-4TrichloromonofluoromethaneSee
F02795-95-42,4,5-
TrichiorophenolSee
F02788-06-22,4,6-TrichlorophenolU4o4l2l-44-
8TriethylamineU23499-35-41,3,5-Trinitrobenzene
CR,
T)U182l23-63-71,3,5-Trioxane,
2,4,6-trimethyl-U235126-72-7Tris
(2,3-dibromopropyl)
phosphateU23672-57-lTrypan
b1ueU23766-
75-lUracil
mustardUl76759-73
-SUrea, N-ethyl-N-nitroso-U177684-
93-
5Urea, N-methyl-N-nitroso-U04375-01-4Vinyl
chlorideU248P 81-81-2Warfarin,
and
salts, when
present
at concentrations
of
0.3
percent
or
lessU239l330-20-7Xylene
(I)U20050-55-5Yohimban-l6-carboxylic
acid, ll,l7-dimethoxy-18-((3,4,5-
trimethoxybenzoyl)oxy)-, methyl
ester,
C3?,16?,17?,18?,20?)-U2491314-84-7Zinc
phosphide
Zn3P2,
when present
at concentrations
of 10 percent
or less
Numerical
Listing
USEPA
Hazardous Waste
No.Chemical Abstracts
No.
(CAS
NojSubstance
U00175-07-OAcetaldehyde
(I)U00175-07-OEthanal
(I)U00267-64-lAcetone
CI)U00267-
64-12-Propanone
(I)U00375-05-8Acetonitrile
(I,
T)U00498-86-2AcetophenoneUoo498-
86-2Ethanone, l-phenyl-U00553-96-3Acetamide,
N-9H-fluoren-2
-yl-U00553-96-32-
AcetylaminofluoreneUoo675-36-5Acetyl
chloride
(C,
R,
T)U00779-06-
lAcrylamideUoo779-06-12-PropenamideUoo879-l0-7Acrylic
acid
CI)U00879-l0-72-
Propenoic
acid
CI)U009107-13
-lAcrylonitrileUOO9lO7
-13
-12-Propenenitrileuolo5o-
07-7AzirinoC2’,3’:3,4)pyrrolo(l,2-a)indole-4,7-dione,
6-amino-8-
(((aminocarbonyl)oxy)methyl)-l,
la,2,
8, 8a, 8b-hexahydro-8a-methoxy-5-methyl-,
(la
S-Cla?,8?,8a?,8b?H-U01050-07-7Mitomycin CUO1161-82-5AmitroleUOll6l-82-51H-
l,2,4-Triazol-3-amineUOl262-53-3Aniline
CI,
T)U01262-53-3Benzenamine
(I,
T)U014492-80-8AuramineUOl4492-80-8Benzenamine,
4,4’-carbonimidoylbisCN,N-
dimethyl-U015115-02-6AzaserineUOl5ll5-02-6L-Serine,
diazoacetate
Cester)U0l6225-
51-4Benz
Cc)
acridineUol798-87-3Benzal
chlorideUOl798-87-3Benzene,
(dichloromethyl)-U01856-55-3Benz(a)anthracerieUol97l-43-2Benzene
(I, T)U02098-09-
9Benzenesulfonic acid
chloride
(C,
R)U02098-09-9Benzenesulfonyl
chloride
(C,
R)U02192_87_5BenzideneUO2l92_87_5(l,1T_Biphenyl)_4,41_diamineUO225O_32_
BBenzo(a)pyreneUO2398-07-7Benzene,
(trichloromethyl) -U02398-07-7Benzotrichloride
(C,
R, T)U024111-91-lDichloromethoxy
ethaneUO24lll-91-lEthane, 1,1’-
(methylenebis(oxy))bis(2-chloro-U02511l-44-4Dichloroethyl etherUO25lll-44-
4Ethane,
l,l-oxybis(2-chloro-U026494-03-lChlornaphazinUO26494-03-
lNaphthaleneamine, N,N’ -his (2-chioroethyl)
-U027108-60-lDichloroisopropyl
etherUO27lO8-60-lPropane, 2,2-oxybis(2-chloro-U028117-8l-71,2-
Benzenedicarboxylic acid, his (2-ethylhexyl)
esterUO2Sll7-81-7Diethylhexyl
phthalateUO2974-83 - 9Methane, bromo-U02974
-83-9Methyl bromideUO3OlOl-55-3Benzene,
l-bromo-4-phenoxy-U030101-55-34-Bromophenyl
phenyl etherUO3l7l-36-31-Butanol
(I)U03171-36-3n-Butyl alcohol
(I)U03213765-19-OCalcium
chromateUO32l3765-l9-
OChromic acid H2CrO4, calcium saltU033353-50-4Carbonic
ditluorideUO33353-50-
4Carbon oxyfluoride
(R,
T)U03475-87-6Acetaldehyde,
trichloro-U03475-87-
6ChloralUO353O5-03-3Benzenebutanoic
acid, 4-(bis(2-chloroethyl)amino)-U035305-
03-3ChlorambucilUO3657-74-9Chlordane,
? and ? isomersUO3657-74-94,7-Methano-1H-
indene, 1,2,4,5,6,7,8, 8-octachloro-2,3,3a,4,
7, 7a-hexahydro-U037108-90-7Benzene,
chloro-U037l08-90-7ChlorobenzeneUO385lO-15-6Benzeneacetic
acid, 4-chloro-?-
(4-
chlorophenyl)-?-hydroxy-, ethyl
esterUO385lO-15-6ChlorobenzilateUO3959-50-7p-
Chloro-m-cresolUO3959-50-7Phenol, 4-chloro-3
-methyl-U04l106-89-
8EpichlorohydrinUO4llO6-89-8Oxirane, (chioromethyl)
-U042110-75-82-Chloroethyl
vinyl etherUO42llO-75-8Ethene, (2-chloroethoxy)
-U04375-Ol-4Ethene, chloro
U04375-O1-4Vinyl chlorideUO4467-66-3ChloroformUO44G7-66-3Methane,
trichioro
U04574-87-3Methane, chioro-
(I,
T)U04574-87-3Methyl
chloride
(I, T)U046107-30-
2Chloromethyl methyl etherUO46lO7-30-2Methane,
chloromethoxy-U04791-58-7?-
ChloronaphthaleneUO479l-58-7Naphthalene, 2-chloro-U04895-57-8o-
ChlorophenolUO489s-57-8Phenol, 2-chloro-U0493165-93-3Benzenamine,
4-chloro-2-
methyl-, hydrochlorideuO493l65-93-34-Chloro-o-toluidine,
hydrochlorideuO5O2l8-
O1-9ChryseneUO5lCreosoteUO52l3l9-77-3Cresol
(Cresylic
acid)U0521319-77-3Phenol,
methyl-U0534170-30-32-ButenalUO534l7O-30-3CrotonaldehydeuOs598-82-8Benzene,
(1-
methylethyl)-
(I)U05598-82-8Cumcmc
Cumene
(I)U056110-82-7Benzene,
hexahydro
(I)U056110-82-7Cyclohexane (I)U057108-94-lCyclohexanone
(I)U05850-18-
OCyclophosphamideUo58sO-l8-02H-1,3,2-Oxazaphosphorin-2-amine,
N,N-bis(2-
chloroethyl)tetrahydro-, 2-oxideU05920830-81-3DaunomycinU0592083O-81-35,12-
Naphthacenedione,
8-acetyl-l0-((3-amino-2,3,6-trideoxy)-?-L-lyxo--
hexapyranosyl)oxyl)-7,8,9,lO-tetrahydro-6,8,ll-trihydroxy-1-methoxy-,
(8S-cis)-
U06072-54-8Benzene, l,1
T
-(2,2-dichloroethylidene)bis(4-chloro-U06072-54-
8DDDU06150-29-3Benzene,
l,1T_(2,2,2_trich1oroethylidene)bis(4_chloroU06l50_29
3DDTU0622303-16-4Carbamothioic acid, bis(l-methylethyl)-,
S-(2,3-dichloro-2-
propenyl)
esterUO6223O3-16-4DiallateUO6353-70-3Dibenz(a,h)anthraceneUo64l89-55-
9Benzo (rst)pentapheneUc64l89-55-9Dibenzo
(a,
i)pyreneUO6696-12-81, 2-Dibromo-3-
chloropropaneuo6696-12-8Propane, 1,
2-dibromo-3-chloro-U067106-93-4Ethane,
1,2-
dibromo-U067106-93-4Ethylene dibromideUo6874-
95-3Methane, dibromo-U06874-95-
3Methylene bromideUo6984-74-21,2-Benzenedicarboxylic
acid, dibutyl esterUO6984-
74-2Dibutyl phthalateUo7o95-50-lBenzene,
1, 2-dichloro-U07095-50-lo-
DichlorobenzeneuO7l54l-73-lBenzene,
1,3-dichloro-U071541-73-lm-
DichlorobenzeneuO72lo6-46-7Benzene, 1,
4-dichloro-U072106-46-7p-
DichlorobenzeneUo739l-94-l(l,l’-Biphenyl)-4,4’-diamine,
3,3’-dichloro-U07391-94-
13,3’-DichlorobenzidineUc74764-41-02-Butene,
1,4-dichioro-
(I, T)U074764-41-
01,
4-Dichloro-2-butene
(I, T)U07575-7l-8DichlorodifluoromethaneUo7575-71-
8Methane, dichlorodifluoro-U07675-34-3Ethane,
1, l-dichloro-U07675-34-3Ethylidene
dichlorideU077l07-06-2Ethane, 1, 2-dichloro-U077107-06-2Ethylene
dichlorideU07875-35-4l, 1-Dichloroethyleneuo7875-35-4Ethene,
1, l-dichloro
U079l56-60-51,2-DichloroethyleneUo79l56-60-5Ethene,
l,2-dichloro-,
(E)-U08075-
09-2Methane, dichloro-U08075-09-2Methylene chlorideUo8ll2o-83-22,
4-
DichlorophenolUo8ll2o-83-2Phenol,
2,4-dichloro-U08287-65-02,6-
DichlorophenolUO8287-65-OPhenol,
2,6-dichloro-U08378-87-SPropane,
1,2-dichloro-
U08378-87-5Propylene
dichlorideUO84542-75-61, 3-DichloropropeneuO84542-75-61-
Propene,
l,3-dichloro-U085l464-53-52,2-BioxiranetJQB5l4E4-53-5l,2:3,4-
Diepoxybutane
(I, T)U0861615-80-1N,N
-DiethylhydrazineUO86l6l5-80-lHydrazine,
1, 2-diethyl-U0873288-58-20,O-Diethyl
S-methyl dithiophosphateuO873288-58-
2Phosphorodithioic acid,
0,0-diethyl S-methyl esterUO8BB4-66-21,2-
Benzenedicarboxylic acid,
diethyl esterUO8884-66-2Diethyl phthalateUo8956-53-
lDiethylstilbestroluO8956-53-lPhenol,
4,4
T
-(l,2-diethyl-1,2-ethenediyl)bis-,
(E)
-U09094-58-61,3-Benzodioxole,
5-propyl-U09094-58-EDihydrosafroleUO9lll9-90-
4(l,l’-Biphenyl)-4,4-diamine, 3,3’-dimethoxy-U091119-90-43,3’-
DimethoxybenzidineUO92l24-40-3Dimethylamine
(I)U092124-40-3Methanamine,
N-
methyl-
(I)U09360-1l-7Benzenamine,
N,N-dimethyl-4-(phenylazo)-U09360-ll-7p-
DimethylaminoazobenzeneUO9457-97-6Benz(a)anthracene,
7,12-dimethyl-U09457-97-
67,l2-Dimethylbenz(a)anthraceneuO95ll9-93-7(l,1’-Biphenyl)-4,4’-diamine,
3,3’-
dimethyl-U095119-93-73,3’-DimethylbenzidineUO968O-15-9?,
?-
Dimethylbenzylhydroperoxide
(R)U09680-15-9Hydroperoxide, l-methyl-l-phenylethyl
(R)U09779-44-7Carbamic chloride,
dimethyl-U09779-44-7Dimethylcarbamoyl
chlorideUO9857-14-71,l-DimethylhydrazineuO9857-14-7Hydrazine, 1,1-dimethyl-
U099540-73-81,
2-DimethylhydrazineUO9954O-73-8Hydrazine, 1, 2-dimethyl-Ul01105-67-
92,4-DimethylphenolulOllO5-67-9Phenol,
2,4-dimethyl-Ul02131-ll-3l,2-
Benzenedicarboxylic acid, dimethyl
esterUlO2l3l-ll-3Dimethyl phthalateUlO377-78-
lDimethyl
sulfateUlO377-78-lSulfuric
acid, dimethyl esterUlO5l2l-14-2Benzene,
1-
methyl-2,4-dinitro-Ul05121-l4-22,4-DinitrotolueneUlo66O6-20-2Benzene, 2-methyl-
l,3-dinitro-U106606-20-22,
6-DinitrotolueneUlO7ll7-84-Ol,2-Benzenedicarboxylic
acid,
dioctyl esterUlO7ll7-84-ODi-n-octyl
phthalateUlOBl23-91-ll, 4-
DiethyleneoxideUlO8l23-91-ll,4-DioxaneUlO9l22-66-71,2-DiphenylhydrazineUlO9l22-
66-7Hydrazine, 1, 2-diphenyl-U110142-84-7Dipropylamine
(I)U110142-84-71-
Propanamine, N-propyl- (I)Ul1162l-64-7Di-n-propylnitrosamineUlll62l-64-7l-
Propanamine, N-nitroso-N-propyl-U112141-78-6Acetic
acid, ethyl ester
(I)U112l41-
78-6Ethyl acetate (I)U113140-88-5Ethyl acrylate
(I)U113l40-88-52-Propenoic
acid,
ethyl ester
(I)U114P
lll-54-GCarbamodithioic acid,
l,2-ethanediylbis-, salts
and
estersUll4P lll-54-6Ethylenebisdithiocarbamic acid,
salts and estersUll575-21-
8Ethylene oxide
(I, T)U11575-21-8Oxirane (I, T)U1l696-45-
7EthylenethioureaUll696-45-72-ImidazolidinethioneTJll76O-29-7Ethane,
1,1’ -oxybis
(I)Ul1760-29-7Ethyl etherUll897-63-2Ethyl
methacrylateull897-63-22-Propenoic
acid, 2-methyl-, ethyl esterUll9G2-50-OEthyl methanesulfonateUll962-50-
OMethanesulfonic acid, ethyl
esterUl2O2O6-44-OFluorantheneUl2l75-69-4Methane,
trichlorofluoro-U12175-69-4TrichloromonofluoromethaneUl225O-OO-
OFormaldehydeUl2364-18-EFormic acid
(C, T)U1241l0-OO-9Furan
(I)U124110-OO-
9Furfuran (I)U12598-O1-l2-Furancarboxaldehyde (I)Ul2598-Ol-lFurfural
(I)U126765-
34 -4GlycidylaldehydeUl267G5-34 -4OxiranecarboxyaldehydeUl27ll8
-74- lBenzene,
hexachloro-U127118-74-lHexachlorobenzeneUl2887-68-3l,3-Butadiene,
1,1,2,3,4,4-
hexachloro-U12887-68-3HexachlorobutadieneUl2958-89-9Cyclohexane,
1,2,3,4,5,6-
hexachioro-,
(l?,2?,3?,4?,5?,6?)-U12958-89-9LindaneUl3O77-47-41,3-
Cyclopentadiene, 1,2,3,4,5,5-hexachloro-U13077-47-
4HexachlorocyclopentadieneUl3l67-72-lEthane,
hexachloro-Ul3167-72-
lHexachloroethaneUl327O-30-4Hexachloropheneul327O-30-4Phenol, 2,2’ -
methylenebis(3,4,6-trichloro-U133302-Ol-2Hydrazine
(R, T)U1347664-39-
3Hydrofluoric acid
(C,
T)U1347664-39-3Hydrogen
fluoride
(C, T)U1357783-06-
4Hydrogen su1fideU1357783-06-4Hydrogen sulfide
H25U13675-60-5Ars±nic acid,
dimethyl-U13675-60-5Cacodylic
acidUl37l93-39-5lndeno(l,2,3-cd)pyreneUl3874-88-
4Methane, iodo-Ul3874-88-4Methyl
iodideUl4O7B-83-llsobutyl
alcohol
(I, T)U14078-
83-11-Propanol, 2-methyl-
(I, T)U141120-58-ll,3-Benzodioxole,
5-(l-propenyl)-
U141120-58-lIsosafroleUl42l43-50-OICeponeUl42l43-50-Ol,3,4-Metheno-2H-
cyclobuta(cd)pentalen-2-one,
l,la,3,3a,4,5,5,5a,5b,6-decachlorooctahydro-
U143303-34-42-Buterioic acid,
2-methyl-, 7- ((2,3-dihydroxy-2-
(l-methoxyethyl)-3-
methyl-l-oxobutoxy)methyl)-2,3,5,7a-tetrahydro-1H-pyrrolizin-1-yl
ester,
(lS
(l?(z),
7(2S*,3R*),
7a?))-Ul43303-34-4LasiocarpeneUl443Ol-04-2Acetic acid,
lead
(2+)
saltUl443Ol- 04-2Lead acetateUl457446-27-7Lead
phosphateUl45744s-27-
7Phosphoric acid, lead
(2+)
salt
(2:3)U146l335-32-6Lead,
bis(acetato
O)tetrahydroxytri-Ul46l335-32-6Lead
subacetateUl47lO8-3l-62,5-FurandioneUl47lO8-
31-6Maleic anhydrideUl48l23-33-lMaleic
hydrazideUl48l23-33-l3,6-Pyridazinedione,
l,2-dihydro-U149l09-77-3Malononitrileul49lO9-77-3PropanedinitrileUl5Ol48-82-
3MelphalanUl5Ol48-82-3L-Phenylalanine, 4-(bis(2-chloroethyl)amino)-Ul5l7439-97-
6MercuryUl52l26-98-7Methacrylonitrile
(I,
T)Ul52126-98-72-Propenenitrile,
2-
methyl-
(I, T)Ul5374-93-lMethanethiol (I, T)U15374-93-lThiomethanol
(I,
T)Ul5467-56-lMethanol
(I)U15467-56-lMethyl alcohol (I)U15591-80-51,
2-
Ethanediamine, N,N-dimethyl-N’ -2-pyridinyl-N’ - (2-thienylmethyl)-U15591-80-
5MethapyrileneUl5679-22-lCarbonochloridic acid,
methyl
ester
(I, T)U15679-22-
lMethyl chlorocarbonate
(I, T)U15756-49-5Benz
(j)aceanthrylene,
1, 2-dihydro-3-
methyl-U15756-49-53-MethylcholanthreneUls8lOl-14-4Benzenamine,
4,4’-
methylenebis(2-chloro-Ul5810l-14-44,4’-Methylenebis(2-chloroaniline)U15978-93-
32-Butanone
(I,
T)U15978-93-3Methyl ethyl ketone (MEK)
(I,
T)U1601338-23-42-
Butanone, peroxide
CR,
T)U160l338-23-4Methyl
ethyl ketone peroxide
CR,
T)U161l08-lO-lMethyl isobutyl ketone CI)Ul61108-lO-14-Methyl-2-pentanone
(I)U161108-lO-lPentanol,
4-methyl-U16280-62-GMethyl methacrylate
CI, T)U16280-
62-62-Propenoic acid, 2-methyl-, methyl ester
CI,
T)U16370-25-7Guanidine,
N-
methyl-N’ -nitro-N-nitroso-Ul6370-25-7MNNGU16456- 04-2MethylthiouracilUl6458-
04-
24C1H)-Pyrimidinone, 2,3-dihydro-6-methyl-2-thioxo-U16591-20-
3NaphthaleneUl66l3o-15-41,4-Naphthalenedioneul66l3o--15-41,4-
NaphthoquinoneUl67l34-32-71-NaphthalenamineUl67l34-32-7?-NaphthylamineUl689l-59-
82-NaphthalenamineUl689l-59-8? -NaphthylamineUl6998-95-3Benzene,
nitro-U16998-95-
3Nitrobenzene
(I,
T)Ul70100-02-7p-NitrophenolUl7Oloo-02-7Phenol,
4-nitro-U17179-
46-92-Nitropropane
CI,
T)U17179-46-9Propane, 2-nitro-
CI, T)U172924-l6-31-
Butanamine, N-butyl-N-nitroso-Ul72924-16-3N-N±trosodi-n-butylamineul73lll6-54-
7Ethanol, 2,2’
- Cnitrosoimino)bis-Ul731116-54-7N-NitrosodiethanolaminetJl7455-18-
5Ethanamine, N-ethyl-N-nitroso-U17455-18-5N-NitrosodiethylamineUl76759-73-9N-
Nitroso-N-ethylureaul76759-73-9Urea, N-ethyl-N-nitroso-Ul77684-93-5N-Nitroso-N-
methylureaul77684-93-SUrea, N-methyl-N-nitroso-U1786l5-53-2Carbamic acid,
methylnitroso-,
ethyl
esterUl786l5-53-2N-Nitroso-N-methylurethaneUl79loo-75-4N-
NitrosopiperidineUl79loo-75-4Piperidine, l-nitroso-U180930-55-2N-
NitrosopyrrolidineUl8o93o-55-2Pyrrolidine,
1-nitroso-Ul8199-55-8Benzenamine,
2-
methyl-5-nitro-U18199-55-85-Nitro-o-toluidineUl82l23-63-7ParaldehydeUl82l23-63-
71,3,5-Trioxane,
2,4,6-trimethyl-Ul83608-93-5Benzene,
pentachloro-Ul83608-93-
5Pentachlorobenzeneul8476-Ol-7Ethane,
pentachloro-U18476-01-
7PentachloroethaneUl8582-68-8Benzene,
pentachloronitro-U18582-68-
SPentachloronitrobenzene CPCNB)Ul86504-60-91-Methylbutadiene
(I)U186504-60-91,3-
Pentadiene
(I)U18762-44-2Acetamide, N-C4-ethoxyphenyl)-U18762-44-
2PhenacetinUl88lo8-95-2PhenolUl89l3l4-80-3Phosphorus
sulfide
(R)U189l314-80-
3Sulfur phosphide
CR)U19085-44-91,
3-IsobenzofurandioneUl9085-44-9Phthalic
anhydrideUl9llo9- 06-82 -Picolineul9llo9-
06-8Pyridine, 2-methyl-U19223950-58-
5Benzamide,
3,5-dichloro-N-C1,l-dimethyl-2-propynyl)--Ul9223950-58-
5PronamideUl93ll2O-71-41, 2-Oxathiolane, 2,2-dioxideUl93ll2O-71-41,
3-Propane
sultoneUl94lO7-10-81-Propanamine
CI,
T)U194107-l0-8n-Propylamine
CI, T)U196110-
86-lPyridineUl97lO6-51-4p-Benzoquinoneuls7lo6-51-42,5-Cyclohexadiene-l,4-
dioneU20050-55-5ReserpineU2005O-55-5Yohimban-l6-carboxylic
acid, 11, 17-
dimethoxy-18-
C
(3,4,5-trimethoxybenzoyl)oxy) -, methyl ester,
(3?,16?,17?,18?,20?)-U201108-46-31,3-BenzenediolU2ollo8-46-3ResorcinolU2O2P
81-
07-21,2-Benzisothiazol-3C2H)-one, 1,1-dioxide, and saltsU2O2P 81-07-2Saccharin
and
saltsU2O394-59-71,3-Benzodioxole,
5-C2-propenyl)-U20394-59-7Safro1eU2047783-
00-8Selenious
acidU2047783 -00-8Selenium
dioxideU2O57488-56-4Selenium
sulfideU2O57488-56-4Selen±um
sulfide
SeS2
CR,
T)U20618883-66-4Glucopyranose, 2-
deoxy-2-(3-methyl-3-nitrosoureido)-, D-U20618883-66-4D-Glucose,
2-deoxy-2-
(C
(methylnitrosoamino) -carbonyl)amino) -U20618883-66-4StreptozotocinU2o795-94-
3Benzene,
1,2,4,5-tetrachloro-U20795-94-31,2,4,5-Tetrachlorobenzeneu2O863O-20-
6Ethane, 1,1,l,2-tetrachloro-U208630-20-61,1,l,2-TetrachloroethaneU2O979-34-
5Ethane, 1,1,2,2-tetrachloro-U20979-34-51,1,2,2-TetrachloroethaneU2lOl27-18-
4Ethene, tetrachloro-U210127-18-4TetrachloroethyleneU2ll56-23-5Carbon
tetrachlorideU2ll56-23-5Methane,
tetrachloro-U213l09-99-9Furan,
tetrahydro
(I)U213109-99-9Tetrahydrofuran
(I)U214563-68-8Acetic
acid, thallium
(1+)
saltU2l4563-68-8Thallium
(I)
acetateU2l56533-73-9Carbonic
acid,
dithallium
(1+)
saltU2l56533
-73 -9Thallium
(I)
carbonateU2l6779l-12-OThallium
(I)
chlorideU2l6779l-12-OThallium
chloride
T1C1U21710102-45-lNitric
acid,
thallium
(1+)
saltU2l7lOlO2-45-lThallium
(I)
nitrateU2l862-55-5EthanethioamideU2l862-55-
5ThioacetamideU2l962
-56-GThioureaU22OlO8-
88-3Benzene,
methyl-U220108-88-
3To1ueneU22l25376-45-8Benzenediamine,
ar-methyl-U22125376-45-
8ToluenediamineU222636-21-5Benzenamine,
2-methyl-,
hydrochlorideU222636-21-5o-
Toluidine
hydrochlorideU2232647l-62-5Benzene,
1,
3-diisocyanatomethyl-
CR,
T)U22326471-62-5Toluene
diisocyanate
(R,
T)U22575-25-2BromoformU22575-25-
2Methane,
tribromo-U22671-55-6Ethane,
l,l,l-trichloro-U2267l-55-
U22779-00-5
Ethane,
l,1,2-trichloro-
725.176U22779-O0-5Ethanc,
1,1,2
trichioro
U22779 00
51,1,2-
TrichloroethaneU22879-0l-6Ethene,
trichloro-U22879-0l-6TrichloroethylerieU23499-
35-4Benzene,
l,3,5-trinitro-U23499-35-41,3,5-Trinitrobenzene
(R, T)U235126-72-
71-Propanol,
2,3-dibromo-,
phosphate
(3:l)U235126-72-7Tris(2,3-dibromopropyl)
phosphateU23E72-57-12,7-Naphthalenedisulfonic
acid,
3,3’
- ((3,3
-dimethyl-
(1,1’ -
tetrasodium
saltU23672-57-
lTrypan
blueU23766-75-12,4-
(1H,3H)-Pyrimidinedione,
5-
(bis(2-chloroethyl)amino)-
U23766-75-luracil
mustardU238sl-79-6Carbamic
acid,
ethyl esterU2385l-79-6Ethyl
carbamate
(urethane)U2391330-20-7Benzene,
dimethyl-
(I,
T)U2391330-20-7Xylene
(I)U240P
94-75-7Acetic
acid, (2,4-dichiorophenoxy)-,
salts and estersU24oP
94-
75-72,4-D,
salts
and
estersU243l888-71-7HexachloropropeneU243ls8s-71-71-Propene,
1,1,2,3,3,3-hexachloro-U244137-26-8Thioperoxydicarbonic
diamide
((H2N)C(SH2S2,
tetramethyl—U244137-26-8ThiramU2465O6-68-3Cyanogen
bromide CNBrU24772-43-
SBenzene, 1,1’-(2,2,2-trichloroethylidene)bis(4-methoxy-U24772-43-
5Methoxychlorti248P
81-81-22H-1-Benzopyran-2-one,
4-hydroxy-3-
(3-oxo-1-
phenylbutyl)-,
and salts, when
present
at concentrations
of
0.3 percent or
lessU248P
81-81-2Warfarin,
and salts,
when
present at
concentrations
of 0.3
percent or
1essU2491314-84-7Zinc
phosphide
Zn3P2,
when
present
at concentrations
of 10
percent or 1essU27117804-35-2BenomylU27ll78O4-35-2Carbamic
acid,
(1-
((butylamino)carbonyl)-1H-benzimidazol-2-yl)-,
methyl
esterU27822781-23-
3BendiocarbU27S2278l-23-31,3-Benzodioxol-4-ol,
2,2-dimethyl-, methyl
carbamateU27963-25-2CarbarylU27963-25-21-Naphthalenol,
methylcarbamateU2golol-
27-9BarbanU28OlOl-27-9Carbamic
acid,
(3-chiorophenyl)-,
4-chloro-2-butynyl
esterU32895-53
-4Benzenamine,
2-methyl-U32895-53
-4o-ToluidineU353lO6-49-
OBenzenamine,
4-methyl-U353106-49-Op-ToluidineU359llO-80-5Ethanol,
2-ethoxy-
U3591l0-80-SEthylene
glycol
monoethyl etherU3642296l-82-6Bendiocarb
phenolU3642296l-82-61,
3-Benzodioxol-4-ol,
2,
2-dimethyl-U367l563-38-87-
Benzofuranol,
2,3-dihydro-2,2-dimethyl-U3671563-38-SCarbofuran
phenolU372lO6O5-
21-7Carbamic
acid, 1H-benzimidazol-2-yl,
methyl esterU372lO6OS-21-
7CarbendazimU373l22-42-9Carbamic
acid, phenyl-,
1-methylethyl
esterU373l22-42-
9ProphamU38752888-80-9Carbamothioic
acid, dipropyl-,
5- (phenylmethyl)
esterU38752888-80-9ProsulfocarbU38923O3-17-5Carbamothioic
acid, bis
(1-
methylethyl)-,
S-(2,3,3-trichloro-2-propenyl)
esterU3B923O3-17-
5TriallateU3943OSS8-43
-1A2213U39430558-43
-lEthanimidothioic
acid,
2-
(dimethylamino)-N-hydroxy-2-oxo-, methyl esterU3955952-26-lDiethylene
glycol,
dicarbamateU3955952-26-lEthanol,
2,2’-oxybis-,
dicarbamateU4o4l2l-44-
8Ethanamine,
N,N-diethyl-U404121-44-8TriethylamineU4O923564-05-8Carbamic
acid,
(l,2-phenylenebis(iminocarbonothioyl)
)bis-,
dimethyl esterU40923564-05-
8Thiophanate-methylU4lO59669-26-OEthanimidothioic
acid, N,N’ -
(thiobis(
(methylimino)carbonyloxyHbis-,
dimethyl
esterU4l059669-26-
OThiodicarbU4llll4-26-lPhenol, 2- (l-methylethoxy)-, methylcarbamateU4llll4-26-
iPropoxur
(Source:
Amended at 33 Ill. Reg.
, effective
Section
72l.Appea4xAEENDIX
G
Basis for Listing
Hazardous Wastes
USEPA hazardous waste
No.Hazardous
constituents for which
listedFOOlTetrachloroethylene,
methylene chloride, trichloroethylene, 1,1,1-
trichloroethane,
carbon
tetrachioride, chlorinated
fluorocarbons. FOO2Tetrachloroethylene, methylene chloride, trichloroethylene,
1, l,l-trichloroethane, l,l,2-trichlorethane, chlorobenzene, l,l,2-trichloro-
1,2, 2-trifluoroethane, ortho-dichlorobenzene,
trichlorofluoromethane.FOO3N.A.FOO4Cresols and cresylic
acid,
nitrobenzene.FOO5Toluene, methyl ethyl ketone, carbon disulfide, isobutanol,
pyridine, 2-ethoxyethanol, benzene, 2-nitropropane. FOO6Cadmium, hexavalent
chromium, nickel,
cyanide
(complexed) .FOO7Cyanide
(salts)
.FOO8Cyanide
(salts)
.FOO9Cyanide
(salts)
.FOlOCyanide
(salts)
.FollCyanide
(salts)
.FOl2Cyanide
(complexed) .FOl9Hexavalent chromium, cyanide (complexed) .FO2OTetra- and
pentachlorodibenzo-p-dioxins; tetra- and pentachlorodibenzofurans; tn- and
tetrachlorophenols
and
their clorophenoxy derivative acids, esters, ethers,
amines, and other
salts.FO2lPenta-
and hexachlorodibenzo-p-dioxins;
penta- and
hexachlorodibenzofurans;
pentachlorophenol and its derivatives. FO22Tetra-,
penta- and
hexachlorodibenzo-p-dioxins;
tetra-, penta-, and
hexachlorodibenzofurans . FO23Tetra-
and pentachlorodibenzo-p-dioxins; tetra-
and
pentachlorodibenzofurans;
tn- and tetra- chlorophenols and their chlorophenoxy
derivative acids, esters, ethers,
amines, and other salts.FO24Chloromethane,
dichloromethane, trichloromethane,
carbon tetrachloride, chloroethylene, 1,1-
dichloroethane, 1, 2-dichloroethane,
trans-l, 2-dichloroethylene, 1,1-
dichloroethylene, 1,1, 1-trichloroethane,
1,1, 2-trichloroethane,
trichioroethylene,
1,1,1,
2-tetrachloroethane, 1,1,2, 2-tetrachloroethane,
tetrachloroethylene, pentachloroethane, hexachloroethane, allyl chloride
(3-
chloropropene), dichloropropane, dichloropropene, 2 -chloro-1,
3
-butadiene,
hexachloro- 1, 3 -butadiene, hexachlorochylopentadiene, hexachlorocylohexarie,
benzene, chlorobenzene, dichlorobenzenes, 1,2, 4-trichlorobenzene,
tetrachlorobenzenes, pentachlorobenzene, hexachlorobenzene, toluene,
naphthalene. FO25Chloromethane, dicloromethane, trichloromethane; carbon
tetrachioride;
chloroethylene;
1, l-dichloroethane; 1, 2-dichloroethane; trans
1,2-dichioroethylene; l,l-dichloroethylene;
l,1,l-trichloroethane; 1,1,2-
trichloroethane; trichloroethylene; 1, 1,1,2-tetrachloroethane;
1,1,2,2-
tetrachloroethane; tetrachloroethylene; pentachloroethane; hexachloroethane;
allyl chloride (3-chloropropene); dichloropropane; dichloropropene; 2-chloro-
1,
3-butadiene; hexachloro-l, 3-butadiene; hexachlorocyclopentadiene; benzene;
chlorobenzene; dichlorobenzene; 1,2, 4-trichlorobenzene; tetrachlorobenzene;
pentachlorobenzene; hexachlorobenzene; toluene; naphthalene. FO26Tetra-,
penta-,
and
hexachlorodibenzo-p-dioxins;
tetra-, penta-, and
hexachlorodibenzofurans
. FO27Tetra-,
penta, and hexachlorodibenzo-p-dioxins;
tetra-, penta-,
and hexachlorodibenzofurans;
tn-, tetra-, and
pentachlorophenols
and their chiorophenoxy
derivative acids, esters, ethers,
amines, and
other salts.FO28Tetra-,
penta-, and hexachlorodibenzo-p-dioxins;
tetra-, penta-,
and hexachlorodibenzofurans;
tn-, tetra-, and
pentachlorophenols and their chiorophenoxy derivative acids, esters, ethers,
amines, and
other salts.FO32Benz(a)anthracene;
benzo(a)pyrene;
dibenz
(a,h)
anthracene;
indeno(l,
2, 3-cd)pyrene; pentachlorophenol; arsenic;
chromium;
tetra-, penta-,
hexa-, and heptachlorordibenzo-p-dioxins; tetra-,
penta-,
hexa-, and heptachlorodibenzofurans
. FO34Benz
(a)
anthracene,
benzo(k)
fluoranthene, benzo (a)pyrene,
dibenz
(a,h)
anthracene,
indeno(l,
2,3-
cd)pyrene,
naphthalene, arsenic, chromium.
FO35Arsenic, chromium,
lead. FO37Benzene,
benzo(a)pyrene,
chrysene,
lead, chromium.FO38Benzene,
benzo(a)pyrene,
chrysene,
lead, chromium.F039A11
constituents
for which
treatment
standards
are specified
for multi-source
leachate
(wastewaters
and
nonwastewaters)
under
Table B
to 35 Ill. Adm.
Code
728
(Constituent
Concentrations
in
Waste)
.KOolPentachlorophenol,
phenol,
2-chlorophenol,
p
chloro-m-cresol,
2,4-dimethyiphenol,
2,4- dinitrophenol,
trichlorophenols,
tetrachlorophenols,
2,4- dinitrophenol,
creosote, chrysene,
naphthalene,
fluoranthene,
benzo(b)
fluoranthene,
benzo (a)pyrene,
indeno(l,
2, 3-cd)pyrene,
benz
(a)
anthracene,
dibenz
(a)
anthracene,
acenaphthalene
. KOO2Hexavalent
chromium,
lead.Koo3Hexavalent
chromium,
lead.KOO4Hexavalent
chromium.KOO5Hexavalent
chromium,
lead.KOO6Hexavalent
chromium.KoO7Cyanide
(complexed),
hexavalent
chromium.KOO8Hexavalent
chromium.KOO9Chloroform,
formaldehyde,
methylene
chloride,
methyl
chloride, paraldehyde,
formic
acid.KOlOChloroform,
formaldehyde,
methylene
chloride, methyl
chloride,
paraldehyde,
formic
acid,
chloroacetaldehyde.KOllAcrylonitrile,
acetonitrile,
hydrocyanic
acid.KOl3Hydrocyanic
acid,
acrylonitrile,
acetonitrile.KOl4Acetonitrile,
acrylamide
.
KOl5Benzyl chloride,
chlorobenzene,
toluene,
benzotr±chloride
. KOl6Hexachlorobenzene,
hexachlorobutadiene,
carbon
tetrachloride,
hexachioroethane,
perchioroethylene
. KOl7Epichlorohydrin,
chloroethers
(bis(chloromethyl)
ether and bis- (2-chioroethyl)
ethers),
trichloropropane,
dichloropropanols
.K0l81, 2-dichloroethane,
trichloroethylene,
hexachiorobutadiene,
hexachlorobenzene.
KOl9Ethylene dichloride,
1,1,1-
tr±chloroethane,
1,1,2-trichioroethane,
tetrachloroethanes
(1,1,2,2-
tetrachioroethane
and 1,1,1, 2-tetrachioroethane),
trichloroethylene,
tetrachloroethylene,
carbon tetrachloride,
chloroform,
vinyl
chloride,
vinylidene
chloride.KO2OEthylene
dichloride,
1,1, 1-trichioroethane,
1,1,2-
trichloroethane,
tetrachloroethanes
(1,1,2,
2-tetrachloroethane
and 1,1,1,2-
tetrachioroethane),
trichloroethylene,
tetrachloroethylene,
carbon
tetrachioride,
chloroform,
vinyl chloride,
vinylidene
chloride.KO2lAntimony,
carbon
tetrachloride,
chloroform.KO22Phenol,
tars
(polycyclic
aromatic
hydrocarbons)
.KO23Phthalic
anhydride, maleic
anhydride.KO24Phthalic
anhydride,
1,
4-naphthoguinone
.KO2SMeta-dinitrobenzene,
2,4-dinitrotoluene
.KO26Paraldehyde,
pyridines, 2-picoline.KO27Toluene
diisocyanate, toluene-2,4-diamine.K0281,l,l-
trichloroethane,
vinyl
chloride.K0291,
2-dichioroethane,
1,1, l-trichloroethane,
vinyl
chloride,
vinylidene
chloride, chloroform.
K03 OHexachlorobenzene,
hexachlorobutadiene,
hexachloroethane,
1,1,1,
2-tetrachloroethane,
1,1,2,2-
tetrachioroethane,
ethylene
dichloride
. KO3lArsenic
. KO32Hexachlorocyclopentadiene
. K0331-{exachlorocyclopentadie
ne.KO34Hexachlorocyclopentadiene.KO3sCreosote,
chrysene,
naphthalene,
fluoranthene,
benzo(b)
fluoranthene,
benzo(a)
-pyrene,
indeno (1,2,3-cd)
pyrene,
benzo (a)anthracene,
dibenzo
(a)anthracene,
acenaphthalene.KO36Toluene,
phosphorodithioic
and phosphorothioic
acid esters.Ko37Toluene,
phosphorodithioic
and
phosphorothioic
acid
esters.KO38Phorate,
formaldehyde,
phosphorodithioic
and
phosphorothioic
acid
esters.KO39Phosphorodithioic
and
phosphorothioic
acid
esters.Ko4oPhorate,
formaldehyde,
phosphorodithioic
and
phosphorothioic acid
esters .KO4lToxaphene.KO42Hexachlorobenzene,
ortho-dichlorobenzene.1C0432,
4-
dichlorophenol,
2,
6-dichlorophenol,
2,4,6-
trichlorophenol.K044N.A.K045N.A.KO46Lead.K047N.A.KO48Hexavalent
chromium,
lead.KO49Hexavalent
chromium,
lead.KO5OHexavalent
chromium.KOslHexavalent
chromium,
lead.
KO52Lead . KO6OCyanide,
naphthalene,
phenolic
compounds,
arsenic.
KO6lHexavalent
chromium,
lead,
cadmium.
KO62Hexavalent
chromium,
lead.KO64Lead,
cadmium.KOG5Lead,
cadmium.KO66Lead,
cadmium.KO69Hexavalent
chromium,
lead, cadmium.KO7lMercury.KO73Chloroform,
carbon
tetrachloride,
hexachioroethane,
trichloroethane,
tetrachloroethylene,
dichloroethylene,
1,1,2,
2-tetrachloroethane.KO83Aniline,
diphenylamine,
nitrobenzene,
phenylenediamine.KO84Arsenic
.KO85Benzene,
dichlorobenzenes,
trichlorobenzenes,
tetrachlorobenzenes,
pentachlorobenzene,
hexachlorobenzene,
benzyl
chloride. KOB6Lead, hexavalent chromium.
KO87Phenol, naphthalene
. KO88Cyanide
(complexes)
.KO9OChromium.KO9lChromium.KO93phthalic anhydride,
maleic
anhydride.KO94Phthalic
anhydride.K095l,l,2-trichloroethane,
1,1,1,2-
tetrachloroethane,
l,l,2,2-tetrachloroethane.K096l,2-dichloroethane,
1,1,1-
trichloroethane, 1,1,
2-trichloroethane.KO97chlordane,
heptachlor.KO9sToxaphene.K0992,4-dichlorophenol,
2,4,6-
trichlorophenol . KlOOHexavalent chromium,
lead,
cadmium.KlOlArsenic.KlO2Arsenic .KlO3Aniline,
nitrobenzene,
phenylenediamine . KlO4Aniline, benzene,
diphenylamine, nitrobenzene,
phynylenediamine . KlO5Benzene,
monochlorobenzene, dichlorobenzenes,
2,4, 6-
trichlorophenol . lClO6Mercury.IClll2,
4-Dinitrotoluene.1Cl122, 4-Toluenediamine,
o
toluidine, p-toluidine, aniline.Kll32
, 4-Toluenediamine,
o-toluidine,
p
toluidine, aniline.1Cll42,4-Toluenediamine,
o-toluidine, p-toluidine.Kl152,4-
Toluenediamine . Kll6Carbon tetrachloride,
tetrachloroethylene,
chloroform,
phosgene.Kll7Ethylene dibromide.Kll8Ethylene
dibromide.Kl23Ethylene
thiourea
. Kl24Ethylene thiourea
. Kl2sEthylene thiourea. Kl26Ethylene
thiourea.Kl3lDimethyl sulfate,
methyl bromide.Kl32Methyl
bromide .Kl36Ethylene
dibromide.Kl4lBenzene,
benz
(a)
anthracene, benzo(a)pyrene,
benzo(b)
fluoranthene,
benzo(k)
fluoranthene, dibenz
(a,h)
anthracene, indeno(l,
2,3-cd)
pyrene.ICl42Benzene,
benz
(a)anthracene, benzo
(a)pyrene,
benzo(b)
fluoranthene,
benzo(k)
fluoranthene,
dibenz (a,h) anthracene, indeno(l,
2, 3-cd)pyrene.Kl43Benzene,
benz
(a)anthracene,
benzo(b)
fluoranthene,
benzo(k)
fluoranthene.Kl44Benzene, benz
(a)anthracene,
benzo(a)pyrene,
benzo(b)
fluoranthene,
benzo(k)
fluoranthene,
dibenz
(a,h)anthracene.Kl45Benzene,
benz
(a)anthracene,
benzo(a)pyrene,
dibenz
(a,h)
anthracene, naphthalene.Kl47senzene,
benz
(a)anthracene,
benzo (a)pyrene,
benzo(b)
fluoranthene,
benzo(k)
fluoranthene,
dibenz
(a,h)anthracene, indeno(l,
2,3-cd)
pyrene.Kl48Benz
(a)anthracene,
benzo(a)pyrene,
benzo(b)
fluoranthene,
benzo(k)
fluoranthene,
dibenz
(a,h)anthracene, indeno(l,
2,
3-cd)pyrene.Kl49Benzotrichloride, benzyl
chloride, chloroform, chloromethane,
chlorobenzene, 1, 4-dichlorobenzene,
hexachlorobenzene, pentachlorobenzene,
1,2,4, 5-tetrachlorobenzene,
toluene.Kl5OCarbon tetrachioride,
chloroform, chloromethane, 1,4-
dichlorobenzene, hexachlorobenzene,
pentachlorobenzene, 1,2,4,5-
tetrachlorobenzene, 1,1,2, 2-tetrachloroethane,
tetrachloroethylene, 1,2,4-
trichlorobenzene . Kl5lBenzene, carbon
tetrachloride, chloroform,
hexachlorobenzene, pentachlorobenzene,
toluene, 1,2,4, 5-tetrachlorobenzene,
tetrachioroethylene. Icls6Benomyl, carbaryl,
carbendazim, carbofuran, carbosulfan,
formaldehyde, methylene chloride, triethylamine
. Kls7Carbon tetrachloride,
formaldehyde, methyl chloride, methylene
chloride, pyridine,
triethylamine . Kl5SBenomyl, carbendazim, carbofuran,
carbosulfan, chloroform,
methylene chloride.Kls9Benzene, butylate, EPTC, molinate,
pebulate,
vernolate
. Kl6lAntimony,
arsenic, metam- sodium,
ziram.Kl69Benzene.Kl7OBenzo(a)pyrene,
dibenz(a,h)anthracene,
benzo
(a)
anthracene, benzo
(b)
fluoranthene,
benzo(k)
fluoranthene,
3-methyicholanthrene,
7,
12-dimethylbenz
(a)
anthracene .Kl7lBenzene,
arsenic.Kl72Benzene,
arsenic.K174l,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin
(l,2,3,4,6,7,8-HpCDD),
l,2,3,4,6,7,8-heptachlorodibenzofuran
(l,2,3,4,6,7,8-HpCDF) , 1,2,3,4,7,8,9-
heptachlorodibenzofuran
(1,2,3,6,7,8,
9-}-IpCDF),
all hexachlorodibenzo-p-dioxins
(HxCDD5), all hexachlorodibenzofurans (I-{xCDF5),
all pentachlorodibenzo-p-dioxins
(PeCEDs), 1,2,3,4,6,7,8,9-octachlorodibenzo-p-dioxin
(OCDD),
1,2,3,4,6,7,8,9-
octachlorodibenzofuran
(OCDF),
all
pentachlorodibenzofurans
(PeCDF5),
all
tetrachlorodibenzo-p-dioxins
(TCDD5),
all
tetrachlorodibenzofurans
(TCDF5)
.ICl7SMercury.Kl76Arsenic,
lead.Kl77Antimony.Kl78Thallium.KlslAniline,
o
anisidine,
4-chioroaniline,
p-cresidine, 2,4-dimethylaniline,
1,2
-phenylenediamine,
1, 3 -phenylenediamine.
N.A. -— Waste
is hazardous
because it fails the
test for the characteristic
of
ignitability,
corrosivity,
or reactivity.
e
(Source:
Amended
at 33 Ill. Reg.
—,
effective
Section
721.AppendixAEPENflIX
Y
Table
to
Section
721.138
Chemical
nameCAS
NoComposite value
(mg/kg)Heating
value
(BTU/lb)ConccntrationConcentra-tion
limit (mg/kg
at
10,000 Btu/lb)Minimum
required
detection limit
(mg/kg)Total
Nitrogen
as
NNA9,00018,4004,900Total
Halogens
as
C1NAC1NA1,000l8,40054OTotal
Organic Halogens
as
C1NA
C1NA--
(Note
1)
Polychlorinated
biphenyls,
total
(Arocolors,
total)
l336-36-3N0-—NDl.4Cyanide,
totals7-l2-5N0-—ND1.OMetals:
Antimony,
total744o-36-OND-—12
Arsenic,
total744O-38-2N0-—0.23
Barium, total744O-39-3ND-——23
Beryllium,
total744o-41-
7ND-—l.2
Cadmium,
total744O-43-9-—ND1.2
Chromium,
total744O-47-3ND-—
2.3
Cobalt744O-48-4ND-—4.6
Lead, tota17439-92-157l8,lOO3l
Manganese7439-
96-SND-—l.2
Mercury,
total7439-97-6ND---—0.25
Nickel,
total744o-02-
010618,40058
Selenium,
total7782-49-2ND-—0.23
Silver,
total744O-22-4ND-—
—2.3
Thallium, total744O-28-OND--—23Hydrocarbons:
Benzo(a)anthracenes6-55-
3ND-——2,400
Benzene7l-43-28,000l9,6004,100
Benzo(b)fluoranthene2os-99-2N0-—
—2,400
Benzo(k)fluoranthene2o7-08-9ND- 2,400 Benzo(a)pyrene50-32-
8ND--—--2,400
Chrysene2l8-0l-9ND-—2,400
Dibenzo(a,h)anthracenes3-70-3ND-—
2,400 7,122.4007.l2-Dimethylbenz(a)-anthracenes7-97-6ND-—2,400
Fluoranthene2o6-44-OND---—2,400
Indeno(l,2,3-cd)pyrenel93-39-SND-
2,400
32.4003-Methylcholanthrenes6-49-5ND-—2,400
Naphthalene9l-20-
36,20019,4003,200
Toluenelo8-88-369,
00019,40036,
0000xygenates:
Acetophenone98-86-2ND-—2,400
Acroleinlo7-02-8ND-—-39
Allyl alcohollo7-18-6N0-—
30
Bis (2-ethylhexyl)phthalate
(Di-2-cthylhcxylethvl-
hexvl
phthalate)
117-
81-7ND-—2,400
Butyl
benzyl phthalate8s-68-7ND-—2,400
o-Cresol
(2-Methyl
phenol)95-48-7ND-
2,400
2.4002m-Cresol
(3-ri cthylj
phenol) 108-39-4ND-—
2,400
p-Cresol
(4-Methyl
phenol) 106-44-SND-—2,400
Di-n-butyl
phthalate84-74-
2ND-—2,400
Diethyl phthalates4-66-2ND-
2,400
-
7
-4-2.4002.4-Dimethylphenoll05-
67-9ND-—2,400
Dimethyl phthalatel3l-ll-3ND--—-2,400
Di-n-octyl
phthalatell7-84-OND-——2,400
Endothalll4s-73-3ND-——lOO
Ethyl
methacrylate97-63-2ND-
39
-flZ-Ethoxyethanol
(Ethylene
glycol
monoethyl
ether)
llO-80-SND-----l00
Isobutyl
alcohol78-83-1ND-——39
Isosafrolel2o-58-
1ND-—2,400
Methyl
ethyl ketone
(2- Butanone)78-93-3ND-—-—39
Methyl
methacrylateso-62-6ND-
39
-
7
439l.4-Naphthoquinonel30-l5-4ND--—2,400
Phenollo8-95-2ND-—2,400
Propargyl
alcohol
(2-Propyn-1i-e-kQJjlO7-l9-7ND-—
30.
lQSafrole94-59-7ND-—---2,400Sulfonated
Organics:
Carbon
disulfide7s-l5-OND-
—ND39
Disulfoton298-04-4ND-—ND2,400
Ethyl methanesulfonate62-50-OND-
—ND2,
400
Methyl
mcthancsulfonatcmethane-sulfonate66-27-3ND-—ND2,
400
Phorate298-02-2ND-—ND2,400
t-
1
-12.400l.3-Propane
sultonell2o-71-4ND-
ND100
TctracthyldithiopyrophosphatcNfllooTetraethvldithioovro-
ohosohate
(Sulfotepp)3689-24-SND-——ND2,400
Thiophenol
(BenzcncthiolBenzene-
thiol)l08-
98-SND-——ND3O
0,0,0-Triethyl
phosphorothioatel26-68-1ND-—
ND2,400Nitrogenated
Organics: Acetonitrile
(Methyl
cyanide)75-05-8ND-—ND-9
-192-Acetylaminofluorene
(2-AAF)53-96-3ND-—ND2,4oo
Acrylonitrilelo7-l3-1ND-—
ND34
432A-Aminobiphenyl92-67-1ND-—ND2,
400
42.4004-AminopyridineSo4-24-SND-
—ND100
Aniline62-53-3ND-——ND2,400
Benzidine92-87-SND-—-—-ND2,400
Dibenz(a,j)acridine224-42-OND-—ND2,400
0,0-Diethyl
0- pyrazinyl
phophoro
thioate
(Thionazin)297-97-2ND-—ND2,400
Dimethoate6o-Sl-SND-—-ND2,400
p
(Dimethylamino)
azobcnzcnc
(‘1
Dimcthylaminoazobcnzcncazo-
benzene (4-Dimethvl-
aminoazobenzene)60-ll-7ND-—ND2,400
ND2, 400 a, a
Dimcthylphcncthylaminca.
a-Dimethvlohenethvl-
aminel22-09-8ND-----
ND2,400
3,3’ DimothoxybcnzidincND2.4003.3’-Dimethoxv-
benzidinell9-90-4ND--—
NDi-0-G
a--3jQ-Dinitrobenzene
(m- Dinitrobenzene)99-65-OND-—ND2,400
4,6-Dinitro-o-cresols34-52-1ND-—ND2,400
-
7
42.4002.4-Dinitrophenol5l-28-5ND-----—
ND2, 400
e-r42.4002_.4-Dinitrotoluenel2l-l4-2ND-—---ND2,400
-7--6-2
.4002.6-
DinitrotolueneE06-20-2ND-—ND2,400
Dinoseb
(2-sec-Butyl-4,6-dinitrophenol)88-
85-7ND-—ND2,400
Diphenylaminel22-39-4ND-—ND2,400
Ethyl carbamate
(Urethane)
51-79-6ND-—ND100
Ethylenethiourea
(2-Imidazolidinethione)96-45-7ND-
—ND11O
Famphur52-85-7ND-—ND2,400
Methacrylonitrilel26-98-7ND--—ND39
Methapyrilene9l-80-5ND-—ND2,400
Methorny1l6752-77-5ND-—ND
-51Z-
Methyllactonitrile
(Acetone
cyanohydrin
)
75-86-5ND-—ND100
Methyl
parathion298-
00-0ND-—ND2,400
MNNG
(N-Metyl-N- nitroso-N’
-nitroguanidincnitro-
auanidine)70-
25-7ND-—NDI-l-0-
ll0l-Naphthylamine
(?
Naphthylaminel
(a-Naothvlamine)
134-32-
7ND-—ND2,400
-2.4002-Naphthylam±ne
(-I-
Naphthylamine)91-59-8ND-—
ND2,400
Nicotine54-ll-5ND-—-—ND-G-G
4l004-Nitroaniline
(p
Nitroaniline)l00-Ol-6ND-—ND2,400
Nitrobenzene98-95-3ND-—ND2,400
Nitrophenol
(p-
Nitrophenol)l00-02-7ND-—ND2,400
&2.4005-Nitro-o-
toluidine99-55-8ND-—ND2,400
N-Nitrosodi-n-butylaminebutvl-_amine924-16-3ND-------
ND2,400
N-Nitrosodiethylamine55-18-5ND-
ND2,
400
N Nitrociodiphcnylaminc
(DiphcnylnitrozamincND2
400N-Nitrosodiohenvl-
amine.
(Diohenvi- nitrosamine)
86-
30-6ND-—ND2,400
N-Nitroso-N-mcthylcthylamincmethvl-_ethylaminelo595-95-6ND-—ND2,400
N
Nitrosomorpholine59-89-2ND-—ND2,400
N-Nitrosopiperidineloo-75-4ND-—
ND2,400
N-Nitrosopyrrolidine93o-55-2ND-—ND2,’lOO
-2.4002--Nitropropane79-46-
9ND-—ND3O
Parathion56-38-2ND-—ND2,400
Phenacet±n62-44-2ND-—ND2,400
--42
40Ol.
4-Phenylene
diamine, (p-PhcnylcncdiamincPhenvlene-diamine)
106-50-3ND-—
—ND2,400
N-Phenylthioureal03-85-5ND------ND
51Z-Picoline
(alpha
Picoline)109-06-8ND--—ND2,400
Propythioracil
(6-
Propyl-2-thiouracil)51-52-5ND-—
—ND100
Pyridinello-86-1ND-—ND2,400
Strychnine57-24-9ND-—ND100
Thioacetamide62-55-5ND-—ND57
Thiofanox39l96-l8-4ND------ND100
Thiourea62-56-6ND-—
ND57
Toluene-2,4-diamine
(2,4-Diam±notoluene)95-80-7ND-—ND57
Toluene-2,6-
diamine
(2,6-Diaminotoluene)823-40-5ND------ND57
o-Toluidine95-53-4ND-—
ND2,400
p-ToluidinelO6-49-OND-
ND100 1,3,5
Trinitrobcnzcnc,ND1001.3.5-
Trinitrobenzne
(sym-Trinitrobenzene)
99-35-4ND—-ND2
, 400Halogenated
Organics:—
Allyl
chloridel07--G--lND-—ND39
Aramitel4o-57--8ND-—ND2,400
Benzal
chloride
(Dichloromcthylfli-
chloromethvl
benzene)
98-87-3ND-—ND100
Benzyl
chlorideloo-44-77ND-—ND100
Bis(2-chloroethyl)ether
(Dichloroethyl
ether)
ill
44-4ND-—ND2,400
Bromoform (Tribromomethane)75-25-2ND-—ND39
Bromomethane
(Methyl
bromide)
74-83
-
9ND--—--ND34
419-Bromophenyl
phenyl
ether
(p-BromodiphcnylBromodi-
ohenvl
ether) lol-55-3ND-—ND2,400
Carbon
tetrachloride56-23-SND-—ND39
Chlordane57-74-9ND-—ND14
p-Chloroanilinelo6-
47-8ND-—ND2,400
Chlorobenzenelo8-90-7ND-—ND39
Chlorobenzilate5lo-lS-6ND-
—ND2,400
p-Chloro-m-cresol59-50-7ND-—ND2,400
2.4002-Chloroethy1
vinyl
etherllo-75-8ND-—ND39
Chloroform67-66-3ND-—ND39
Chioromethane (Methyl
chloride)
74-87-3ND-—ND
-2--Chloronaphthalene
(f
-Chlorophthalene)
91-58-
7ND-—ND2,400
-2_4002-Chlorophenol
(o-
Chlorophenol) 95-57-8ND-—ND2,
400
Chloroprene
(2-Chloro-1,3-butadiene)ll26-99-8ND-
ND39
2,4
D
(2,4
Dichlorophcnoxyacctic
acid)ND392.4-D
12.4-Dichioro-
ohenoxvacetic
acid94-75-7ND-
—ND7.
0
Diallate23o3-l6-4ND-—ND2,400
---2-2.400l.2-Dibromo-3-
chloropropanechloro-
orooane96-l2-8ND-—NL34
----Dichlorobenzene
(o
Dichlorobenzene)95-50-1ND-—ND2,400 --32.400l.3-Dichlorobenzene
(m
Dichlorobenzene)541-73-1ND-—N02,400
-r42.400l.4-Dichlorobenzene
(p
Dichlorobenzene)106-46-7ND-—N02,400
--32.4003.3-Dichlorobenzidine9l-94-
1ND-—ND2,
400 DichlorodifluoromcthancDichlorodifluoro-
methane
(CFC-12)
75-71-
8ND-—ND-9
-39l.2-Dich1oroethane
(Ethylene
dichloride)l07-06-2ND-—ND4
--39l._1-Dichloroethylene
(Vinylidene
chloride) 75-35-4ND-—ND39
Dichloromethoxy
ethane (Bis(2-chloroethoxy)
methane) lll-9l-1ND-—ND2,400
--42.4002.4-Dichlorophenoll20-83-2ND-—ND2,400
-r&2.4002.6-Dichlorophenol87-65-
OND-—ND2,400
-r2.400l.2-Dich1oropropane
(Propylene
dichloride)178-87-5ND----
—ND39
cis-l,
3-D-ichloropropylcncDichloro-
orovlenel0061-0l-5ND-—ND39
trans
l,3-DichloropropylcncDichloro-_oronvleneloo6l-02-6ND-—Nfl4
--339l.3-Dichloro-2-
propanol96-23-1ND-—ND3O
Endosulfan 1959-98-8ND------ND1.4
Endosulfan
1133213-65-9ND-—ND1.4
Endrin72-20-8ND-------ND1.4
Endrin
aldehyde742l-93-4ND-—
ND1.4
Endrin
Ketone53494-70-5N]J-—ND1.4
Epichiorohydrin
(1-
Chloro-2,3-epoxy
propane)
106-89-8ND-—ND3O
Ethylidene
dichloride
(l,l-Dichloroethane)75-34-
3ND-—ND-34
-392-F1uoroacetamide640-19-7ND-—NDl00
Heptachlor76-44-8ND-—
ND1.4
Heptachlor
epoxidelo24-57-3ND-—ND2.8
Hexachlorobenzenell8-74-1ND-—
ND2,400
Hexachloro-l, 3-butadicncbuta-
diene
(Hexachlorobutadiene)
87-68-3ND----
—ND2, 400
Hexachlorocyclopentadiene77-47-4ND-—ND2,
400
Hexachloroethane67-
72-1ND-—ND2,
400
Hexachlorophene7o-30-4ND-—ND59,
000
Hexachioropropene
(Hexachloropropylene)l888-71-7ND-—ND2,400
Isodrin465-73-6ND----—ND2,400
Kepone
(Chlordecone)l43-50-OND-—ND4,700
Lindane
(gamma-Hcxachlorocyclohcxanc)
(?
Hexachlorocvclo-
hexane)
(?
-BHC)
58-89-
9ND-—ND1.4
Methylene
chloride
(Dichloromethane)75-09-2ND-—--ND34
4-4394.4
-
methylene-bis(2-
chioroaniline)
lOl-14-4ND-—ND100
Methyl
iodide
(Iodomcthanelodo-
methane)
74-88-4ND-—ND39
Pentachlorobenzene6o8-93-5ND-—
ND2, 400
Pentachloroethane76-0l-7ND-
ND39
PcntpchloronitrobcnzcncND39Pentachloronitro-
benzene
(PCNB)
(Quintobenzene)
(Quintozene)82-68-8ND-—ND2,400
Pentachlorophenol87-86-5ND-—ND2,400
Pronamide2395O-58-5ND-—ND2,400
Silvex
(2,4,5-TrichlorophcnoxropionicTri-
chloroohenoxv-
oraoionic
acid)93-72-1ND-
ND7.0 2,3,7,8
TctrachlorodibcnzoND7.02.
3
.7.8-Tetrachioro-
dibenzo-p-dioxin
(2,3,
7,8-TCDD)
1746-
0l-6ND- ND3-0
1,2,4,5
TctrachlorobcnzencND3pl.2.4.5-Tetrachloro-
benzene95-
94-3ND-
ND2,400 1,1,2,2
TctrachlorocthpncND2.4001.l.2.2-Tetrachloro-
ethane79-
34-5ND--—-ND39
Tetrachioroethylene
(Perchloroethylene)127-18-4ND-
ND39
2,3,4,6
TctrachlorophcnolND392
.3.4.
6-Tetrachioro-
ohenol58-90-2ND-
ND2, 400
l,2,4ND2.4001.2.4-Trichlorobenzene
120-82-1ND-
ND2,400
l,l,1ND2.4001.l.l-
Trichioroethane
(Methyl
chloroform)
7l-55-6ND-—ND
1,1,2391.1.2-
Trichloroethane
(Vinyl
trichloride)
79-00-5ND-—ND39
Trichloroethylene79-0l-
6ND-—ND3
9
Trichiorofluoromethane
(TrichloromonofluoromcthancTrichloromonofluoro
methane)75-69-4ND-—ND34
2,’1,5392.4.5-Trichlorophenol95-95-4ND-
ND2,400
2,4,6ND2.4002.4.
6-Trichlorophenol88-06-2ND-
N02,400
l,2,3N02.4001.2.3-
Trichloropropane96-18-4ND-—ND39
Vinyl
Chloride75-01-4ND—-ND39
NA means
not
applicable.
ND
means
nondetect.
Note
1: 25
(mg/kg at 10,000
Btu/lb)
as
organic
halogen or
as
the
individual
halogenated
organics
listed in the
table
at
the
levels
indicated.
(Source:
Amended at 33
Ill. Reg.
,
effective
Section
72l.Append-xAPPENDIX
Z
Table
to
Section 721.102
Table
l234Use
constituting disposalBurning
for energy
recovery or
use to produce
a
fuelReclamation
(except
as provided
in Section
721.104
(a) (17)
for mineral
processing secondary
materials)Speculative
accumulationApplicable
Subsection
of
Section
721.102:
(c) (1) (c) (2)
(c) (3) Cc)
(4)Spent
matcrialcYcoYccYcoYeoSludgczmaterialsYesYesYesYesSludaes
(listed
in Section
721.131
or
721.
l32)YcoYccYczYczSludgcoYesYesYesYesSludces
exhibiting
a
characteristic
of
hazardous wasteYesYes-
YccEyYesBv-products
(listed
in
Section
P)$W
Z’<wdn—
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F)Q
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Input:
Document 1
ile://l :/Input/35-721
-Agency(issue39).doc
Document
2
file://l:/lnputI35-721
-JCARrOI (issue39).doc
Rendering set
Standard
Legend:
Insertion
Deletion
Moved from
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to
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Inserted cell
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cell
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cell
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Statistics:
Count
Insertions
132
Deletions
349
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0
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to
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481
TITLE
35:
ENVIRONMENTAL
PROTECTION
SUBTITLE
G:
WASTE
DISPOSAL
CHAPTER
I:
POLLUTION CONTROL
BOARD
SUBCHAPTER
C:
HAZARDOUS
WASTE
OPERATING
REQUIREMENTS
PART
724
STANDARDS
FOR
OWNERS
AND
OPERATORS
OF
HAZARDOUS
WASTE
TREATMENT,
STORAGE,
AND
DISPOSAL FACILITIES
SUBPART
A:
GENERAL
PROVISIONS
Section
724.101
Purpose,
Scope,
and
Applicability
724.103
Relationship
to
Interim
Status
Standards
724.104
Electronic
Reporting
SUBPART
B:
GENERAL
FACILITY
STANDARDS
Section
724.110
Applicability
724.111
USEPA
Identification
Number
724.112
Required
Notices
724.113
General
Waste
Analysis
724.114
Security
724.115
General
Inspection
Requirements
724.116
Personnel
Training
724.117
General
Requirements
for
Ignitable,
Reactive,
or
Incompatible
Wastes
724.118
Location
Standards
724.119
Construction
Quality
Assurance
Program
SUBPART
C:
PREPAREDNESS
AND
PREVENTION
Section
724.130
Applicability
724.131
Design
and
Operation
of
Facility
724.132
Required Equipment
724.133
Testing
and
Maintenance
of
Equipment
724.134
Access
to
Communications
or
Alarm
System
724.135
Required
Aisle
Space
724.137
Arrangements
with
Local
Authorities
SUBPART
D:
CONTINGENCY
PLAN
AND
EMERGENCY
PROCEDURES
Section
724.150
Applicability
724.151
Purpose
and
Implementation
of
Contingency
Plan
724.152
Content
of
Contingency
Plan
724.153
Copies
of
Contingency
Plan
724.154
Amendment
of
Contingency
Plan
724.155
Emergency
Coordinator
724.156
Emergency
Procedures
SUBPART
E:
MANIFEST
SYSTEM, RECORDKEEPING
AND
REPORTING
Section
724.170
Applicability
724.171
Use
of
Manifest
System
724.172
Manifest
Discrepancies
724.173
Operating Record
724.174
Availability,
Retention, and Disposition
of Records
724.175
Annual
Facility
Activities 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
Program
724.201
Corrective Action
for Solid Waste Management
Units
SUBPART
G:
CLOSURE AND POST-CLOSURE
CARE
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 Care Plan;
Amendment of Plan
724.219
Post-Closure Notices
724.220
Certification of Completion
of Post-Closure Care
SUBPART H:
FINANCIAL REQUIREMENTS
Section
724.240
Applicability
724.241
Definitions of Terms
as Used in This Subpart
724.242
Cost Estimate for Closure
724.243
Financial Assurance for Closure
724.244
Cost Estimate for Post-Closure Care
724.245
Financial Assurance for Post-Closure
Care
724.246
Use of a Mechanism for Financial Assurance
of Both Closure and Post-
Closure Care
724.247
Liability Requirements
724.248
Incapacity of Owners
or Operators, Guarantors,
or Financial
Institutions
724.251
Wording of the Instruments
SUBPART I:
USE AND MANAGEMENT OF CONTAINERS
Section
724.270
Applicability
Condition
of
Containers
Compatibility
of
Waste
with Container
Management of
Containers
Inspections
Cont
a ± nment
Special
Requirements for
Special Requirements
for
Closure
Air Emission Standards
SUBPART
J:
TANK SYSTEMS
Applicability
Assessment
of Existing
Tank System
Integrity
Design
and Installation
of New Tank
Systems
or
Containment
and Detection
of Releases
General
Operating
Requirements
Inspections
Response
to Leaks or
Spills and
Disposition of
Systems
Closure
and
Post-Closure
Care
Special Requirements
for
Ignitable or Reactive
Waste
Special
Requirements
for
Incompatible
Wastes
Air Emission
Standards
SUBPART
K:
SURFACE IMPOUNDMENTS
Section
724.320
724
.321
724 .322
724.323
724.326
724 .327
724.328
724.329
724.330
724.331
F026,
and
724 .332
Applicability
Design and
Operating Requirements
Action Leakage
Rate
Response
Actions
Monitoring
and Inspection
Emergency
Repairs;
Contingency
Plans
Closure and Post-Closure
Care
Special Requirements
for
Ignitable
or Reactive
Waste
Special
Requirements
for
Incompatible
Wastes
Special
Requirements for
Hazardous
Wastes F020, F021,
F022,
F023,
F027
Air Emission
Standards
Applicability
Design
and
Operating
Requirements
Action Leakage
Rate
Response
Action Plan
Monitoring and
Inspection
Special
Requirements
for Ignitable
or
Reactive Waste
Special
Requirements
for Incompatible
Wastes
Closure and
Post-Closure
Care
Special Requirements
for
Hazardous Wastes
F020, F02l,
F022, F023,
724.271
724.272
724.273
724.274
724.275
724.276
724 .277
724.278
724.279
Ignitable
or
Reactive Waste
Incompatible
Wastes
Section
724.290
724.291
724.292
724.293
724.294
724
.295
724.296
Use Tank
724.297
724.298
724 .299
724.300
Components
Leaking
or
Unfit-for-
SUBPART L:
WASTE
PILES
Section
724 .350
724.351
724.352
724.353
724 .354
724 .356
724.357
724.358
724.359
F026,
and
F027
SUBPART M:
LAND
TREATMENT
Section
724.370
Applicability
724.371
Treatment
Program
724.372
Treatment Demonstration
724.373
Design and Operating
Requirements
724.376
Food-Chain Crops
724.378
Unsaturated Zone Monitoring
724 .379
Recordkeeping
724.380
Closure and Post-Closure
Care
724.381
Special Requirements for
Ignitable or Reactive
Waste
724.382
Special Requirements
for Incompatible Wastes
724.383
Special Requirements
for Hazardous Wastes F020,
F02l, P022, F023,
F026, and F027
SUBPART N:
LANDFILLS
Section
724.400
Applicability
724.401
Design and Operating Requirements
724.402
Action Leakage Rate
724.403
Monitoring and Inspection
724.404
Response Actions
724.409
Surveying and Recordkeeping
724.410
Closure and Post-Closure
Care
724.412
Special Requirements for Ignitable
or Reactive Waste
724.413
Special Requirements for Incompatible
Wastes
724.414
Special Requirements for Bulk
and Containerized Liquids
724.415
Special Requirements for
Containers
724.416
Disposal of Small Containers
of Hazardous Waste in Overpacked
Drums
(Lab Packs)
724.417
Special Requirements for Hazardous
Wastes F020, F02l, P022,
F023,
F026,
and F027
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:
SPECIAL PROVISIONS
FOR CLEANUP
Section
724.650
Applicability of Corrective
Action Management Unit
Regulations
724.651
Grandfathered
Corrective
Action Management Units
724.652
Corrective
Action Management
Units
724.653
Temporary
Units
724.654
Staging Piles
724.655
Disposal of CAMU-Eligible
Wastes in Permitted
Hazardous Waste
Landfills
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
724.702
Monitoring,
Analysis,
Inspection,
Response,
Reporting,
and
Corrective
Action
724.703
Post-Closure
Care
SUBPART
AA:
AIR EMISSION STANDARDS
FOR PROCESS
VENTS
Section
724.930
Applicability
724.931
Definitions
724.932
Standards: Process
Vents
724.933
Standards:
Closed-Vent
Systems
and
Control
Devices
724.934
Test Methods
and Procedures
724 . 935
Recordkeeping
Requirements
724.936
Reporting Requirements
SUBPART
BB:
AIR
EMISSION STANDARDS
FOR EQUIPMENT
LEAKS
Section
724.950
Applicability
724.951
Definitions
724.952
Standards:
Pumps in
Light Liquid Service
724.953
Standards:
Compressors
724.954
Standards:
Pressure Relief
Devices in Gas/Vapor
Service
724.955
Standards: Sampling
Connecting
Systems
724.956
Standards:
Open-ended
Valves or Lines
724.957
Standards:
Valves in
Gas/Vapor or Light
Liquid
Service
724.958
Standards: Pumps,
Valves,
Pressure Relief
Devices,
and Other
Connectors
724.959
Standards:
Delay of
Repair
724.960
Standards:
Closed-Vent
Systems
and
Control
Devices
724.961
Alternative
Percentage Standard
for
Valves
724.962
Skip Period Alternative
for Valves
724.963
Test
Methods and
Procedures
724
. 964
Recordkeeping
Requirements
724.965
Reporting
Requirements
SUBPART
CC:
AIR
EMISSION
STANDARDS FOR TANKS,
SURFACE
IMPOUNDMENTS,
AND
CONTAINERS
Section
724.980
Applicability
724.981
Definitions
724.982
Standards: General
724.983
Waste
Determination
Procedures
724.984
Standards: Tanks
724.985
Standards: Surface Impoundments
724.986
Standards: Containers
724.987
Standards: Closed-Vent Systems and Control Devices
724.988
Inspection
and Monitoring Requirements
724
. 989
Recordkeeping
Requirements
724.990
Reporting
Requirements
724.991
Alternative
Control Requirements for Tanks (Repealed)
SUBPART DD:
CONTAINMENT BUILDINGS
Section
724 .1100
Applicability
724.1101
Design and Operating Standards
724.1102
Closure and
Post-Closure Care
SUBPART EE:
HAZARDOUS WASTE MUNITIONS AND
EXPLOSIVES STORAGE
Section
724.1200
Applicability
724.1201
Design and Operating Standards
724.1202
Closure and Post-Closure Care
724 .AppenthPPENDIX
A Recordkeeping Instructions
724 .Append4APPEND1X
B EPA Report Form and
Instructions (Repealed)
724.Appen44APPEND1X
D Cochran’s Approximation
to the Behrens-Fisher Student’s
T- Test
724.Appen4xAEPEND1X
E Examples of Potentially
Incompatible Waste
724.Append-iAEENDIX
I Groundwater Monitoring
List
AUTHORITY:
Implementing Sections 7.2
and 22.4 and authorized by Section 27 of
the
Environmental Protection Act
[415
ILCS
5/7.2, 22.4, and
271
SOURCE:
Adopted in R82-19
at
7 Ill. Reg. 14059, effective October 12, 1983;
amended
in R84-9 at 9 Ill. Reg. 11964, effective July 24, 1985; amended in
R85-
22 at
10 Ill. Reg. 1136, effective January 2, 1986; amended in R86-l
at
10
Ill.
Reg.
14119, effective August 12, 1986; amended in R86-28 at 11 Ill. Reg. 6138,
effective March 24, 1987; amended in R86-28 at 11 Ill. Reg. 8684, effective
April 21, 1987;
amended
in R86-46 at 11 Ill. Reg. 13577, effective August 4,
1987; amended in R87-5 at 11 Ill. Reg. 19397, effective November 12, 1987;
amended in R87-39 at 12 Ill. Req. 13135, effective July 29, 1988; amended in
R88-16 at 13 Ill. Req.
458, effective
December 28, 1988; amended in R89-l at 13
Ill. Reg.
18527, effective November 13,
1989; amended in R90-2 at 14 Ill. Reg.
14511,
effective August 22, 1990; amended
in R90-l0 at 14 Ill. Reg. 16658,
effective
September 25, 1990; amended
in R90-ll at 15 Ill. Reg. 9654, effective
June 17, 1991;
amended in R9l-l
at
15
Ill. Reg. 14572, effective October 1,
1991; amended
in R9l-13
at
16 Ill.
Reg. 9833, effective June 9, 1992; amended in
R92-l at 16
Ill. Reg. 17702, effective
November 6, 1992; amended in R92-l0 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. Reg. 6973,
effective
April 26, 1994; amended in
R94-7 at 18 Ill. Reg. 12487, effective July
29, 1994;
amended in R94-17
at
18 Ill.
Reg. 17601, effective
November
23, 1994;
amended
in R95-6 at 19 Ill. Req. 9951,
effective June 27, 1995;
amended
in R95-
20 at
20 Ill. Reg. 11244, effective August 1, 1996; amended in R96-l0/R97-3/R97-
5
at 22 Ill. Req. 636, effective December 16, 1997; amended in R98-12
at
22
Ill.
Reg.
7638,
effective April 15, 1998; amended
in
R97-2l/R98-3/R98-5
at 22 Ill.
Reg.
17972,
effective September 28, 1998; amended in R98-21/R99-2/R99-7
at 23
Ill.
Reg. 2186,
effective January 19, 1999;
amended in
R99-15
at 23 Iii. Reg.
9437,
effective July 26, 1999; amended in R00-5
at 24 Iii.
Reg. 1146,
effective
January 6, 2000;
amended in R00-13 at 24 Ill.
Reg. 9833,
effective
June 20,
2000;
expedited
correction at 25 Ill. Reg. 5115, effective June 20,
2000;
amended in
R02-l/R02-l2/R02-17 at 26 Ill. Reg.
6635,
effective April
22, 2002;
amended in
R03-7 at 27 Ill. Reg. 3725, effective February 14, 2003;
amended in
R05-8 at 29 Ill.
Reg.
6009,
effective April
13, 2005;
amended in
R05-2 at 29
Ill. Reg. 6365,
effective April 22, 2005;
amended in
R06-5/R06-6/R06-7
at 30
Ill. Reg. 3196,
effective February 23, 2006;
amended in R06-l6/R06-17/R06-18 at
31 111. Reg. 893,
effective December 20,
2006; amended in R07-5/R07-14 at 32
Ill. Reg. 12365,
effective July 14, 2008; amended in R09-3
at 33 Iii. Reg.
,
effective
SUBPART A:
GENERAL PROVISIONS
Section 724.103
Relationship
to
Interim
Status Standards
A facility
owner or operator that has fully
complied with the
requirements
for
interim status -—
as
defined in Section
3005(e)
of RCRA and regulations under
Subpart C of 35
Ill. Adm.
Code
703,
Subpart C
703
must comply with the
regulations
specified in
35
Iii. Adm.
Code 725 in lieu of the
regulations
in
this Part, until
final administrative
disposition of his permit application is
made, except as
provided under
Subpart S of this Part.
BOARD NOTE: As stated
in
Section
21(f)
of the Illinois Environmental Protection
Act
[415
ILCS
5/21(f)], the treatment,
storage-
7- or disposal of hazardous waste
is prohibited-
7-
except in accordance with
a
RCRA
permit. 35 Iii. Adm. Code 703,
Subpart C
provides for the continued operation of an existing facility
that
meets
certain conditions until final administrative disposition of the
ownerTs
or
operators permit application.
(Source:
Amended at 33 Ill. Reg.
—,
effective
SUBPART
B:
GENERAL FACILITY STANDARDS
Section
724.114
Security
a)
The owner or operator must prevent the unknowing entry, and minimize the
possibility for the unauthorized entry, of persons or livestock onto the active
portion of the facility, unless the owner or operator demonstrates the following
to
the Agency:
1)
That physical contact with the waste, structures or equipment within the
active portion of the facility will not injure unknowing or unauthorized persons
or
livestock that may enter the active portion of a facility; and
2)
That
disturbance of the waste
or equipment, by the unknowing or
unauthorized
entry of persons or livestock onto the active portion
of a
facility,
will not cause
a
violation of the requirements
of this
Part.
BOARD NOTE:
35 111. Adm. Code 703 requires that an owner or operator who
wishes
to
make the
demonstration referred
to above must do so with Part B of the permit
application.
b)
Unless the
owner
or operator has made
a
successful
demonstration under
subsections
(a) (1)
and
(a) (2)
of this Section,
a facility must have the
following:
1)
A 24-hour
surveillance
system
(e.g.,
television monitoring
or
surveillance
by guards or facility personnel) that continuously monitors
and controls entry
onto the active portion of the facility; or
2)
Physical barriers.
A)
An artificial or natural barrier
(e.g., a
fence in
good repair or a fence
combined with a
cliff),
which completely surrounds
the active portion of the
facility; and
B)
A means to control entry,
at
all times, through
the gates or other
entrances
to
the active portion of the facility
(e.g., an attendant, television
monitors, locked entrance, or controlled roadway
access to the facility)
BOARD NOTE: The requirements of subsection
(b)
of this
Section are satisfied if
the facility or plant within which the active portion is located itself
has a
surveillance system, or a barrier and a means
to
control entry, that complies
with the requirements of subsection
(b) (1)
or
(b) (2)
of this Section.
c)
Unless the
owner
or operator has made a successful demonstration under
subsections
(a) (1)
and
(a) (2)
of this Section, a sign with the legend, “Danger-—
— Unauthorized
Personnel
Keep
Out,TT
must be posted at each entrance
to
the
active portion
of
a facility, and at other locations, in sufficient numbers
to
be seen from any
approach
to this active portion. The sign must
be
legible
from
a distance of at
least 25 feet.
Existing signs with a legend other than
“Danger-—
Unauthorized Personnel
Keep Out’ may be used if the legend on the
sign indicates that only authorized personnel are allowed
to
enter the
active
portion, and that entry onto the active portion can
be
dangerous.
BOARD NOTE: See Section
724.217(b)
for discussion of security requirements
at
disposal facilities during the post-closure care period.
(Source:
Amended at 33 Ill. Reg.
—,
effective
SUBPART D:
CONTINGENCY PLAN AND EMERGENCY PROCEDURES
Section
724.154
Amendment of
Contingency Plan
The
contingency plan must
be
reviewed, and immediately
amended, if necessary,
when any of the following occurs:
a)
The facility permit is revised;
b)
The plan fails in an emergency;
c)
The
facility
changes -—
in its design, construction, operation,
maintenance
or other circumstances
-—
in a way that materially increases
the
potential
for fires, explosions
or releases of hazardous waste or hazardous
waste
constituents, or changes
the response necessary in an emergency;
d)
The
list of emergency
coordinators changes; or
e)
The list of emergency equipment
changes.
(Source:
Amended at 33 Iii. Reg.
—,
effective
SUBPART F:
RELEASES FROM SOLID WASTE MANAGEMENT
UNITS
Section
724.194
Concentration Limits
a)
The Agency
must specify in
the facility permit concentration limits in the
groundwater for
hazardous constituents
established under Section 724.193. The
following must be
true of the
concentration of a hazardous constituent:
1)
It must not
exceed the background
level of that constituent in the
groundwater
at
the time that limit is
specified in the permit; or
2)
For any of the constituents listed in Table 1, it must not exceed the
respective value given in that Table if the background level of the constituent
is below the value given in Table 1; or
3)
It must not exceed an alternative limit established
by
the Agency under
subsection
(b)
of this Section.
TABLE 1 -
MAXIMUM CONCENTRATION OF CONSTITUENTS FOR GROUNDWATER
PRpTECTlpNConctitucntMaximumPROTECTlONConstituentMaximum Concentration
(mg/1)Arsenico . O5Bariuml. OCadmiumo . OlChromiumo . O5LeadO . O5Mercuryo . Oo2Seleniumo
.0
lSilvero.O5Endrin
(1,2,3,4,
10,lO-hexachloro-6,7-epoxy-1,4,4a,5,6,7,
8,8a-
octahydro-endo,endo-1,4: 5,8-dimetharionaphthalene)0.0002Lindane
(1,2,3,4,5,6-
hexachlorocyclohexane, gamma
isomer)
0. Oo4Methoxychlor
(1,1,
l-Trichloro-2, 2
T
bis
(p-methoxyphenyl)ethane)
0.
lToxaphene
(Technical
chlorinated camphene, 67-69
percent
chlorine)0.0052,4-D
(2,4-Dichiorophenoxyacetic acid)0.l2,4,5-TP
(Silvex)
(2,4,
5-TrichlorophcnoxypropionicTrichloroohenoxv- orooionic
acid)
0.01
b)
The
Agency must establish an alternative concentration limit for
a
hazardous
constituent if it finds that the constituent will not
pose a
substantial present or potential hazard
to
human health or the environment
as
long
as
the alternative concentration limit is not exceeded. In establishing
alternate concentration limits, the Agency must consider the following factors:
1)
Potential adverse effects on groundwater
quality, considering the
following:
A)
The
physical and chemical characteristics of the waste in the regulated
unit,
including its potential for migration;
B)
The
hydrogeological characteristics of the
facility and
surrounding
land;
C)
The
quantity of groundwater and the direction
of
groundwater flow;
D)
The
proximity and withdrawal rates of groundwater
users;
E) The current and future
uses of groundwater in the area;
F)
The
existing quality of groundwater, including
other sources
of
contamination
and their cumulative impact on the groundwater quality;
G)
The potential for health risks caused by human exposure
to
waste
constituents;
H)
The
potential
damage
to wildlife, crops, vegetation,
and physical
structures caused by exposure to waste constituents;
I)
The
persistence
and permanence of the potential adverse
effects; and
2)
Potential
adverse effects on
hydraulically-connected surface-water
quality,
considering the following:
A)
The volume
and physical and chemical
characteristics of the waste in the
regulated
unit;
B)
The
hydrogeological characteristics
of the facility and surrounding land;
C)
The quantity and quality of groundwater and the direction of groundwater
flow;
D)
The patterns of rainfall in the region;
E)
The proximity of the regulated unit
to
surface waters;
F)
The current and future uses of surface waters in the area and any water
quality standards established for those surface waters;
G)
The existing quality of surface water, including other sources of
contamination and
the
cumulative impact on surface-water quality;
H)
The
potential for health risks
caused by human exposure to waste
constituents;
I)
The
potential damage
to
wildlife,
crops, vegetation, and physical
structures caused by
exposure
to
waste
constituents; and
J)
The
persistence and permanence
of the potential adverse effects.
c)
In
making any determination under
subsection
(b)
of this Section about
the
use of
groundwater in the area around
the facility, the Agency must consider
any
identification of underground sources of drinking
water and exempted aquifers
made under 35
Ill. Adm.
Code
704.123.
d)
The Agency
must make specific
written findings in setting any alternate
concentration
limits under
subsection
(b)
of this Section.
(Source:
Amended
at 33
Ill. Reg.
—,
effective
SUBPART N:
LANDFILLS
Section 724.416
Disposal
of Small Containers of Hazardous Waste in
Overpacked Drums
(Lab
Packs)
Small
containers of hazardous waste
in overpacked drums
(lab
packs) may
be
placed
in
a
landfill if the following requirements
are met:
a)
Hazardous waste must be packaged
in
non-leaking
inside containers. The
inside
containers must be of a design
and
constructed
of a material that will
not
react dangerously with, be decomposed
by, or be ignited by the contained
waste.
The inside containers must
be
tightly
and securely sealed. The inside
containers must be of the size and
type
specified
in the USDOT hazardous
materials
regulations
(49
CFR
173 (Shippers
-—
General
Requirements
for
Shipments
and
Packages), 178
(Specifications
for Packagings),
and 179
(Specifications
for Tank Cars),
each incorporated
by
reference
in
35
Ill. Adm.
Code
720.111(b)),
if those
regulations
specify a
particular inside
container
for
the
waste.
b)
The
inside
containers
must
be
overpacked
in
an
open
head USDOT
specification
metal shipping
container
(49
CFR 178
(Specifications
for
Packagings)
and 179 (Specifications
for
Tank
Cars))
of
no more
than 416 liter
(110
gallon)
capacity
and surrounded
by, at
a minimum, a
sufficient
quantity
of
sorbent material,
determined
to be nonbiodegradable
in
accordance
with Section
724.414(e),
to completely
sorb all
of the liquid
contents
of
the inside
containers.
The metal outer
container
must be full after
packing with
inside
containers
and sorbent material.
c)
In
accordance
with Section 724.117(b),
the
sorbent
material
used must not
be capable
of reacting
dangerously with,
being
decomposed
by,
or being ignited
by
the
contents
of the
inside
containers,
in accordance with
Section 724.117(b).
d)
Incompatible
waste,
as defined
in 35 Iii. Adm.
Code 720.110,
must not
be
placed
in the
same outside
container.
e)
Reactive
wastes,
other
than cyanide-
or sulfide-bearing
waste as defined
in
35
111.
Adm.
Code
721.123
(a)
(5),
must
be
treated
or rendered
non-reactive
prior
to
packaging
in
accordance
with subsections
(a)
through
(d)
of
this
Section.
Cyanide-
and
sulfide-bearing
reactive waste
may be packed in
accordance
with subsections
(a)
through
(d)
of this Section
without first
being
treated
or
rendered
non-reactive.
f)
Such
disposal
is in compliance
with
35
Iii.
Adm. Code 728. Persons
who
incinerate
lab packs
according to 35
Ill. Adm.
Code
728.142(c)
(1)
may
use fiber
drums in
place of metal
outer containers.
Such
fiber
drums
must meet the
USDOT
specifications
in 49 CFR
173.12 (Exceptions
for
Shipments of
Waste Materials),
incorporated
by reference in
35 Ill. Adm.
Code
720.111(b),
and
be
overpacked
according
to
the
requirements
of
subsection
(b)
of
this Section.
g)
Pursuant to
35 111. Adm.
Code 729.312,
the
use
of labpacks
for disposal
of
liquid wastes
or
wastes containing
free liquids
allowed
under
this Section is
restricted
to labwaste
and non-periodic
waste,
as those
terms
are
defined in
that Part.
(Source:
Amended
at 33 111.
Reg.
—,
effective
SUBPART
0:
INCINERATORS
Section
724.440
Applicability
a)
The regulations
in this Subpart
0
apply
to
owners
and operators
of
hazardous
waste
incinerators
(as
defined
in
35
Iii.
Adm.
Code
720.110),
except
as
Section
724.101
provides
otherwise.
b)
Integration
of
the
MACT
standards.
1)
Except
as provided
by subsections
(b) (2)
through
(b) (5)
(b) (4)
of
this
Section,
the
standards of this
Part
do
not apply
to a
new
hazardous waste
incineration
unit
that became
subject to RCRA
permit
requirements
after October
12, 2005; or
no
longer
apply when the
owner or
operator
of
an
existing
hazardous
waste
incineration
unit demonstrates
compliance
with
the maximum
achievable
control
technology
(MACT)
requirements
of
subpart EEE
of
40
CFR
63
(National
Emission Standards
for Hazardous
Air Pollutants
from
Hazardous
Waste
Combustors),
incorporated
by
reference
in 35 Ill.
Adm. Code
720.111(b),
by
conducting a
comprehensive
performance
test and submitting
to the Agency
a
Notification
of Compliance,
pursuant to
40 CFR 63.1207(j)
and
63.1210(d),
documenting
compliance
with
the requirements
of subpart
EEE of 40
CFR 63.—
rrrn
nftr’r t-H’
demonstration of
compliance
,Hth t-hr M
T
’CT
standards, RC
permit
conditions
that
were
based
on
the
standards of
this Part
will
continue
to be in effect
until
they are removed
from the
permit or
the
permit
is
terminated
or revoked,
unless
the permit
expressly provides
otherwise.
2)
The
MACT
standards of subpart
EEE of 40
CFR 63
do not replace
the closure
requirements
of Section
724.451 or
the applicable requirements
of Subparts
A
through H,
BB, and CC
of this Part.
3)
The
particulate
matter
standard of
Section
724.443(c)
remains
in effect
for
incinerators
that elect
to
comply
with
the
alternative
to
the
particulate
matter standard
of
40 CFR
63.1206(b)
(14)
and
63.1219(e)
(When
and How
Must
You
Comply with
the Standards
and Operating
Requirements?),
incorporated
by
reference in 35
Ill. Adm.
Code
720.111(b).
4)
The
following
requirements
remain in
effect for
startup,
shutdown, and
malfunction
events
if the
owner
or operator elects
to
comply with
35 111. Adm.
Code
703.320
(a)
(1)
(A)
to minimize
emissions of toxic
compounds from
the
following events:
A)
Section
724.445(a),
requiring
that
an
incinerator
operate in
accordance
with operating
requirements
specified
in the permit;
and
B)
Section
724.445(c),
requiring compliance
with
the emission
standards
and
operating
requirements
during
startup and shutdown
if
hazardous
waste is in
the
combustion
chamber,
except for particular
hazardous
wastes.
&)-
The
particulate
matter standard of
Section 724.’143”
‘-‘-
inerators unac cicce
to comp±y wiun
une accrnacive
to cat parcicu±ace
matter
standard
of 40 CFR
63.1206(b)
(14)
and
63.1219(e),
incorporated
by
reference
in
35
Ill. Adm. Code
720.111(b)
(as
subpart
EEE of 40 CFR
63)
BOARD NOTE:
Sections
9.1 and 39.5 of the
Environmental
Protection Act
[415
ILCS
5/9.1
and
39.51
make the
federal MACT standards
directly applicable
to entities
in
Illinois
and
authorize
the
Agency to issue
permits based on
the federal
standards.
Operating
conditions
used to determine
effective treatment
of
hazardous
waste
remain
effective after
the owner or operator
demonstrates
compliance
with the
standards
of subpart
EEE of 40 CFR 63.
In adopting this
subsection
(b)
, USEPA
stated
as follows
(at
64 Fed Reg. 52828,
52975 (Sept.
30,1999))
:Seotember
30. 1999)):
Under
this approach
. . .
, MACT
air
emissions and related
operating
requirements
are to be included
in Title
V permits;
RCRA permits
will
continue
to
be
required
for all other aspects
of
the
combustion
unit and the
facility
that are
governed
by RCRA (e.g., corrective
action,
general
facility standards,
other
combustor-specific
concerns such
as
materials handling,
risk-based
emissions
limits
and
operating
requirements,
as
appropriate,
and other
hazardous
waste
management
units)
c)
After
consideration
of the waste
analysis included
with Part B of
the
permit
application,
the Agency,
in establishing
the
permit
conditions, must
exempt
the
applicant from
all requirements
of this Subpart
0, except Section
724.441
(Waste
Analysis)
and Section 724.451
(Closure):
1)
If the Agency finds
that the waste
to be
burned is
one of the
following:
A)
It is
listed as
a hazardous waste
in Subpart
D
of
35 Ill. Adm. Code
721
solely
because it is ignitable
(Hazard
Code
I),
corrosive
(Hazard
Code
C),
or
both;
B)
It is
listed
as a hazardous waste
in
Subpart
D
of 35 Ill. Adm. Code
721
solely because
it is
reactive
(Hazard
Code
R)
for
characteristics
other than
those listed
in Section 721.123
(a)
(4)
and
(5),
and
will not
be burned when
other
hazardous
wastes
are present
in the
combustion
zone;
C)
It is
a
hazardous
waste solely
because it
possesses
the characteristic
of
ignitability,
as
determined
by
the
test for
characteristics
of hazardous
wastes
pursuant
to
Subpart C of
35
Ill. Adm.
Code 721; or
D)
It
is a
hazardous
waste solely
because
it
possesses
any of the
reactivity
characteristics
described
by
35
Ill.
Adm. Code
721.123
(a)
(1), (a) (2), (a)
(3),
(a) (6), (a)
(7),
and
(a) (8)
and will not
be burned
when other
hazardous wastes
are
present
in the combustion
zone; and
2)
If
the
waste
analysis
shows
that the waste
contains
none
of the
hazardous
constituents
listed
in
Subpart H of
35 Ill. Adm.
Code
721 that
would
reasonably
be expected
to be
in
the waste.
d)
If the
waste to be burned
is one that is
described by subsection
(b) (1) (A)
, (b) (1) (B)
, (b) (1) (C)
,
or
(b) (1) (D)
of
this Section and
contains
insignificant
concentrations
of the
hazardous constituents
listed in Subpart
H
of
35
Ill.
Adm. Code
721, then the Agency
may, in establishing
permit
conditions,
exempt the applicant
from all
requirements of this
Subpart 0, except
Section
724.441
(Waste
Analysis)
and Section 724.451
(Closure),
after
consideration
of
the waste analysis
included with
Part B of the permit
application,
unless
the Agency finds
that the waste
will
pose a threat
to human
health or
the
environment
when burned in
an incinerator.
e)
The
owner
or
operator
of
an incinerator
may conduct
trial
burns subject
only to
the
requirements
of
35 Ill.
Adm. Code 703.222
through
703.225
(short-
term and
incinerator
permits)
(Source:
Amended
at 33
Ill. Reg.
—,
effective
SUBPART CC:
AIR EMISSION
STANDARDS
FOR TANKS,
SURFACE
IMPOUNDMENTS,
AND
CONTAINERS
Section
724.982
Standards:
General
a)
This
Section applies
to the management
of hazardous
waste in tanks,
surface
impoundments, and
containers subject
to this
Subpart
CC.
b)
The
owner
or operator must
control air pollutant
emissions from
each waste
management
unit in
accordance with
the standards specified
in Sections
724.984
through
724.987, as
applicable
to the waste
management
unit,
except as provided
for
in
subsection
(c)
of this
Section.
c)
A
tank,
surface impoundment, or container
is exempt from standards
specified in
Sections 724.984 through 724.987,
as applicable, provided that all
hazardous
waste
placed in the waste
management unit is one of the following:
1)
A tank, surface
impoundment, or
container for which all hazardous waste
entering the unit has
an average VO
concentration
at
the point of
waste
origination of less
than
500 parts per million
by
weight (ppmw).
The average VO
concentration must be
determined
by the procedures specified in
Section
724.983(a).
The
owner or operator
must review and update,
as
necessary,
this
determination at least
once every 12
months following the
date
of the initial
determination for
the hazardous waste
streams entering the unit.
2)
A tank,
surface impoundment, or
container for which the organic content
of
all
the
hazardous waste entering the waste
management unit has been reduced
by
an organic destruction or removal process
that achieves any one of the following
conditions:
A)
The
process removes or destroys
the organics contained in the hazardous
waste
to a
level such that the average
VO concentration of the hazardous waste
at the point
of waste treatment is
less than the exit concentration limit
(Ct)
established
for the process. The
average VO concentration of the hazardous
waste at the
point of waste treatment
and the exit concentration limit for
the
process must be
determined using
the procedures specified in Section 724.983(b).
B)
The process
removes or
destroys the organics contained in the hazardous
waste to a
level such that the
organic reduction efficiency
(R)
for the process
is equal to or
greater than
95 percent, and the average VO concentration
of the
hazardous waste at
the point
of waste treatment is less than 100 ppmw. The
organic
reduction efficiency
for the process and the average VO concentration
of
the hazardous waste at
the
point of waste treatment must
be
determined using
the
procedures
specified in Section
724.983
(b)
C)
The
process removes or destroys
the organics contained in the hazardous
waste to
such
a
level that the actual
organic
mass
removal rate
(MR)
for the
process
is equal to or greater than the required organic
mass removal rate (RMR)
established for the process. The required organic mass
removal rate and the
actual organic mass removal rate for the process must
be determined using the
procedures specified in Section 724
. 983
(b)
D)
The process
is
a biological process that destroys or degrades the organics
contained in the
hazardous
waste so that either of the following conditions
are
met:
i)
The organic reduction efficiency
(R)
for the process
is equal to
or
greater than 95 percent, and the organic biodegradation
efficiency
(Rbio)
for
the
process is
equal
to or greater than
95
percent. The organic reduction
efficiency and
the organic
biodegradation efficiency for the process must
be
determined
using the procedures
specified in Section 724
.983
(b)
ii)
The total actual organic mass
biodegradation rate
(MRbio)
for all
hazardous waste treated
by
the process
is equal to or greater than the required
organic
mass removal rate
(RMR)
. The
required organic mass removal rate and
the
actual
organic mass biodegradation
rate for the process must be determined
using
the
procedures specified in Section
724.983(b).
E)
The process removes or destroys the organics
contained in the hazardous
waste and meets
all
of the following conditions:
i)
From the point
of waste
origination through
the point where the hazardous
waste
enters the
treatment
process, the hazardous waste
is continuously managed
in waste management units
that use air emission controls
in accordance
with
the
standards specified in Sections
724.984 through 724.987,
as
applicable
to the
waste management unit.
ii)
From the point of waste origination
through the point where the hazardous
waste enters the treatment process,
any transfer of the hazardous waste is
accomplished through continuous
hard-piping or other closed system transfer
that
does not allow exposure of the
waste to the atmosphere.
BOARD NOTE: The USEPA
considers a drain system that meets the
requirements of federal
subpart RR of 40 CFR 63
(National
Emission Standards
for
Individual Drain Systems)
to be a closed system.
iii) The average
VO
concentration of the hazardous waste
at the point of waste
treatment is less
than
the lowest average VO concentration
at the point of waste
origination, determined for each of the individual
hazardous waste streams
entering the process or 500 ppmw, whichever value is
lower. The average VO
concentration
of each
individual hazardous waste stream
at the point of waste
origination must be determined using the procedures specified in Section
724
. 983
(a)
. The average VO
concentration of the hazardous waste
at
the
point of
waste treatment must
be determined using the procedures specified in
Section
724.983(b).
F)
A process that removes or
destroys the organics contained in the hazardous
waste
to a
level such that the
organic reduction efficiency
(R)
for the process
is
equal
to
or greater than
95 percent and the owner or operator certifies
that
the average VO concentration
at
the point
of waste origination for each of
the
individual waste streams entering the process
is less than 10,000 ppmw. The
organic reduction efficiency for the process
and the average VO concentration
of
the hazardous waste at the point of waste
origination must be determined using
the
procedures specified in Section 724.983(b)
and Section
724.983(a),
respectively.
G)
A hazardous waste incinerator for which
either of the following conditions
is
true:
i)
The owner or operator has been issued
a
final
permit under 35 Ill. Adm.
Code 702, 703, and 705 that implements the requirements
of Subpart H of 35 111.
Adm. Code 726;
or
ii)
The
owner
or
operator
has designed and operates the
incinerator in
accordance
with the interim
status requirements of Subpart
0 of 35 Ill. Adm.
Code
725.
H)
A boiler or industrial
furnace for which either of the following
conditions is true:
i)
The owner or operator has
been issued a final permit under
35
Ill. Adm.
Code 702, 703, and 705 that implements
the
requirements
of Subpart H of 35 Ill.
Adm. Code 726; or
ii)
The
owner or
operator has designed and operates
the boiler or industrial
furnace
in accordance with
the interim status requirements
of Subpart 0 of 35
Ill.
Adm.
Code
725.
I)
For the purpose of determining the
performance of an organic destruction
or removal process in accordance with the
conditions in each of subsections
(c) (2) (A)
through
(c) (2) (F)
of this Section,
the owner or operator must account
for vo concentrations determined
to be
below
the limit of detection of the
analytical method by using the following VO
concentration:
i)
If Method 25D
(Determination
of
the Volatile Organic Concentration of
Waste
Samples)
in appendix A
to
40 CFR
60
(Test Methods),
incorporated
by
reference
in 35
Ill. Adm.
Code
720.111(b),
is used for the analysis, one-half
the blank value determined in
Section 4.4 of the method or a value of 25 ppmw,
whichever is less.
ii)
If any other analytical method is
used, one-half the sum of the limits of
detection established for each organic
constituent in the waste that has
a
Henry
Tslaw constant value at least 0.1
mole-fraction-in-the-gas-phase/mole
fraction-in-the-liquid-phase
(0.1
Y/x) (which
can also be expressed as 1.8
x
10-6 atmospheres/gram-mole/m3)
at
25°
C.
3)
A tank or surface impoundment
used
for
biological treatment of hazardous
waste in accordance with the requirements of
subsection
(c) (2) (D)
of this
Section.
4)
A tank, surface impoundment, or container for which all hazardous
waste
placed in the unit fulfills either of the following
conditions:
A)
It meets the numerical concentration limits
for organic hazardous
constituents, applicable to the hazardous waste,
as specified in Table T
to 35
Ill. Adm. Code 728; or
B)
The organic hazardous constituents in the waste have
been treated by the
treatment technology established by USEPA for the waste,
as set forth in 35 Ill.
Adm. Code
728.142(a),
or have been removed or destroyed
by an equivalent method
of treatment approved by the Agency pursuant
to 35
Ill.
Adm. Code
728.142(b).
5)
A tank used for bulk feed of hazardous waste
to a
waste
incinerator and
all of the
following conditions
are met:
A)
The tank is
located inside
an enclosure vented
to a
control device
that is
designed
and operated in accordance
with all applicable requirements
specified
under
federal subpart FF of 40 CFR
61
(National
Emission Standard for Benzene
Waste
Operations), incorporated
by reference in 35 Ill. Adm.
Code
720.111(b),
for a
facility
at
which the
total annual benzene quantity from the facility
waste is
equal
to
or greater than
10 megagrams
(11 tons)
per year;
B)
The enclosure and control device
serving the tank were installed and
began
operation prior
to
November 25, 1996;
and
C)
The enclosure is designed and
operated in accordance with the criteria
for
a
permanent total enclosure as specified in
T
Procedure
T -— Criteria for and
Verification of a Permanent or Temporary Total Enclosure’
under appendix B to 40
CFR 52.741
(VOM
Measurement Techniques for Capture Efficiency),
incorporated
by
reference
in
35
Ill. Adm.
Code
720.111(b).
The enclosure
may
have
permanent or
temporary
openings
to
allow
worker access; passage of material into or
out of
the
enclosure
by
conveyor, vehicles,
or other mechanical or electrical
equipment; or to direct air flow into
the enclosure. The owner or operator
must
perform the verification procedure for
the enclosure as specified in Section
5.0
to Procedure T -— Criteria for and
Verification of a Permanent
or
Temporary
Total Enclosure’ annually.
d)
The Agency may at any time perform
or request that the owner
or operator
perform
a
waste determination for
a
hazardous
waste managed in
a tank, surface
impoundment, or container that is exempted
from using air emission controls
under the provisions of this Section,
as
follows:
1)
The waste determination for average VO
concentration of
a
hazardous
waste
at the point of waste origination must
be performed using direct measurement
in
accordance with the applicable requirements
of Section 724 . 983
(a)
. The waste
determination for a hazardous waste
at
the
point of waste treatment must
be
performed in accordance with the applicable
requirements of Section 724
. 983
(b)
2)
In performing a waste determination
pursuant to subsection
(d) (1)
of
this
Section, the sample preparation and analysis
must be conducted
as
follows:
A)
In accordance with the method
used by the owner or operator
to
perform
the
waste analysis, except in the
case specified in subsection
(d)
(2) (B) of
this
Section.
B)
If the Agency determines that the
method used by the owner or operator
was
not appropriate for the hazardous waste
managed in the tank, surface
impoundment, or container, then the Agency
may choose an appropriate method.
3)
Where the owner or operator is requested
to perform the waste
determination, the Agency may elect
to
have
an authorized representative
observe
the collection of the hazardous waste samples
used for the analysis.
4)
Where the results of the waste determination
performed or requested
by the
Agency do not agree with the results of
a
waste
determination performed by
the
owner or operator using knowledge of the waste,
then the results of the waste
determination performed in accordance with the requirements
of subsection
(d) (1)
of this Section must be used to establish compliance
with the requirements
of
this Subpart CC.
5)
Where the owner or operator
has used an averaging period greater
than one
hour for determining the average
VO concentration of a hazardous waste
at the
point
of waste origination, the
Agency may elect to establish compliance
with
this
Subpart
CC
by performing or
requesting that the owner or operator
perform
a
waste
determination using direct
measurement based on waste samples
collected
within
a
one-hour period, as follows:
A)
The average VO concentration of
the hazardous waste at the point of
waste
origination must be determined
by
direct measurement
in accordance with
the
requirements of Section 724.983
(a)
B)
Results of the waste determination
performed or requested by the Agency
showing that the average VO concentration
of the hazardous waste
at
the
point of
waste origination is equal to or greater
than 500 ppmw must constitute
noncompliance with this Subpart
CC,
except
in a case as provided for in
subsection
(d) (5) (C)
of this Section.
C)
Where the
average
VO concentration of the hazardous
waste at the point
of
waste
origination previously
has been determined
by the owner or operator using
an
averaging period greater
than one hour
to be
less
than 500 ppmw but because
of
normal operating process variations
the VO concentration
of the hazardous
waste
determined by
direct
measurement for any given
one-hour period may be
equal to or greater
than
500 ppmw, information that was
used by the owner or
operator
to
determine the average VO concentration of the
hazardous waste (e.g.,
test results,
measurements,
calculations, and other documentation)
and recorded
in
the facility
records
in accordance with the requirements
of Section
724.983(a)
and Section 724.989 must
be
considered
by
the
Agency together with
the results of the waste determination performed or requested
by the Agency in
establishing compliance with this Subpart
CC.
(Source:
Amended at 33 Ill. Reg.
—,
effective
Section 724.989
Recordkeeping Requirements
a)
Each owner or operator of
a facility subject to the requirements of this
Subpart
CC
must record and maintain
the information specified in subsections
(b)
through
(j)
of this Section,
as
applicable
to the facility. Except for air
emission control equipment design
documentation and information required
by
subsections
(i)
and
(j)
of this Section,
records required by this Section must
be maintained in the operating record for
a
minimum
of three years. Air
emission control equipment design documentation must
be maintained in the
operating record until the air emission control equipment
is replaced or is
otherwise no longer in service. Information required
by subsections
(i)
and
(j)
of this Section must be maintained in the operating
record for as long as the
waste management unit is not using air emission
controls specified in Sections
724.984 through 724.987, in accordance with the
conditions specified in Section
724.980(d)
or
(b) (7),
respectively.
b)
The owner or operator of a tank using air emission
controls in accordance
with the requirements of Section 724.984 must prepare
and maintain records for
the tank that include the following information:
1)
For each tank using air emission controls in accordance
with the
requirements of Section 724.984, the owner or operator must record the
following:
A)
A
tank identification number
(or
other unique identification description,
as
selected
by
the owner or operator)
B)
A record for each inspection required
by Section 724.984 that includes
the
following information:
i)
Date inspection was conducted.
ii)
For
each defect
detected during the inspection: the location of the
defect, a
description of the defect,
the date of detection, and corrective
action taken
to
repair the defect.
In the event that repair of the defect is
delayed
in accordance with the
requirements of Section 724.984, the owner or
operator must also record the reason
for the delay and the date that completion
of
repair of the defect is expected.
2)
In
addition
to the information required
by
subsection
(b)
(1)
of
this
Section,
the owner or
operator must record the following information,
as
applicable
to
the tank:
A)
The owner or operator using
a fixed roof to comply with the Tank Level 1
control requirements specified in
Section
724.984(c)
must prepare and maintain
records for each determination for
the
maximum
organic vapor pressure of the
hazardous waste
in
the
tank
performed in accordance
with the requirements
of
Section
724.984(c).
The records
must include the
date and time the
samples were
collected,
the
analysis
method used,
and the analysis
results.
B)
The
owner
or operator
using an internal
floating roof
to comply with the
Tank
Level 2
control
requirements
specified in
Section
724.984(e)
must prepare
and
maintain
documentation
describing
the floating
roof design.
C)
Owners
and
operators
using an external
floating roof
to comply with
the
Tank
Level 2
control
requirements
specified
in Section
724.984(f)
must prepare
and maintain
the
following
records:
i)
Documentation
describing the
floating roof design
and the dimensions
of
the tank.
ii)
Records
for each seal gap
inspection required
by
Section
724.984(f)
(3)
describing
the
results
of the seal
gap measurements.
The
records must
include
the date
that
the measurements
were
performed, the raw
data obtained for
the
measurements,
and the
calculations of the
total
gap
surface
area.
In the
event
that
the
seal gap
measurements
do not conform
to
the
specifications
in Section
724.984
(f) (1),
the
records
must
include a description
of
the repairs
that were
made, the
date
the
repairs
were
made, and the
date
the tank was emptied,
if
necessary.
D)
Each
owner
or operator using
an enclosure
to comply
with the
Tank Level
2
control requirements
specified in
Section
724.984(i)
must prepare and
maintain
the following
records:
i)
Records
for the most recent
set of
calculations
and measurements
performed
by
the owner
or
operator
to
verify
that the
enclosure
meets the criteria
of a
permanent
total
enclosure
as
specified in ‘Procedure
T -— Criteria for
and
Verification of
a
Permanent
or Temporary
Total Enclosure”
under appendix
B to 40
CFR
52.741
(VOM
Measurement
Techniques
for Capture Efficiency),
incorporated
by
reference
in 35
Iii. Adm.
Code
720.111(b).
ii)
Records
required
for the closed-vent
system
and
control device in
accordance
with the requirements
of
subsection
(e)
of
this
Section.
c)
The owner
or operator of
a
surface
impoundment
using air
emission
controls
in accordance
with
the requirements
of Section 724.985
must prepare
and maintain
records for
the surface
impoundment
that include
the
following information:
1)
A
surface impoundment
identification
number
(or
other
unique
identification
description as
selected
by
the
owner or operator)
2)
Documentation
describing the floating
membrane
cover
or cover design,
as
applicable
to the
surface
impoundment,
that includes
information
prepared
by the
owner
or
operator
or provided
by the cover
manufacturer
or vendor describing
the
cover
design,
and
certification
by the owner or
operator
that the cover
meets
the
specifications
listed
in
Section
724.985(c).
3)
A record
for each inspection
required
by Section
724.985
that includes
the
following
information:
A)
Date
inspection
was conducted.
B)
For
each defect
detected
during
the
inspection the
following information:
the
location
of
the defect,
a description
of the defect, the
date of detection,
and corrective
action
taken
to
repair
the defect.
In the event
that repair of
the
defect
is
delayed
in accordance
with the provisions
of Section
724.985(f),
the
owner or
operator
must also record
the reason for
the delay and the
date
that
completion
of repair
of the defect
is expected.
4)
For a
surface
impoundment
equipped with
a
cover and vented
through
a
closed-vent
system
to a
control
device, the owner
or operator must
prepare and
maintain
the
records
specified in subsection
Ce)
of
this Section.
d)
The
owner or operator
of containers
using
Container Level
3
air emission
controls
in
accordance with
the requirements
of
Section 724.986
must prepare
and
maintain
records
that include the
following information:
1)
Records for
the
most recent set of
calculations and
measurements performed
by
the owner
or
operator
to verify that the
enclosure meets
the criteria of
a
permanent
total
enclosure
as
specified in
Tprocedure
T-—
Criteria
for and
Verification of
a
Permanent
or Temporary
Total
EnclosureTT
under appendix
B
to
40
CFR 52.741
(VOM
Measurement
Techniques
for Capture Efficiency)
2)
Records
required
for
the closed-vent
system
and
control
device in
accordance
with the requirements
of subsection
Ce)
of
this Section.
e)
The
owner or
operator using
a
closed-vent
system
and control device
in
accordance
with the requirements
of Section
724.987 must
prepare and maintain
records
that include the
following information:
1)
Documentation
for the closed-vent
system
and
control device that
includes
the
following:
A)
Certification
that
is signed and dated
by
the owner or
operator stating
that
the control
device
is
designed
to operate
at the
performance level
documented by
a
design
analysis
as specified in
subsection
Ce) (1) (B)
of
this
Section
or by
performance
tests as
specified in
subsection
Ce) (1)
(C)
of
this
Section
when
the tank, surface
impoundment,
or
container is or
would
be
operating
at
capacity
or the highest
level
reasonably
expected
to
occur.
B)
If a
design analysis
is used, then
design documentation,
as specified
in
Section
724.935(b)
(4).
The
documentation
must include information
prepared
by
the
owner or
operator or provided
by the control
device manufacturer
or vendor
that
describes
the control device
design in accordance
with Section
724.935(b)
(4) (C)
and
certification
by
the owner
or
operator
that the control
equipment
meets the applicable
specifications.
C)
If
performance
tests are
used, then
a
performance
test plan
as specified
in
Section
724.935(b)
(3)
and all
test results.
D)
Information as required
by
Section
724.935
Cc) (1)
and
Section
724.935(c)
(2),
as applicable.
E)
An
owner
or
operator must
record, on
a
semiannual
basis, the
information
specified in
subsections
Ce) (1) CE) Ci)
and
Ce)
(1)
CE) (ii)
of this Section
for
those
planned
routine maintenance
operations
that would
require
the control
device not
to
meet
the requirements
of Section
724 .987
Cc) (1) (A),
Cc) (1) (B),
or
(c)
(1) (C)
of
this
Section, as applicable.
i)
A description
of the planned
routine maintenance
that is anticipated to
be
performed for the
control device
during
the next
six-month
period. This
description must
include the
type of maintenance necessary,
planned frequency of
maintenance,
and lengths
of
maintenance
periods.
ii)
A
description of the planned
routine maintenance
that was performed for
the
control
device during the previous
six-month period.
This description must
include
the type
of maintenance
performed and the total
number of hours during
those six months that the control
device did not meet the
requirements of
Section 724.987
Cc) (1) (A), (c)
(1)
(B)
, or
Cc) (1) (C)
, as applicable, due to planned
routine maintenance.
F)
in owner
or operator
must record the information
specified in subsections
(e) (1) (F) Ci)
through
(e) (1) (F) (iii)
of
this Section for those unexpected control
device system malfunctions that would require
the control device not
to
meet
the
requirements of Section 724.987
(c) (1)
(A),
(c) Cl) (B),
or
(c) (1) (C)
of this
Section, as applicable.
i)
The occurrence and duration of each malfunction
of the control device
system.
ii)
The duration of each period during
a
malfunction
when gases, vapors,
or
fumes are vented from the waste management unit
through the closed-vent system
to the control device while the control device is
not properly functioning.
iii)
Actions
taken during
periods of malfunction
to restore a malfunctioning
control
device
to
its normal
or usual manner of operation.
G)
Records of the management
of carbon removed from
a carbon adsorption
system conducted in accordance
with Section 724.987
Cc)
(3) (B).
f)
The owner or operator of
a tank, surface impoundment, or container
exempted from standards in
accordance with the provisions of Section
724.982(c)
must
prepare and maintain the following
records, as applicable:
1)
For tanks, surface impoundments,
or containers exempted under the
hazardous waste organic concentration
conditions specified in Section
724.982(c) (1)
or
Cc) (2) CA)
through
Cc) (2) CE),
the owner or operator must
record
the
information used for each waste
determination (e.g.,
test
results,
measurements, calculations, and
other
documentation)
in the facility
operating
log.
If analysis results for waste
samples are used for the waste
determination, then the owner
or operator must record the
date, time, and
location that each waste sample
is collected in accordance with
the applicable
requirements of Section 724.983.
2)
For tanks,
surface
impoundments, or containers
exempted under the
provisions
of Section 724.982
Cc) (2) (G)
or
(c)C2)(H),
the
owner or operator must
record the identification number
for the incinerator, boiler,
or industrial
furnace in which the hazardous waste
is treated.
g)
Jn owner or operator designating
a cover as unsafe
to
inspect and
monitor’ pursuant to Section 724.984(1)
or Section 724.985(g) must record
in a
log
that is kept in the facility operating
record the following information:
the identification numbers for waste management
units with covers that are
designated as
“unsafe
to inspect and monitor,”
the explanation for each cover
stating
why
the
cover
is unsafe to inspect
and monitor, and the plan and
schedule for inspecting and monitoring each
cover.
h)
The owner or
operator
of a facility that is subject
to
this Subpart
CC
and
to the control device standards in federal subpart VV of 40 CFR
60
(Standards
of
Performance
for
Equipment
Leaks of VOC in the Synthetic Organic Chemicals
Manufacturing Industry)
or subpart V of 40 CFR 61
(National
Emission Standard
for Equipment Leaks
(Fugitive
Emission
Sources)),
each incorporated
by
reference
in 35 Iii. Adm. Code
720.111(b),
may elect to demonstrate compliance with the
applicable Sections
of
this Subpart CC by documentation either pursuant
to
this
Subpart CC, or pursuant to the provisions of subpart VV of 40 CFR
60
or
subpart
V of 40 CFR 61, to the extent that the documentation required
by
40 CFR
60 or 61
duplicates the documentation required
by
this Section.
i)
For each tank or container not using air emission controls specified
in
Sections 724.984 through 724.987 in accordance with the conditions specified
in
Section
724.980(d),
the owner or operator must record and maintain the following
information:
1)
A list of
the individual
organic peroxide compounds manufactured at the
facility that meet
the conditions
specified in Section
724.980(d) (1).
2)
A
description of how
the hazardous waste containing the organic peroxide
compounds
identified pursuant
to subsection
(i) (1)
of this Section are managed
at the facility
in tanks
and containers. This description must include the
following
information:
A)
For the tanks used at the facility to manage this hazardous waste,
sufficient
information
must be provided to describe the following for each
tank:
a
facility identification number for the tank, the purpose and placement of
this
tank in the management train of this hazardous waste, and the procedures
used to
ultimately dispose of the hazardous waste managed in the tanks.
B)
For containers used at the facility to manage this hazardous waste,
sufficient information must be provided to describe each tank:
a
facility
identification number for the container or group of containers, the purpose
and
placement of this
container
or group of containers in the management train of
this
hazardous waste, and the procedures
used to ultimately dispose of the
hazardous waste managed in the containers.
3)
An explanation of why managing the hazardous waste containing the organic
peroxide compounds identified pursuant to subsection
(i) (1)
of this Section
in
the tanks or containers identified pursuant to subsection
(i) (2)
of this
Section
would create an undue safety hazard if the air emission controls specified
in
Sections 724.984 through 724.987 were installed and operated on these waste
management units. This explanation must include the following information:
A)
For tanks used at the facility to manage this hazardous waste, sufficient
information must be
provided
to explain the following: how use of the required
air emission controls on the tanks would affect the tank design features and
facility operating procedures currently used to prevent an undue safety hazard
during management of this hazardous waste in the tanks; and why installation
of
safety devices on the required air emission controls,
as
allowed under this
Subpart CC, would not address those situations in which evacuation of tanks
equipped with these air emission controls is necessary and consistent with
good
engineering and safety
practices
for handling organic peroxides.
B)
For containers used at the facility
to
manage
this hazardous waste,
sufficient information must be provided
to
explain the following: how
use of
the required air emission controls on the
tanks would affect the container
design features and handling procedures
currently used to prevent an undue
safety hazard during management of this hazardous
waste in the containers; and
why installation of safety devices on the
required air emission controls, as
allowed under this Subpart CC, would not
address those situations in which
evacuation
of
containers equipped with these
air emission controls is necessary
and consistent with good engineering and
safety practices for handling organic
peroxides.
j)
For each hazardous waste management
unit not using air emission controls
specified in Sections 724.984 through 724.987
in accordance with the
requirements of Section
724.980(b) (7),
the owner
and operator must record and
maintain the following information:
1)
The certification that the waste management
unit is equipped with and
operating air emission controls in accordance with the requirements
of an
applicable federal Clean Air Act regulation codified
under 40 CFR 60, 61, or
63.
2)
An identification of the specific federal requirements codified
under 40
CFR
60,
61, or 63 with which the waste management
unit is in compliance.
(Source:
Amended at 33 Ill. Reg.
, effective
Section
724.Appeed4APPENDfl
I
Groundwater
Monitoring List
a)
Common names are those widely
used in government regulations, scientific
publications and commerce; synonyms exist
for many chemicals.
b)
“CAS RN” means “Chemical Abstracts Service Registry Number.”
Where
“total” is entered, all species in the groundwater that contain this element
are
included.
c)
CAS index
names
are
those
used in the 9th Cumulative index.
d)
PCBs
(CAS
RN
1336-36-3)
. This category contains congener chemicals,
including
constituents Aroclor-lOl6
(CAS
RN
12674-11-2),
Aroclor-1221
(CAS
RN
11104-28-2)
, Aroclor-1232
(CAS
RN
11141-16-5)
, Aroclor-1242
(CAS
RN 53469-21-9)
Aroclor-l248
(CAS
RN 12672-29-6),
Aroclor-1254
(CAS
RN
11097-69-1)
and Aroclor
1260
(CAS
RN 11096-82-5)
e)
PCDDs. This category includes congener
chemicals, including
tetrachlorodibenzo-p-dioxins
(see
also 2,3,7,
8-TCDD),
pentachlorodibenzo-p
dioxins and hexachlorodibenzo-p-dioxins.
f)
PC1DFs. This category contains congener chemicals, including
tetrachlorodibenzofurans,
pentachlorodibenzofurans,
and hexachlorodibenzofurans.
Common NameCAS RNChemical Abstracts Service
Index NameAcenaphthenes3 -32- 9Acenaphthylene,
1,2 -dihydro-Acenaphthylene2o8-
96-
8AcenaphthyleneAcetone67 -64-12- PropanoneAcetophenone98-
86-2Ethanone, 1-phenyl-
Acetonitrile; Methyl cyanide7s-05-8Acetonitrile2-Acetylaminofluorene;
2-AAFS3-
96-3Acetamide, N-9H-fluoren-2-yl-Acroleinlo7-02-82-PropenalAcrylonitrilelo7-13-
12-PropenenitrileAldrin3o9-00-2l,4:5,8-Dimethanonaphthalene, 1,2,3,4,10,10-
hexachloro-l,4,4a,5,8,8a-hexahydro-
(la,4a,4ab,Sa,8a,8ab)-Allyl chloridelo7-0S-
11-Propene, 3-chloro-4-Aminobiphenyl92-67-1(l,l’-Biphenyl)-4-amineAniline62-53-
3BenzenamineAnthracenel2o-12-7AnthraceneAntimony(Total)AntimonyAramitel4o-57-
BSulfurous acid, 2-chloroethyl 2-
(4- (1,
l-dimethylethyl)phenoxy)
-1-methylethyl
esterArsenic (Total)ArsenicBarium(Total)BariumBenzerie7l-43-
2BerizeneBenzo
(a)
anthracene; Benzanthracene56-55-
3Benz
(a)
anthraceneBenzo
(b)
fluoranthene2O5-99-
2Benz
(e)
acephenanthryleneBenzo(k) fluoranthene2O7-08-
9Benzo
(k)
fluorantheneBenzo (ghi) perylenel9l-24-
2Benzo(ghi)peryleneBenzo(a)pyrene5O-32-8Benzo(a)pyreneBenzyl
alcohollOO-51-
6BenzenemethanolBeryllium(Total)Berylliuma-BHC319-84-6Cyclohexane,
1,2,3,4,5,6-
hexachioro-, (la,2a,3b,4a,5b,6b)-b-BHC319-85-7Cyclohexane,
1,2,3,4,5,6-
hexachioro-,
(la,2b,3a,4b,Sa, Gb)
-d-BHC319-86-8Cyclohexane,
1,2,3,4,5,6-
hexachloro-, (la,2a,3a,4b,5a,Gb)-g-BHC; Lindane58-89-9Cyclohexane,
1,2,3,4,5,6-
hexachloro-,
(la,2a,3b,4a,5a,6b)-Bis(2-chloroethoxy)methanelll-91-lEthane, 1,1’-
(methylenebis(oxy))bis(2-chloro-Bis(2-chloroethyl)
etherlll-44-4Ethane,
l,1T -
oxybis
(2-chioro-Bis (2-chloro-l-methylethyl)
ether; 2,2
T
-Dichlorodiisopropyl
etherlO8-60-lPropane, 2,2’-oxybis(l-chloro-Bis(2-ethylhexyl)
phthalatell7-81-
71, 2-Benzenedicarboxylic acid, bis(2-ethylhexyl)
esterBromodichloromethane75-27-
4Methane, bromodichioro-Bromoform;
Tribromomethane75-25-2Methane, tribromo-4-
Bromophenyl phenyl etherlOl-55-3Benzene,
1-bromo-4-phenoxy-Butyl benzyl
phthalate;
Benzyl butyl
phthalate85-68-71,2-Benzenedicarboxylic acid,
butyl
phenylmethyl esterCadmiumTotalCadmiumCarbon
disulfide75-15-OCarbon
disulfideCarbon tetrachloride56-23-5Methane,
tetrachloro-Chlordane57-74-94, 7-
Methano-1H-indene,l,2,4,5,6,7,8,8-octachloro-2,3,3a,4,7,7a-hexahydro-p-
ChloroanilinelO6-47-8Benzeneamine, 4-chloro-ChlorobenzenelO8-90-7Benzene,
chloro-Chlorobenzilate5lO-15-6Benzeneacetic acid, 4-chloro-a--
(4-chiorophenyl)
-a
hydroxy-, ethyl esterp-Chloro-m-cresol59-50-7Phenol,
4-chloro-3-methyl-
Chloroethane; Ethyl chloride75-OO-3Ethane, chloro-Chloroform67-66-3Methane,
trichloro-2-Chloronapthalene9l-58-7Naphthalene, 2-chloro-2-Chlorophenol95-57-
8Phenol, 2-chloro-4-Chlorophenyl phenyl ether7005-72-3Benzene,
l-chloro-4-
phenoxy-Chloroprenel26-99-81, 3-Butadiene, 2-chloro-
Chromium(Total)
ChromiumChrysene2l8-Ol-
9ChryseneCobalt (Total)CobaltCopper(Total)Copperm-CresollO8-39-4Phenol,
3-methyl-
o-Cresol95-48-7Phenol, 2-methyl-p-CresollO6-44-5Phenol,
4-methyl-Cyanide57-12-
SCyanide2,4-D; 2,4-Dichlorophenoxyacetic acid94-75-7Acetic
acid,
(2,4-
dichlorophenoxy) -4,4’ -D]JD72-54-8Benzene, 1,1’-
(2,2-dichloroethylidene)bis(4-
chloro-4,4’-DDE72-55-9Benzene,
1,1’-(dichloroethylidene)bis(4-chloro-4,4’-DDT5O-
29-3Benzene, l,l’-(2,2,2-trichloroethylidene)bis(4-chloro-Diallate23O3-16-
4Carbamothioic acid, bis(l-methylethyl)-,
S-(2,3-dichloro-
2 propcnyl)
S
(2,3
dichioro
2-propenyl)
esterDibenz(a,h)anthracenes3-70-
3Dibenz
(a, h)
anthraceneDibenzofuranl32 -64- 9DibenzofuranDibromochloromethane;
Chlorodibromomethanel24 -48- lMethane, dibromochioro- 1, 2-Dibromo-3
-chloropropane;
DBCP96-12-8Propane, 1, 2-dibromo-3-chloro-l, 2-Dibromoethane; Ethylene
dibromidelO6-93-4Ethane, 1, 2-dibromo-Di-n-butyl phthalate84-74-21,
2-
Benzenedicarboxylic
acid,
dibutyl estero-Dichlorobenzene9s-50-lBenzene,
1,2-
dichloro-m-Dichlorobenzene54l-73-lBenzene,
l,3-dichloro-p-DichlorobenzenelO6-46-
7Benzene, l,4-dichloro-3,3’-Dichlorobenzidine9l-94-l(1,l’-Biphenyl)-4,4’-
diamine, 3,3’-dichloro-trans-1,4-Dichloro--2-butenellO-57-62-Butene,
1,4-
dichloro-,
(E)
-Dichlorodifluoromethane75-71-8Methane,
dichlorodifluoro-1, 1-
Dichloroethane75-34-3Ethane, 1, l-dichloro-l, 2-Dichloroethane;
Ethylene
dichloridelO7-06-2Ethane, 1, 2-dichloro-l, 1-Dichloroethylene;
Vinylidene
chloride75-35-4Ethene,
l,l-dichloro-trans-1,2-Dichloroethylenel56-60-5Ethene,
l,2-dichloro-, (E)-2,4-Dichlorophenoll2O-83-2Phenol,
2,4-dichloro-2,6-
Dichlorophenol87-65-OPhenol,
2,6-dichloro-l,2-Dichloropropane78-87-5Propane,
l,2-dichloro-cis-l,3-DichloropropenelOO6l-O1-51-Propene,
l,3-dichloro-,
(Z)
trans-l,3-DichloropropenelOO6l-02-61-Propene, 1,3-dichioro-,
(E)-Dieldrin6o-57-
12,7:3,6-Dimethanonaphth(2,3-b)oxirene, 3,4,5,6,9,9-hexachloro-
la,2,2a,3,6,6a,7,7a-octahydro-, (laa,2b,2aa,3b,6b,6aa,7b,7aa)-Diethyl
phthalate84-66-21,2-Benzenedicarboxylic
acid, diethyl
esterO,O-Diethyl 0-2-
pyrazinyl phosphorothioate;
Thionazin297-97-2Phosphorothioic
acid, 0,0-diethyl
0-pyrazinyl esterDimethoate6O-51-5Phosphorodithioic acid,
0,0-dimethyl S-
(2-
(methylamino)
-2-oxoethyl)
esterp-
(Dimethylamirio)azobenzene6O-ll-7Benzenamine,
N,N-dimethyl-4- (phenylazo) -7, l2-Dimethylbenz
(a)anthracene57-97-
6Benz (a)anthracene, 7, l2-dimethyl-3
.3’ -Dimethylbenzidinell9-93-7
(1,1’
-Biphenyl) -
4,4’ -diamine, 3,3
T
-dimethyl-a,a-Dimethylphenethylaminel22-09-8Benzeneethanamine,
a,a-dimethyl-2,4-DimethylphenollO5-67-9Phenol,
2,4-dimethyl-Dimethyl
phthalatel3l-1l-31,2-Benzenedicarboxylic
acid, dimethyl esterm-Dinitrobenzene99-
65-OBenzene,
l,3-dinitro-4,6-Dinitro-o-cresol534-52-lPhenol, 2-methyl-4,6-
dinitro-2,4-Dinitrophenol5l-28-5Phenol,
2,4-dinitro-2,4-Dinitrotoluenel2l-14-
2Benzene, 1-methyl-2,4-dinitro-2,
6-DinitrotolueneEO6-20-2Benzene, 2-methyl-1,3-
dinitro-Dinoseb; DNBP;
2-sec-Butyl-4,6-dinitrophenol88-85-7Phenol,
2-(l-
methylpropyl) -4, 6-dinitro-Di-n-octyl
phthalatell7-84-Ol,2-Benzenedicarboxylic
acid, dioctyl esterl,4-Dioxanel23-9l-ll,4-DioxaneDiphenylaminel22-39-
4Benzeneamine, N-phenyl-Disulfoton298-04-4Phosphorodithioic
acid, 0,0-diethyl
S
(2-(ethylthio)ethyl) esterEndosulfan 1959-98-86,9-Methano-2,4,3-
benzodioxathiepin,6,7,8,9,1O,lO-hexachloro-1,5,5a,E,9,9a-hexahydro-,
3-oxide,
(3a,5ab,6a,9a,9ab)-Endosulfan
11332l3-65-96,9-Methano-2,4,3-
benzodioxathiepin,6,7,8,9,lO,lO-hexachloro-l,5,5a,6,9,9a-hexahydro-,
3-oxide,
(3a,5aa,Eb,9b,9aa)-Endosulfan
sulfatelo3l-07-86,9-Methano-2,4,3-
benzodioxathiepin,6,7,8,9,1O,1O-hexachloro-1,5,5a,6,9,9a-hexahydro-,3,3-
dioxideEndrin72-20-82,7:3,6-Dimethanonaphth(2,3-b)oxirene,
3,4,5,6,9,9-
hexachloro-la,2,2a,3,6,6a,7,7a-octahydro-,
(laa,2b,2ab,3a,6a,6ab,7b,7aa)-Endrin
aldehyde742l-93-4l, 2, 4-Methanocyclopenta(cd)pentalene-5-carboxaldehyde,
2,2a,3,3,4, 7-hexachlorodecahydro-, (la,2b,2ab,4b,4ab,Sb,Eab,
Ebb,
7R)-
EthylbenzenelOo-41-4Benzene, ethyl-Ethyl
methacrylate97-63-22-Propenoic acid,
2-
methyl-, ethyl esterEthyl
methariesulfonate62-5O-OMethanesulfonic acid, ethyl
esterFamphur52-85-7Phosphorothioic
acid, 0-
(4-c
(dimethylamino) sulfonyl)phenyl) -
0,0-dimethyl
esterFluoranthene2O6-44-OFluorantheneFluorene86-73-79H-
FluoreneHeptachlor76-44-84,7-Methano-lH-indene,
1,4,5,6,7,8,8-heptachioro-
3a,4,7,7a-tetrahydro-Heptachlor epoxidelO24-57-32,5-Methano-2H-indeno(l,2-
b)oxirene,
2,3,4,5, 6,7,7-heptachloro-la,lb,5,Sa,6,
6a-hexahydro-,
(laa,
lbb, 2a, 5a, 5ab, 6b,
Eaa)
-Hexachlorobenzenell8-74-lBenzene,
hexachloro
Hexachlorobutadiene87-68-3l,3-Butadiene, l,l,2,3,4,4-hexachloro-
Hexachlorocyclopentadiene77-47-4l, 3-Cyclopentadiene,
1,2,3,4,5, 5-hexachloro-
Hexachloroethane67-72-lEthane, hexachloro-Hexachlorophene7O-30-4Phenol,
2,2’ -
methylenebis(3,4,6-trichloro-Hexachloropropenel888-7l-71-Propene, 1,1,2,3,3,3-
hexachloro-2-Hexanone59l-78-62-Hexanonelndeno(l,2,
3-cd)
pyrenel93-39-
5lndeno(l,2,3-cd)pyrenelsobutyl alcohol78-83-ll-Propanol,
2-methyl-Isodrin46s-
73-61,4,5,8-Dimethanonaphthalene, 1,2,3,4, lO,lO-hexachloro-1,4,4a,5,
8,8a-
hexahydro-
(la,
4a, 4ab,
5b, Sb,
8ab)
-Isophorone78-59-l2-Cyclohexen-1-one,
3,5,5-
trimethyl-Isosafrolel2O-58-1l,3-Benzodioxole,
5- (1-propenyl)-Keponel43-50-
Ol,3,4-Metheno-2H-cyclobuta-
(c,d)pentalen-2-one, 1,la,3,3a,4,5,5,5a,5b,6-
decachlorooctahydro-Lead(Total)LeadMercury(Total)MercuryMethacrylonitrilel26-96-
72-Propenenitrile, 2-methyl-Methapyrilene9l-80-5l,2-Ethanediamine,
N,N-dimethyl
1,l’-(2,2,2-
trichloroethylidene)bis (4-methoxy-Methyl
bromide; Bromomethane74-83-9Methane,
bromo-Methyl chloride; Chloromethane74-87-3Methane,
chloro-3-
Methylcholanthrenes6-49-5Benz(j)aceanthrylene,
1, 2-dihydro-3-methyl-Methylene
bromide; D±bromomethane74-95-3Methane, dibromo-Methylene
chloride;
Dichloromethane7s-09-2Methane, dichioro-Methyl
ethyl ketone; MEK78-93-32-
ButanoneMethyl iodide; Iodomethane74-88-4Methane,
iodo-Methyl methacrylate8O-62-
62-Propenoic acid,
2-methyl-,
methyl esterMethyl
methanesulfonate66-27-
3Methanesulfonic acid, methyl ester2-Methylnaphthalene9l-57-6Naphthylene,
2-
methyl-Methyl parathion;
Parathion methyl298-OO-CPhosphorothioic
acid, 0,0-
dimethyl
0-
(4-nitrophenyl)
ester4-Methyl-2-pentanone; Methyl isobutyl ketonelO8-
10-12-Pentanone,
4-methyl-Naphthalene9l-20-3Naphthalenel,4-Naphthoquinonel3O-15-
41, 4-Naphthalenedionel-Naphthylaminel34-32-71-Naphthalenamine2-Naphthylamine9l-
59-82-NaphthalenamineNickel(Total)Nickelo-Nitroaniline88-74-4Benzenamine,
2-
nitro-m-Nitroaniline99-09-2Benzenamine,
3-nitro-p-NitroanilineloO-Ol-
6Benzenamine,
4-nitro-Nitrobenzene98-95-3Benzene,
nitro-o-Nitrophenol88-75-
5Phenol, 2-nitro-p-Nitrophenolloo-02-7Phenol,
4-nitro-4-Nitroquinoline
1-
oxide56-57-5Quinoline, 4-nitro-,
1-oxideN-Nitrosodi-n-butylamine924-16-31-
Butanamine,
N-butyl-N-nitroso-N-Nitrosodiethylamine55-18-5Ethanamine,
N-ethyl-N
nitroso-N-Nitrosodimethylamine62-75-9Methanamine,
N-methyl-N-nitroso-N
Nitrosodiphenylamine86-30-6Benzenamine,
N-nitroso-N-phenyl-N
Nitrosodipropylamine;
Di-n-propylnitrosamine62l-64-71-Propanamine,
N-nitroso-N
propyl-N-Nitrosomethylethylaminelo595-95-6Ethanamine, N-methyl-N-nitroso-N
Nitrosomorpholine59-89-2Morpholine,
4—nitroso-N-Nitrosopiperideneloo-75-
4Piperidene,
1-nitroso-N-Nitrosopyrrolidine93o-55-2Pyrrolidine,
1-nitroso-5-
Nitro-o-toluidine99-55- 8Benzenamine,
2 -methyl-5-nitro-Parathion56-38 -
2Phosphorothioic acid,
O,O-diethyl-O- (4-nitrophenyl)
esterPolychiorinated
biphenyls; PCBsSee
(g)l,1TBipheny1,
chloro derivativesPolychiorinated
dibenzo
p-dioxins;
PCDDsSee (h)Dibenzo(b,e)
(l,4)dioxin,
chioro
derivativesPolychlorinated dibenzofurans; PCDFsSee
(i)
Bibenzofuran, chloro
derivativesPentachlorobenzene6Os-93-5Benzene,
pentachloro-Pentachloroetharie76-
01-7Ethane, pentachloro-Pentachloronitrobenzene82-68-8Benzene,
pentachloronitro
Pentachlorophenol87-86-SPhenol, pentachloro-Phenacetin62-44-2Acetamide,
N-
(4-
ethoxyphenyl) Phenanthrene85- 01- SPhenanthrenePhenollo8-
95 -2Phenolp-
Phenylenediaminelo6-50-31,
4-BenzenediaminePhorate298-02-2Phosphorodithioic
acid,
0,0-diethyl 5-
((ethylthio)methyl)
ester2-Picolinelo9-06-8Pyridine,
2-methyl-
Pronamide23950-58-5Benzamide,
3,5-dichloro-N- (l,l-dimethyl-2-propenyl) -
Propionitrile; Ethyl
cyanidelo7-12-OPropanenitrilePyrenel29-00-
OPyrenePyridinello-86-lPyridineSafrole94-59-71,3-Benzodioxole,
5- (2-propenyl)-
Selenium(Total)SeleniumSilver(Total)SilverSilvex;
2,4,5-TP93-72-lPropanoic
acid,
2-(2,4,5-trichlorophenoxy)-Styreneloo-42-SBenzene,
ethenyl-Sulfidel8496-25-
8Sulfide2,4,5-T; 2,4,5-Trichiorophenoxyacetic
acid93-76-5Acetic acid, (2,4,5-
trichlorophenoxy)-2,3,7,8-TCDD;
2,3,7,8-Tetrachlorodibenzo-p-dioxinl746-Ol-
BDibenzo(b,e) (l,4)dioxin,
2,3,7,8-tetrachloro-l,2,4,5-Tetrachlorobenzene9s-94-
3Benzene,
1,2,4,5-tetrachloro-1,l,1,2-Tetrachloroethane63o-20-6Ethane, 1,1,1,2-
tetrachloro-1,l,2,2, -Tetrachloroethane79-34-5Ethane,
1,1,2,2-tetrachloro-
Tetrachloroethylene; Perchioroethylene;
Tetrachloroethenel27-18-4Ethene,
tetrachloro-2,3,4, 6-Tetrachlorophenol58-90-2Phenol,
2,3,4,6-tetrachioro-
Tetraethyl dithiopyrophosphate;
Sulfotepp3689-24-5Thiodiphosphoric acid
(((HO)2P(S) )20),
tetraethyl
esterThallium(Total)ThalliumTin(Total)TinToluenelos
88-3Benzene, methyl-o-Toluidine9s-53-4Benzenamine,
2-methyl-Toxaphene800l-35-
2Toxaphenel,2,4-Trichlorobenzenel2o-82-lBenzene,
1,2,4-trichloro-l,1,1-
Trichioroethane; Methyl chloroform7l-55-6Ethane,
1,1, l-trichloro-l, 1,2-
Trichloroethane79-00-SEthane, 1,1,
2-trichloro-Trichloroethylene;
Trichloroethene79-0l-6Ethene,
trichloro-Trichlorofluoromethane75-69-4Methane,
trichlorofluoro-2,4,5-Trichlorophenol95-96-4Phenol,
2,4,5-trichloro-2,4,6-
Trichlorophenol88-06-2Phenol,
2,4,6-trichloro-l,2,3-Trichloropropane9s-18-
4Propane, l,2,3-trichloro-O,O,O-Triethyl
phosphorothioatel26-68-lPhosphorothioic
acid,
0,0,0-triethyl
estersym-Trinitrobenzene99-35-4Benzene,
1,3,5-trinitro-
Vanadium(Total)VanadiumVinyl
acetatel08-05-4Acetic
acid, ethenyl esterVinyl
chloride75-0l-4Ethene,
chloro-Xylene
(total)1330-20-7Benzene,
dimethyl
Zinc
(Total)
Zinc
(Source: Amended at
33
Ill. Reg.
, effective
ILLINOIS REGISTER
I
POLLUTION CONTROL BOD
I
NOTICE OF PROPOSED ENDMENT
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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
725.102
Electronic Reporting
725.104
Imminent Hazard Action
SUBPART B:
GENERAL FACILITY STANDARDS
Section
725.110
Applicability
725.111
USEPA Identification Number
725.112
Required
Notices
725.113
General
Waste
Analysis
725.114
Security
725.115
General Inspection Requirements
725.116
Personnel Training
725.117
General Requirements for Ignitable, Reactive, or Incompatible Wastes
725.118
Location Standards
725.119
Construction Quality Assurance Program
SUBPART C:
PREPAREDNESS AND PREVENTION
Section
725.130
Applicability
725.131
Maintenance
and
Operation of Facility
725.132
Required
Equipment
725.133
Testing and Maintenance of
Equipment
725.134
Access to
Communications or
Alarm System
725.135
Required Aisle
Space
725.137
Arrangements with Local Authorities
SUBPART
D:
CONTINGENCY PLAN AND EMERGENCY PROCEDURES
Section
725.150
Applicability
725.151
Purpose and Implementation of Contingency Plan
725.152
Content of Contingency Plan
725.153
Copies of Contingency Plan
725.154
Amendment of Contingency Plan
725.155
Emergency
Coordinator
725.156
Emergency Procedures
SUBPART
E:
MANIFEST SYSTEM, RECORDKEEPING,
AND REPORTING
Section
725.170
Applicability
725.171
Use of Manifest System
725.172
Manifest
Discrepancies
725.173
Operating
Record
725.174
Availability,
Retention, and Disposition of Records
725.175
Annual
Report
725.176
Unmanifested Waste Report
725.177
Additional Reports
SUBPART F:
GROUNDWATER
MONITORING
Section
725.190
Applicability
725.191
Groundwater Monitoring
System
725.192
Sampling and Analysis
725.193
Preparation, Evaluation,
and Response
725.194
Recordkeeping and Reporting
SUBPART G:
CLOSURE AND POST-CLOSURE
CARE
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 Care
Plan; Amendment of Plan
725.219
Post-Closure Notices
725.220
Certification of Completion of
Post-Closure Care
725.221
Alternative Post-Closure Care Requirements
SUBPART H:
FINANCIAL REQUIREMENTS
Section
725.240
Applicability
725.241
Definitions of Terms as Used in this Subpart H
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 Containers
725.273
Management
of Containers
725.274
Inspections
725.276
Special Requirements
for Ignitable or Reactive Wastes
725.277
Special
Requirements for Incompatible
Wastes
725.278
Air Emission Standards
SUBPART J:
TANK SYSTEMS
Section
725.290
Applicability
725.291
Assessment of Existing Tank
System
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
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 Wastes
725.299
Special Requirements for Incompatible Wastes
725.300
Waste
Analysis and Trial Tests
725.301
Generators of 100
to
1,000 Kilograms of Hazardous Waste Per Month
725.302
Air Emission Standards
SUBPART K:
SURFACE IMPOUNDMENTS
Section
725.320
Applicability
725.321
Design and Operating Requirements
725.322
Action Leakage Rate
725.323
Containment System
725.324
Response Actions
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 Wastes
725.330
Special
Requirements
for Incompatible Wastes
725.331
Air
Emission Standards
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 Wastes
725.357
Special Requirements for Incompatible Wastes
725.358
Closure and Post-Closure Care
725.359
Response Actions
725.360
Monitoring and Inspections
SUBPART M:
LAND TREATMENT
Section
725.370
Applicability
725.372
General Operating Requirements
725.373
Waste Analysis
725.376
Food Chain Crops
Unsaturated Zone
(Zone
of Aeration)
Monitoring
Recordkeeping
Closure and Post-Closure Care
Special
Requirements for Ignitable
or Reactive Wastes
Special Requirements for Incompatible
Wastes
Applicability
Design Requirements
Action Leakage Rate
Response Actions
Monitoring and Inspections
Surveying and Recordkeeping
Closure and Post-Closure Care
Special Requirements for Ignitable
or Reactive Wastes
Special Requirements for Incompatible
Wastes
Special Requirements for Liquid Wastes
Special Requirements for Containers
Disposal of Small Containers
of Hazardous Waste in Overpacked Drums
Applicability
Waste Analysis
General Operating Requirements
Monitoring and Inspections
Closure
Interim Status Incinerators Burning Particular
Hazardous Wastes
SUBPART P:
THERMAL TREATMENT
Other Thermal Treatment
General Operating Requirements
Waste Analysis
Monitoring and
Inspections
Closure
Open Burning; Waste Explosives
Interim
Status
Thermal
Treatment Devices Burning Particular
Applicability
General Operating Requirements
Waste Analysis and Trial Tests
Inspections
Closure
Special
Requirements for Ignitable or Reactive Wastes
Special Requirements for Incompatible Wastes
725.378
725.379
725.380
725.381
725.382
SUBPART N:
LANDFILLS
Section
725.400
725.401
725.402
725.403
725.404
725.409
725.410
725.412
725.413
725.414
725.415
725.416
(Lab
Packs)
SUBPART
0:
INCINERATORS
Section
725.440
725.441
725.445
725.447
725.451
725.452
Section
725.470
725.473
725.475
725.477
725.481
725.482
725.483
Hazardous
Wastes
SUBPART
Q:
CHEMICAL, PHYSICAL, AND
BIOLOGICAL TREATMENT
Section
725.500
725.501
725
.502
725.503
725.504
725.505
725.506
SUBPART R:
UNDERGROUND INJECTION
Section
725.530
Applicability
SUBPART
W:
DRIP
PADS
Applicability
Assessment of Existing Drip
Pad Integrity
Design
and Installation
of New Drip Pads
Design
and Operating
Requirements
Inspections
Closure
SUBPART 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
SUBPART BB:
AIR
EMISSION
STANDARDS FOR EQUIPMENT LEAKS
Section
725.950
Applicability
725.951
Definitions
725.952
Standards:
725.953
Standards:
725.954
Standards:
725.955
Standards:
725.956
Standards:
725.957
Standards:
725.958
Standards:
Other
Connectors
725.959
Standards: Delay of Repair
725.960
Standards: Closed-Vent Systems and Control Devices
725.961
Percent Leakage Alternative for Valves
725.962
Skip Period Alternative for Valves
725.963
Test Methods and Procedures
725.
964
Recordkeeping Requirements
SUBPART
CC:
CONTAINERS
Section
725.980
725.981
725.982
725.983
725.
984
725
. 985
725.986
725.987
725.988
725.989
Section
725.540
725.541
725.542
725.543
725.544
725.545
Section
725.930
725.931
725.932
725.933
725. 934
725.935
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, Flanges,
and
AIR EMISSION STANDARDS FOR TANKS, SURFACE IMPOUNDMENTS, AND
Applicability
Definitions
Schedule for
Implementation
of Air Emission Standards
Standards:
General
Waste
Determination
Procedures
Standards: Tanks
Standards: Surface
Impoundments
Standards: Containers
Standards: Closed-Vent Systems and Control Devices
Inspection and
Monitoring
Requirements
725
. 990
Recordkeeping Requirements
725.991
Alternative Tank Emission Control Requirements (Repealed)
SUBPART
DD:
CONTAINMENT BUILDINGS
Section
725.1100
Applicability
725.1101
Design and
Operating
Standards
725.1102
Closure and Post-Closure Care
SUBPART EE:
HAZARDOUS
WASTE MUNITIONS
AND
EXPLOSIVES
STORAGE
Section
725.1200
Applicability
725.1201
Design and Operating Standards
725.1202
Closure and Post-Closure Care
725.Apper44-AP2END1X A Recordkeeping Instructions
725.Apped4APPENflIX B EPA Report Form and Instructions (Repealed)
725.Aped4EAPPENDIX C USEPA Interim
Primary
Drinking
Water Standards
725.Apped4PPEND1X D Tests for Significance
725.Appe4PPED1X E Examples of Potentially Incompatible
Wastes
725.Appea44.EPEND.IX F Compounds with Henrys Law Constant Less
Than 0.1
Y/X
(at 25°C)
AUTHORITY: Implementing Sections 7.2 and 22.4 and authorized by
Section
27 of
the Environmental Protection Act
[415
ILCS 5/7.2, 22.4, and
27]
SOURCE: Adopted in R8l-22 at 5 Iii. Reg. 9781,
effective May 17, 1982; amended
and codified in
R81-22
at 6
Ill. Reg. 4828, effective May 17, 1982; amended in
R82-18 at 7 Ill.
Reg. 2518, effective February 22, 1983; amended in R82-19
at 7
Ill. Reg. 14034,
effective October 12, 1983; amended in R84-9
at 9
Ill. Reg.
11869, effective
July 24, 1985; amended in R85-22
at
10 Ill. Reg. 1085,
effective
January 2, 1986; amended in R86-l at 10 Ill. Reg. 14069, effective
August 12,
1986; amended in R86-28 at 11 Ill. Reg. 6044, effective March 24,
1987;
amended in R86-46 at 11 Ill. Reg. 13489, effective August 4, 1987; amended
in
R87-5
at
11 Ill. Reg. 19338, effective November 10, 1987; amended in R87-26
at 12
Iii. Reg. 2485, effective January 15, 1988; amended in R87-39 at 12 Ill.
Reg.
13027, effective July 29, 1988; amended in R88-l6 at 13 111. Reg. 437,
effective
December 28, 1988; amended in R89-1 at 13 111. Reg. 18354, effective
November
13, 1989; amended in R90-2 at 14 Iii. Reg. 14447, effective August 22,
1990; amended
in R90-10
at
14 Ill. Reg. 16498, effective September 25, 1990;
amended in R90-l1 at
15 Ill. Reg.
9398,
effective June 17, 1991; amended in R91-
1
at 15 Iii. Reg.
14534, effective October 1, 1991; amended in R91-l3 at 16 Ill.
Reg. 9578,
effective June
9,
1992; amended in R92-l
at
16 Iii. Reg. 17672,
effective
November 6, 1992; amended in R92-10
at
17 111. Reg. 5681, effective
March
26, 1993; amended in R93-4 at 17 Iii. Reg. 20620, effective November 22,
1993;
amended in R93-l6 at 18 Iii. Reg. 6771, effective April 26, 1994; amended
in
R94-7
at
18 Ill. Reg. 12190, effective July 29, 1994; amended in R94-17 at 18
Ill. Reg. 17548, effective
November
23, 1994; amended in R95-6 at 19
Ill.
Reg.
9566, effective
June 27,
1995;
amended
in R95-20 at 20 Ill. Reg.
11078,
effective August
1, 1996; amended in R96-l0/R97-3/R97-5
at
22 Ill. Reg.
369,
effective
December 16, 1997; amended in R98-12
at
22 Ill. Reg. 7620, effective
April 15, 1998; amended in R97-2l/R98-3/R98-5 at 22 111. Reg. 17620, effective
September 28, 1998; amended in R98-21/R99-2/R99-7 at 23 Ill. Reg. 1850,
effective January 19, 1999;
amended
in R99-l5 at 23 Ill. Reg. 9168,
effective
July 26, 1999;
amended
in R00-5 at 24 Ill. Reg. 1076,
effective January
6, 2000;
amended in R00-13 at 24 Iii. Reg. 9575, effective June 20, 2000; amended in R03-
7
at
27
Ill.
Reg. 4187, effective February 14, 2003; amended in R05-8 at 29 Ill.
Reg. 6028, effective April 13, 2005; amended in R05-2 at 29 Ill. Reg. 6389,
effective April 22, 2005; amended in R06-5/R06-6/R06-7 at 30 Ill. Reg. 3460,
effective February 23, 2006; amended in R06-l6/R06-l7/R06-l8 at 31 Ill. Reg.
1031, effective December 20, 2006; amended in R07-5/R07-14 at 32 Ill. Reg.
12566, effective July 14, 2008; amended in R09-3 at 33 Ill. Reg.
effective
SUBPART B:
GENERAL FACILITY SThNDARDS
Section 725.114
Security
a)
The owner or operator must prevent the unknowing entry and minimize the
possibility for the unauthorized entry of persons or livestock onto the active
portion of his facility, unless the following are true:
1)
Physical contact with the waste, structures, or equipment of the active
portion
of the facility will not injure unknowing or unauthorized persons or
livestock that may enter the active portion of the facility; and
2)
Disturbance of the waste or equipment by the unknowing or
unauthorized
entry of persons or livestock onto the active portion of a
facility will
not
cause a
violation of the requirements of this Part.
b)
Unless exempt
under subsections
(a) (1)
and
(a)
(2) of this Section,
a
facility must
have the following:
1)
A 24-hour
surveillance system
(e.g.,
television monitoring or surveillance
by
guards or
facility personnel) that continuously monitors and controls entry
into the active
portion of the facility; or
2)
Controlled access,
including
the
following minimum elements:
A)
An artificial or natural
barrier
(e.g., a fence
in
good
repair or
a fence
combined with a
cliff)
that
completely
surrounds the
active portion of the
facility; and
B)
A means to control
entry
at all times
through the
gates
or other entrances
to
the active portion
of the facility
(e.g., an
attendant, television monitors,
locked entrance, or
controlled roadway
access to
the facility)
BOARD NOTE: The requirements of subsection
(b)
of this Section are
satisfied
if the facility or plant within which the active portion is located
itself
has
a
surveillance system or a barrier and a means to control entry that
complies with the requirements of subsection
(b) (1)
or
(b) (2)
of this Section.
c)
Unless exempt under subsection
(a) (1)
or
(a) (2)
of this Section, a sign
with the legend,
ITDanger
-—
Unauthorized Personnel
Keep
Out,TT
must
be posted at
each entrance to
the active portion
of a
facility
and at
other locations in
sufficient
numbers
to be
seen from any approach
to
this active portion. The
sign must be
legible from
a
distance of
at
least 25
feet.
Existing signs with
a
legend other
than
Tioanger
-—
Unauthorized Personnel Keep
OutTT
may
be used
if
the legend on
the sign indicates that only authorized personnel are allowed
to
enter the
active portion and that entry onto the active portion can
be
dangerous.
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1
a)
If
a
facility accepts
for treatment, storage, or disposal any hazardous
waste from an
off-site source without an accompanying manifest, or without
an
accompanying
shipping paper, as described by 35 Ill. Adm. Code
723.120(e),
and
if the waste is
not excluded from the manifest requirement by 35 Ill.
Adm.
Code
260 through 265,
then the owner or operator must prepare and submit a
letter
to
the Agency
within 15 days after receiving the waste. The unmanifested
waste
report must
contain the following information:
1)
The
USEPA identification number, name, and address of the
facility;
2)
The date
the facility received the waste;
3)
The USEPA
identification number, name, and address of the generator and
the transporter,
if available;
4)
A description
and the quantity of each unmanifested hazardous waste the
facility received;
5)
The method
of treatment, storage, or disposal for each hazardous waste;
6)
The
certification signed
by
the owner or operator of the facility or its
authorized
representative; and
7)
A brief
explanation of why the waste was unmanifested, if
known.
b)
This
subsection
(b)
corresponds with 40 CFR
265.76(b),
which USEPA has
marked
“reserved.” This statement maintains structural
consistency with the
corresponding federal regulations.
BOARD
NOTE: Small quantities of hazardous
waste are excluded from regulation
under
this Part and do not require a
manifest, Where
a
facility received
unmanifested hazardous waste,
USEPA has
suggested
that the owner or operator
obtain from each generator a
certification that the waste qualifies for
exclusion. Otherwise, USEPA has suggested
that the owner or operator file an
unmanifested waste report for the
hazardous
waste
movement.
(Source:
Amended at 33 Ill. Reg.
—,
effective
SUBPART
N:
LANDFILLS
Section
725.416
Disposal of
Small Containers of Hazardous Waste in
Overpacked Drums
(Lab Packs)
Small containers of hazardous
waste in overpacked drums
(lab
packs) may be
placed in a
landfill if the following requirements are met:
a)
Hazardous waste must be packaged in non-leaking inside
containers. The
inside
containers must be of a design and constructed of a
material that will
not
react dangerously with, be decomposed by,
or
be
ignited
by
the waste held
therein. Inside containers must be tightly and
securely
sealed.
The inside
containers must be of the
size
and type
specified in the USDOT hazardous
materials regulations
(49 CFR 173 (Shippers -— General Requirements for
Shipments and Packages), 178
(Specifications for Packagings), and 179
(Specifications
for Tank Cars), each incorporated
by
reference in 35 Ill. Adm.
Code
720.111(b)),
if those regulations specify
a
particular inside container for
the waste.
b)
The inside
containers must
be
overpacked in an open head USDOT
specification
metal shipping container
(49
CFR 178 (Specifications for
Packagings)
and
179 (Specifications for Tank
Cars),
of
no more than 416 liter
(110
gallon)
capacity and surrounded
by, at a
minimum,
a
sufficient quantity
of
sorbent
material, determined
to be
nonbiodegradable
in accordance
with
35
Ill.
Adm. Code
725.414(f)
to
completely
sorb
all of
the liquid contents
of the inside
containers. The
metal outer
container must be full after packing
with inside
containers and
sorbent material.
c)
The sorbent
material
used must not be capable of reacting
dangerously
with, being decomposed by, or being ignited by the contents of the
inside
containers, in
accordance
with Section
725.117(b).
d)
Incompatible wastes,
as
defined
in 35 Ill. Adm. Code
720.110, must not
be
placed in the
same outside container.
e)
Reactive waste, other than cyanide- or sulfide-bearing waste, as defined
in 35 Ill.
Adm. Code 721.123
(a) (5),
must be treated or rendered non-reactive
prior to
packaging in accordance with subsections
(a)
through
(d)
of this
Section.
Cyanide- or sulfide-bearing reactive waste may be packaged in
accordance
with subsections
(a)
through
(d)
of this Section without first being
treated
or rendered non-reactive.
f)
Such
disposal is in compliance with the requirements of
35
Ill. Adm.
Code
728. Persons
that incinerate lab packs according
to
the requirements of
35
Ill.
Adm. Code
728.142(c) (1)
may
use
fiber drums in place of metal outer containers.
Such fiber drums must
meet the USDOT specifications in 49 CFR 173.12 (Exceptions
for Shipments of Waste
Materials),
incorporated by reference
in
35
Ill. Adm.
Code
720.111(b),
and be overpacked according to subsection
(b)
of
this
Section.
g)
Pursuant to 35
Ill. Adm.
Code
729.312,
the use
of labpacks for disposal
of
liquid wastes or
wastes containing free liquids allowed under this Section
is
restricted to
labwaste and non-periodic waste,
as
those terms are defined in
that Part.
(Source:
Amended at 33 Ill. Reg.
—,
effective
SUBPART AA:
AIR
EMISSION STANDARDS
FOR PROCESS VENTS
Section 725.933
Standards: Closed-Vent Systems and Control Devices
a)
Compliance
Required.
1)
Owners or
operators
of closed-vent systems and control
devices
used to
comply with provisions of
this Part
must comply with the
provisions of this
Section.
2)
Implementation Schedule.
A)
The
owner or operator of an existing facility that cannot install a
closed-vent
system and control device
to
comply with the provisions of this
Subpart
AR on the effective date that the facility becomes subject to the
provisions of this Subpart AR must prepare an implementation schedule that
includes dates by which the closed-vent system and control device will be
installed and
in
operation. The controls
must be
installed
as
soon
as
possible,
but the
implementation
schedule may allow
up to 30
months
after
the effective
date that the
facility becomes
subject
to this Subpart AA for
installation and
startup.
B)
Any unit that begins
operation
after
Dcc.December
21,
1990, and which is
subject to
the
provisions of this Subpart AA when operation begins, must comply
with the rules
immediately
(i.e.,
must have control devices installed and
operating on startup
of the affected unit); the 30-month implementation schedule
does not apply.
C)
The owner
or operator of any facility in existence on the effective date
of
a
statutory
or regulatory amendment that renders the facility subject to this
Subpart AA must
comply with all requirements of this Subpart AA as soon as
practicable but no
later than
30
months after the effective date of the
amendment. When
control equipment required
by
this Subpart AA cannot be
installed and
begin operation
by
the effective
date
of the amendment, the
facility owner or
operator must prepare an implementation schedule that includes
the following
information: specific calendar
dates
for award of contracts or
issuance of purchase
orders for the control equipment, initiation of on-site
installation of the
control equipment, completion of the control equipment
installation, and performance of any testing to
demonstrate that the installed
equipment
meets the applicable standards of this
Subpart AA. The owner or
operator
must enter the implementation schedule in
the operating record or in
a
permanent,
readily available file located at the facility.
D)
An owner or operator of a
facility
or unit
that becomes newly subject
to
the
requirements of this Subpart AA after
Dcc.December
8,
1997, due to an action
other
than those described in subsection
(a)
(2) (iii) of this Section must comply
with
all applicable
requirements immediately
(i.e.,
the facility or unit must
have control devices
installed and operating on the date the facility or unit
becomes subject to
this Subpart AA; the 30-month implementation schedule does
not apply).
b)
A
control device involving vapor recovery (e.g., a
condenser or adsorber)
must be
designed and operated to recover the
organic vapors vented
to
it with
an
efficiency
of
95
weight percent or greater unless
the total organic emission
limits of
Section 725.932
(a) (1)
for all affected process
vents is attained
at an
efficiency
less than 95 weight percent.
c)
An enclosed
combustion device (e.g., a vapor incinerator,
boiler,
or
process
heater)
must
be
designed and operated to reduce the
organic
emissions
vented to it by 95
weight percent or greater; to achieve a total
organic
compound
concentration of 20 ppmv, expressed as the sum of the actual
compounds,
not
carbon
equivalents, on a dry basis corrected to three percent
oxygen;
or to
provide a
minimum residence time of 0.50 seconds at a minimum
temperature of
760
degrees
Celsius
(°
C)
. If a boiler or process heater is used as
the control
device,
then the vent stream must be introduced into the flame
combustion zone
of the
boiler or process heater.
d)
Flares.
1)
A flare
must be designed for and operated with no visible emissions as
determined by
the methods specified in subsection
(e) (1)
of this Section except
for periods
not to exceed a total of five minutes during any two
consecutive
hours.
2)
A flare must be operated with a flame present at all times, as determined
by the methods specified in subsection
(f) (2) Cc)
of this Section.
3)
A flare must be used only if the net heating value of the gas being
combusted is 11.2 MJ/scm
(300
Btu/scf) or greater if the flare is steam-assisted
or air-assisted, or if the
net
heating value of the gas being combusted is 7.45
MJ/scm
(200
Btu/scf) or greater if the flare is nonassisted. The net heating
value of the gas being
combusted
must be determined by the methods specified in
subsection
(e) (2)
of this Section.
4)
Exit Velocity.
A)
A
steam-assisted or nonassisted flare must
be
designed for and operated
with an exit
velocity, as determined
by
the methods specified in subsection
(e) (3)
of this
Section, less than 18.3 rn/s
(60
ft/s),
except
as
provided in
subsections
Cd)
(4) (B)
and
Cd) (4)
(C)
of this Section.
B)
A
steam-assisted or nonassisted flare designed for and operated with an
exit
velocity, as determined by the methods specified in subsection
Ce) (3)
of
this Section, equal to or greater than 18.3 rn/s
(60
ft/s)
but
less than 122 rn/s
(400 ft/s)
is allowed if the net heating value of the gas being combusted is
greater than 37.3 MJ/scm
(1,000
Btu/scf)
C)
A steam-assisted or nonassisted flare designed for and operated with an
exit velocity, as
determined
by the methods specified in subsection
(e) (3)
of
this Section, less than the
velocity,
V as determined by the method specified in
subsection
Ce) (4)
and less than 122 rn/s
(400
ft/s) is allowed.
5)
An air-assisted flare must be designed and operated with an exit velocity
less than the velocity, V, as determined by the method specified in subsection
Ce)
(5)
of this Section.
6)
A flare used to comply with this Section must be steam-assisted, air-
assisted,
or nonassisted.
e)
Compliance determination and equations.
1)
Reference Method 22
(Visual
Determination of Fugitive
Emissions from
Material Sources and Smoke
Emissions
from
Flares)
in appendix A to
40 CFR
60
(Test
Methods),
incorporated by reference in 35 Ill. Adm. Code
720.111(b),
must
be used
to determine the compliance of a flare with the visible
emission
provisions of
this Subpart AA. The observation
period is
two hours and must
be
used according to
Method 22.
2)
The net
heating value of the
gas
being combusted in
a
flare must
be
calculated
using the following equation:
HT=Kxn
S
i=lCi
x Hi
Where:
HT
= the net heating value of the sample in MJ/scm; where the net enthalpy per
mole of of fgas is based on combustion at 25° C and 760 mm Hg, but the standard
temperature for determining the volume corresponding to 1 mole is 20° CK
CI=
l.74?-10-7
(1/ppm) (g mol/scm) (MJ/kcal) where
the standard
temperature
for
(g
mol/scm) is 20°
C’?Xi
CSXi=
the
sum
of the
values
of X
for
each
component
i,
from
i=l to
nCi
nj=
the
concentration
of sample component i in ppm on
a
wet
basis,
as
measured for
organics by Reference Method 18
(Measurement
of Gaseous
Organic Compound
Emissions
by Gas Chromatography) in appendix A
to
40 CFR
60
(Test Methods),
and for carbon monoxide, by ASTM D 1946-90
(Standard
Practice
for Analysis of Reformed Gas by Gas Chromatography), each incorporated
by
reference
in 35 Ill. Adm.
Code
720.lllHi ic the net heat of combustion
of
sample component i, kcal/gmol at 25°
C
and 760 mm Hg.
The heats
of combustion
must
be
determined using ASTM D 2382-88
(Standard
Test
Method
for Heat of
Combustion of Hydrocarbon Fuels by Bomb Calorimeter
(High
Precision Method)),
incorporated by reference in 35 Ill. Adm.
Code
720.111(a),
if
published values
are not available or cannot be calculated.
3)
The actual exit velocity of a flare must
be
determined
by
dividing
the
volumetric flow rate
(in
units of standard temperature and pressure),
as
determined by Reference Methods 2
(Determination
of Stack
Gas
Velocity and
Volumetric Flow Rate
(Type
S Pitot
Tube)),
2A
(Direct
Measurement of Gas Volume
through Pipes
and Small Ducts),
2C
(Determination
of Gas Velocity and Volumetric
Flow
Rate in
Small Stacks or Ducts
(Standard
Pitot
Tube)),
or 2D
(Measurement
of
Gas Volume
Flow Rates in Small Pipes
and
Ducts)
in appendix A to 40 CFR 60
(Test
Methods),
incorporated
by
reference in
35 Ill. Adm. Code
720.111(b),
as
appropriate, by
the unobstructed
(free)
cross-sectional area of the flare tip.
4)
The maximum
allowed
velocity in m/s, V for a flare complying with
subsection
(d) (4) (C)
of this Section must be determined by the following
equation:
loalO (Vmax)=HT + 28.831.7
Where:
10gb =
logarithm to the base 1OHT = the net heating value as determined
in
subsection
(e) (2)
of this Section.
5)
The maximum allowed velocity in m/s, V. for an air-assisted flare must
be
determined by the following equation:
V
= 8.706
+
0.7084 HT
Where:
HT
= the net heating value as determined in subsection
(e) (2)
of this
Section.
f)
The owner or operator must monitor and inspect each control device
required
to
comply with this Section to ensure proper operation and maintenance
of
the control device
by
implementing the following requirements:
1)
Install, calibrate, maintain, and operate according
to the manufacturers
specifications a
flow indicator that provides
a record
of vent stream flow
from
each
affected process vent to the control device
at least once
every hour.
The
flow indicator sensor must be installed in the vent stream
at
the nearest
feasible point to the control device inlet
but
before being combined with
other
vent streams.
2)
Install, calibrate, maintain, and operate according
to
the manufacturers
specifications a device to continuously monitor control device operation,
as
specified below:
A)
For
a
thermal vapor incinerator,
a temperature monitoring device equipped
with a
continuous recorder. The device must
have accuracy of
±1
percent of the
temperature
being monitored in
° C
or
0.5°
±0.5°
C,
whichever is
greater. The
temperature sensor must be installed at a location in the combustion
chamber
downstream of the
combustion zone.
B)
For a
catalytic vapor incinerator,
a temperature monitoring device
equipped with a
continuous recorder. The
device must be capable of monitoring
temperature at
two locations and have an
accuracy of
±1
percent of the
temperature
being monitored in
°
C or
±
0.5°
±0.50
C, whichever is greater. One
temperature sensor must be installed in the vent
stream at the nearest feasible
point
to
the catalyst bed inlet and a second temperature
sensor must be
installed in the vent stream at the nearest feasible
point to the catalyst bed
outlet.
C)
For a
flare,
a
heat sensing monitoring
device equipped with a continuous
recorder
that
indicates the continuous
ignition of the pilot flame.
D)
For a
boiler or process heater
having a design heat input capacity less
than 44 MW, a
temperature monitoring
device equipped with a continuous recorder.
The device must
have an accuracy
of
±1
percent of the temperature being
monitored
in
0
C
or
0.5°
±0.5°
C, whichever is greater. The temperature
sensor must be
installed
at a
location
in the furnace downstream of the
combustion
zone.
E)
For a
boiler or process heater
having a design heat input capacity greater
than or
equal
to
44 MW,
a
monitoring device
equipped with a continuous recorder
to
measure parameters that indicate
good combustion operating practices are
being
used.
F)
For a condenser, either of the following:
i)
A monitoring device equipped with a continuous recorder
to
measure
the
concentration level of the organic compounds in the exhaust vent stream from
the
condenser; or
ii)
A temperature monitoring device equipped with
a
continuous recorder.
The
device must be capable of monitoring temperature with an accuracy of
±1
percent
of
the temperature being monitored in degrees Celsius
(0
C)
or
±0.5°
C,
whichever is greater. The temperature sensor must
be
installed
at a
location
in
the
exhaust vent stream from the condenser exit
(i.e.,
product
side)
G)
For a carbon adsorption system, such as a fixed-bed carbon adsorber
that
regenerates the carbon bed directly in the control device, either of the
following:
i)
A monitoring device equipped with
a
continuous recorder
to
measure
the
concentration
level
of the organic compounds in the exhaust vent stream from
the
carbon bed; or
ii)
A
monitoring device equipped
with a continuous recorder
to
measure
a
parameter that indicates the carbon
bed is regenerated on a regular,
predetermined time cycle.
3)
Inspect the readings from each monitoring
device required by subsections
(f)
(1)
and
(f) (2)
of this Section
at
least
once each operating day to check
control device operation and, if necessary, immediately implement the
corrective
measures necessary to ensure the control device operates in compliance with
the
requirements of
this
Section.
g)
An
owner or
operator
using a carbon adsorption system such
as a
fixed-bed
carbon adsorber that
regenerates
the carbon bed directly onsite in the control
device must
replace the existing
carbon in the control device with fresh carbon
at a regular,
predetermined time interval
that is no longer than the carbon
service life
established as
a
requirement
of Section
725.935(b) (4) (C) (vi).
h)
An owner or
operator using
a carbon adsorption system, such as a carbon
canister, that does
not regenerate
the carbon bed directly onsite in the control
device must replace
the existing
carbon in the control device with fresh carbon
on
a
regular basis by
using one
of the following procedures:
1)
Monitor the concentration level of the organic compounds in the exhaust
vent stream from the carbon adsorption system on
a
regular schedule, and replace
the existing carbon with fresh carbon immediately when carbon breakthrough is
indicated. The monitoring frequency must
be
daily or
at
an interval no greater
than 20 percent of the time required
to
consume the total carbon working
capacity established as a requirement of Section
725.935(b) (4)(C) (vii),
whichever is longer.
2)
Replace the
existing
carbon with fresh carbon at a regular, predetermined
time interval that is less than the design carbon replacement interval
established as a
requirement
of Section
725.935(b) (4) (C) (vii).
i)
An owner
or operator of an affected
facility seeking to comply with the
provisions of
this Part
by
using
a control device other than a thermal vapor
incinerator,
catalytic vapor incinerator,
flare,
boiler,
process heater,
condenser, or
carbon adsorption system
is required to develop documentation
including
sufficient information
to describe
the
control device operation and
identify the
process parameter or parameters that
indicate proper
operation
and
maintenance of
the control device.
j)
A
closed-vent system must meet either of the following
design
requirements:
1)
A
closed-vent system must
be
designed
to operate
with
no
detectable
emissions, as
indicated
by
an instrument reading of less than
500
ppmv
above
background, as
determined
by
the methods specified
at
Section
725.934(b), and by
visual
inspections; or
2)
A
closed-vent system
must be
designed
to operate at a pressure
below
atmospheric
pressure. The system must
be
equipped with
at
least one pressure
gauge or
other pressure measurement device that can
be
read from
a
readily
accessible location to verify that negative pressure is being maintained in
the
closed-vent system when the control device is operating.
k)
The owner or operator must monitor and inspect each closed-vent system
required
to
comply with this Section to ensure proper operation and maintenance
of
the closed-vent system by implementing the following requirements:
1)
Each
closed-vent
system that is used to comply with subsection
(j)
(1)
of
this Section must be
inspected
and monitored in accordance with the following
requirements:
A)
An initial leak detection monitoring of the closed-vent system must
be
conducted by
the owner or operator on or before the
date
that the system
becomes
subject
to this Section. The owner or operator must monitor the closed-vent
system components and connections using the procedures specified in Section
725.934(b)
to
demonstrate that the closed-vent system operates with no
detectable
emissions, as indicated
by
an instrument reading of less than 500
ppmv above
background.
B)
After
initial leak detection monitoring required
in
subsection
(k) (1)
(A)
of this Section,
the owner
or
operator must inspect
and monitor the
closed-vent
system as
follows:
i)
Closed-vent system
joints,
seams, or other
connections
that are
permanently or
semi-permanently sealed
(e.g., a
welded
joint
between two
sections of
hard piping or
a
bolted and gasketed
ducting flange)
must
be
visually inspected at
least once per year
to
check
for
defects that could result
in air
pollutant emissions. The owner or operator must monitor
a
component
or
connection
using the procedures specified in Section
725.934(b)
to
demonstrate
that it operates
with no detectable emissions following any time the component
is repaired or replaced
(e.g., a
section of damaged hard piping is replaced with
new hard piping) or the connection is unsealed
(e.g.,
a flange is
unbolted).
ii)
Closed-vent system components or connections other than those specified in
subsection
(k) (1) (B) (i)
of this Section must be monitored annually and at other
times
as
requested by the Agency, except as provided for in subsection
(n)
of
this
Section, using the procedures specified in Section
725.934(b)
to
demonstrate that the components or connections operate with no detectable
emissions.
C)
In
the event that
a
defect or leak is
detected,
the owner or operator must
repair
the defect or leak in accordance with the requirements of subsection
(k) (3)
of this Section.
D)
The owner or operator must maintain a record of the inspection and
monitoring in accordance with the requirements specified in Section 725.935.
2)
Each closed-vent system that is used to comply with subsection
(j)
(2)
of
this Section must be inspected and monitored in accordance with the following
requirements:
A)
The
closed-vent
system must be
visually inspected
by the owner or operator
to
check for defects that could
result
in air pollutant emissions. Defects
include, but are not limited to,
visible
cracks, holes, or gaps in ductwork or
piping or loose
connections.
B)
The
owner or operator must perform an initial inspection of the closed-
vent
system on or before the
date
that the system becomes
subject to
this
Section.
Thereafter, the owner or operator must perform
the
inspections
at
least once
every year.
C)
In
the event that
a
defect or leak is detected, the owner or operator
must
repair
the defect in accordance with the requirements of subsection
(k) (3)
of
this Section.
D)
The owner or operator must maintain a record of the inspection and
monitoring in accordance with the requirements specified in Section 725.935.
3)
The owner or operator must repair all detected defects as follows:
A)
Detectable
emissions,
as
indicated
by visual inspection or by an
instrument
reading greater than
500
ppmv
above background, must be
controlled
as
soon as
practicable, but not
later than
15 calendar days after the
emission
is
detected,
except as
provided for in
subsection
(k)
(3) (C)
of this
Section.
B)
A
first attempt at
repair must
be
made no later than five calendar
days
after the emission is detected.
C)
Delay of
repair of
a
closed-vent system for which leaks have been detected
is allowed if
the repair is technically infeasible without a process unit
shutdown, or
if the owner or operator determines that emissions resulting from
immediate
repair would be greater than the fugitive emissions likely to result
from delay of
repair. Repair of such equipment must be completed by the end of
the next process
unit shutdown.
D)
The owner
or operator must maintain
a
record of the defect repair in
accordance with
the requirements specified in Section 725.935.
1)
A
closed-vent system or control device
used to
comply with provisions of
this Subpart AA must be
operated
at
all times when emissions may be vented
to
it.
m)
The owner or
operator using
a
carbon adsorption system to control air
pollutant emissions
must document that all carbon removed that is a hazardous
waste and that is
removed from the control device is managed in one of the
following manners,
regardless of the volatile organic concentration of the
carbon:
1)
It is
regenerated or reactivated in a thermal treatment unit that meets
one of the
following:
A)
The
owner or operator of the unit has been issued a final permit under
35
Ill. Adm. Code
702, 703, and 705 that implements the requirements of Subpart X
of 35 Ill.
Adm. Code 724; or
B)
The
unit is equipped with and operating air emission
controls in
accordance
with the applicable requirements of Subparts AA and CC of
this
Part
or
35
Ill.
Adm. Code 724; or
C)
The
unit is equipped with and operating air
emission controls in
accordance
with a federal national emission standard
for hazardous air
pollutants
under 40 CFR 61
(National
Emission
Standards for Hazardous Air
Pollutants)
or 63
(National
Emission Standards for
Hazardous Air Pollutants
for
Source
Categories), each incorporated by reference in 35
Ill. Adm.
Code
720.111(b).
2)
It is incinerated
in
a
hazardous waste incinerator for which the owner
or
operator has done
either of
the
following:
A)
The owner or
operator has been issued
a
final permit under 35 111. Adm.
Code
702, 703, and 705
that implements the requirements of Subpart
0
of 35 Ill.
Adm.
Code 724; or
B)
The owner
or operator has designed and operates the incinerator in
accordance
with the interim
status
requirements of Subpart 0 of this Part.
3)
It
is burned in a boiler or industrial furnace for which the owner or
operator
has done either of the following:
A)
The
owner
or
operator has been
issued
a final permit under 35 Ill.
Adm.
Code
702, 703,
and
705
that implements
the requirements
of Subpart H of
35
Ill.
Adm.
Code 726;
or
B)
The
owner or operator has
designed and operates
the boiler or industrial
furnace
in
accordance with the interim
status requirements
of Subpart H of
35
Ill.
Adm. Code
726.
n)
Any components
of
a closed-vent system
that are designated, as described
in
Section 725.935
Cc)
(9),
as unsafe
to
monitor
are exempt from the requirements
of subsection
(k) (1)
(B)
(ii)
of this Section
if both of the following conditions
are fulfilled:
1)
The
owner or operator
of the closed-vent
system has determined that the
components of the
closed-vent
system are unsafe
to monitor because monitoring
personnel would be
exposed
to an immediate
danger as a consequence of
complying
with subsection
(k) (1)
(B)
(ii)
of this Section;
and
2)
The owner or operator of the closed-vent
system adheres to
a
written
plan
that requires
monitoring
the closed-vent
system components using the procedure
specified in
subsection
(k) (1) (B) (ii)
of this
Section as frequently as
practicable during
safe-to-monitor
times.
(Source:
Amended at 33 Ill. Reg.
—,
effective
ILLINOIS REGISTER
ui.
CONTROL
NOTICE
OF PROPOSED
E1MENT
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Input:
TITLE 35:
ENVIRONMENTAL PROTECTION
SUBTITLE G:
WASTE DISPOSAL
CHAPTER
I:
POLLUTION CONTROL BOARD
SUBCHAPTER
C:
HAZARDOUS WASTE OPERATING
REQUIREMENTS
PART 728
LARD DISPOSAL RESTRICTIONS
SUBPART A:
GENERAL
Section
728.101
728.102
728.103
728
.104
728.105
728.106
Subpart C
728.107
Treaters,
728.108
728 .109
Purpose, Scope, and Applicability
Definitions
Dilution Prohibited as
a
Substitute for
Treatment
Treatment Surface Impoundment Exemption
Procedures for Case-by-Case Extensions
to an
Effective Date
Petitions to Allow Land Disposal of
a
Waste
Prohibited Pursuant to
Testing, Tracking, and Recordkeeping Requirements
for Generators,
and Disposal Facilities
Landfill and Surface Impoundment Disposal
Restrictions (Repealed)
Special Rules for Characteristic Wastes
SUBPART B:
SCHEDULE FOR LARD DISPOSAL PROHIBITION
AND ESTABLISHMENT OF
TREATMENT STANDARDS
Wastes Whose
Treatment
Standards Were Vacated
728.138
Waste-Specific Prohibitions:
Newly-Identified Organic Toxicity
Characteristic
Wastes and Newly-Listed Coke
By-Product and Chlorotoluene
Production Wastes
728.139
Waste-Specific Prohibitions: Spent Aluminum Potliners and
Carbamate
Wastes
SUBPART D:
TREATMENT STANDARDS
Section
728.140
Section
728.110
First Third (Repealed)
728.111
Second Third (Repealed)
728.112
Third Third (Repealed)
728.113
Newly Listed Wastes
728.114
Surface Impoundment Exemptions
SUBPART C:
PROHIBITION
ON
LAND DISPOSAL
Section
728.120
Waste-Specific Prohibitions: Dyes and Pigments Production Wastes
728.130
Waste-Specific Prohibitions: Wood Preserving Wastes
728.131
Waste-Specific
Prohibitions: Dioxin-Containing Wastes
728.132
Waste-Specific Prohibitions:
Soils Exhibiting the Toxicity
Characteristic for
Metals and Containing
PCB5
728.133
Waste-Specific Prohibitions:
Chlorinated Aliphatic Wastes
728.134
Waste-Specific Prohibitions: Toxicity Characteristic Metal Wastes
728.135
Waste-Specific Prohibitions: Petroleum Refining Wastes
728.136
Waste-Specific Prohibitions:
Inorganic Chemical Wastes
728.137
Waste-Specific
Prohibitions: Ignitable and Corrosive Characteristic
Applicability of Treatment Standards
Treatment Standards Expressed
as
Concentrations
in Waste Extract
Treatment Standards Expressed
as Specified Technologies
Treatment Standards Expressed
as
Waste
Concentrations
Adjustment of
Treatment Standard
Treatment Standards
for Hazardous Debris
Alternative Treatment
Standards Based on HTMR
Universal Treatment
Standards
Alternative LDR Treatment
Standards for Contaminated Soil
SUBPART E:
PROHIBITIONS ON STORAGE
Section
728.150
Prohibitions on
Storage of Restricted Wastes
728.Append4*APPENDIX
A Toxicity
Characteristic Leaching Procedure
(TCLP)
(Repealed)
728.Appe4APEID1X
B Treatment
Standards
(As
concentrations in
the Treatment
Residual
Extract)
(Repealed)
728.Appei4iAPPEND1X
C List of Halogenated Organic Compounds
Regulated under
Section 728.132
728. Apped4.EEEND1X D
728. Appe 4APEED1X E
728. Appe44-*PPE F
728. Apped4*APPEj G
728.
Appe44*APPEN]2IX
H
728.
Appeed- EAEPENDIX
I
728.
Appeed4*APPE11D1X
J
Requirements (Repealed)
728.Appe3d4*AEPENIX
K Metal-Bearing
Wastes Prohibited from Dilution
in a
Combustion
Unit According
to Section
728.103(c)
AUTHORITY:
Implementing Sections 7.2
and 22.4 and authorized by Section
27 of
the
Environmental Protection Act
[415
ILCS 5/7.2, 22.4, and
271
SOURCE: Adopted in R87-5 at 11 Ill. Reg. 19354,
effective November 12, 1987;
amended in R87-39 at 12 Ill. Reg. 13046, effective July
29, 1988; amended in
R89-l at 13 Ill. Reg. 18403, effective November 13, 1989;
amended in R89-9
at
14
Ill. Reg. 6232, effective April 16, 1990; amended in R90-2
at 14 Ill. Reg.
14470,
effective August
22, 1990; amended in R90-10
at
14 Ill. Reg.
16508,
effective
September 25, 1990;
amended in R90-l1 at 15 Ill. Reg.
9462, effective
June 17, 1991; amended in R90-ll
at 15 Ill. Reg. 11937, effective August
12,
1991; amendment withdrawn at 15 111. Reg. 14716,
October 11, 1991; amended in
R91-l3 at 16 Ill. Reg. 9619, effective June
9,
1992; 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-l6
at
18 Ill.
Reg. 6799,
effective April
26, 1994;
amended in R94-7 at 18 Ill. Reg.
12203, effective July
728.141
728.142
728.143
728.144
728.145
728.146
728.148
728.149
Wastes Excluded from Lab Packs
Organic Lab Packs (Repealed)
Technologies
to
Achieve
Deactivation of Characteristics
Federal Effective Dates
National Capacity LDR Variances
for UIC Wastes
EP Toxicity Test Method and Structural
Integrity Test
Recordkeeping, Notification, and Certification
728.TablcTABLE A
728.Tab1cTABLE B
728.TablcTABLE
C
728.TablcTABLE D
728.Tpb1cTABLE E
728.Tpb1cTABLE F
728.Tpb1cTABLE G
728.Tab1eTABLE H
728.Tab1cTABLE I
728.Tab1cTABLE T
Constituent Concentrations
in Waste Extract
(CCWE)
Constituent Concentrations
in Wastes
(CCW)
Technology
Codes
and
Description of Technology-Based
Technology-Based Standards
by RCRA Waste Code
Standards for Radioactive
Mixed Waste
Alternative Treatment Standards
for Hazardous Debris
Alternative Treatment
Standards Based on HTMR
Wastes Excluded from CCW
Treatment Standards
Generator Paperwork Requirements
Treatment Standards for
Hazardous Wastes
Standards
728.Tab1cTABLE
U
Universal Treatment
Standards
(UTS)
29, 1994; amended
in R94-17
at 18 Ill. Reg. 17563, effective November
23,
1994;
amended in R95-6 at
19 111. Reg.
9660, effective June 27, 1995;
amended in
R95-
20
at
20 Ill. Reg.
11100,
effective August 1, 1996; amended
in R96-l0/R97-3/R97-
5
at
22 Ill. Reg.
783, effective
December 16, 1997; amended
in R98-12 at
22
111.
Reg. 7685,
effective April 15,
1998; amended in R97-2l/R98-3/R98-5
at 22
Ill.
Reg. 17706,
effective September
28, 1998; amended in R98-21/R99-2/R99-7
at
23
Ill. Reg.
1964, effective January
19, 1999; amended in R99-15
at 23
Ill.
Reg.
9204, effective
July 26,
1999; amended in R00-13 at 24 Ill. Reg.
9623,
effective
June 20, 2000;
amended in R01-3
at 25 Ill. Reg. 1296, effective January
11,
2001; amended in
R01-21/R01--23
at 25 Ill. Reg. 9181, effective
July 9, 2001;
amended in
R02-l/R02-12/R02-17
at 26 Ill. Reg. 6687, effective
April 22, 2002;
amended in R03-18 at 27 Ill. Reg. 13045, effective
July 17, 2003; amended in
R05-8
at 29
Ill. Reg. 6049, effective April 13,
2005; amended in R06-5/R06-
6/R06-7 at 30
Ill. Reg. 3800, effective
February 23, 2006; amended in R06-
l6/R06-17/R06-18 at 31 111. Reg. 1254, effective
December 20, 2006; amended in
R07-5/R07-14 at 32 Ill. Reg. 12840, effective
July 14, 2008; amended in R09-3
at
33
Ill.
Reg.
—,
effective
SUBPART A:
GENERAL
Section 728.102
Definitions
When used in
this Part, the
following terms have the meanings given below. All
other terms
have the meanings
given under 35 Ill. Adm. Code 702.110, 720.110,
or
721.102 through
721.104.
“Agency” means the Illinois Environmental Protection Agency.
Board’ means the
Illinois
Pollution Control Board.
TTCERCLA
means
the Comprehensive
Environmental Response, Compensation, and
Liability Act of 1980
(42
USC 9601 et seq.)
DebrisTT
means solid material exceeding a 60 mm particle size that is intended
for disposal and that is a manufactured object; plant or animal matter; or
natural geologic material. However, the following materials are not debris:
any material for which a specific treatment standard is provided in Subpart
D of
this Part, namely lead acid batteries, cadmium batteries, and radioactive lead
solids; process
residuals,
such as smelter slag and residues from the treatment
of waste,
wastewater, sludges,
or air emission residues; and intact containers
of hazardous waste
that are
not ruptured and that retain at least 75 percent
of
their original
volume. A
mixture of debris that has not been treated to the
standards
provided
by
Section 728.145
of this Part and other material is
subject
to
regulation
as
debris if the mixture
is comprised primarily of debris, by
volume, based on visual inspection.
“Halogenated organic
compoundsTT
or “Hocs” means those compounds having
a carbon-
halogen bond that are listed under Appendix C of this Part.
“Hazardous
constituent
or constituents” means those constituents listed in
Appendix H to 35 Ill. Adm. Code 721.
“Hazardous
debris” means
debris that contains a hazardous waste listed in
Subpart D
of
35
Ill. Adm.
Code 721 or that exhibits a characteristic of
hazardous
waste identified
in Subpart C of 35 Ill. Adm.
Code
721. Any
deliberate
mixing of prohibited
waste
with
debris that changes its treatment
classification
(i.e.,
from waste
to
hazardous
debris)
is not allowed under
the
dilution prohibition
in
Section
728.103.
ITlnorganic
metal-bearing
waste’ is one
for which USEPA
has established
treatment
standards
for
metal hazardous
constituents
that does
not otherwise
contain
significant
organic
or
cyanide
content, as described
in
Section 728.103(b)
(1),
and which
is
specifically
listed
in Appendix K of
this
Part.
“Land
disposal”
means placement
in or on
the land, except
in
a
corrective
action
management
unit
or staging
pile, and “land
disposal”
includes,
but
is not
limited
to,
placement
in
a landfill,
surface impoundment,
waste pile,
injection
well,
land
treatment
facility,
salt
dome formation,
salt bed
formation,
underground
mine or cave,
or placement
in a concrete
vault
or bunker intended
for
disposal
purposes.
“Land disposal
restriction”
or “LDR”
is
a
restriction
imposed on the land
disposal
of
a hazardous
waste pursuant
to this Part
or 40
CFR 35 Ill. Adm.
Code
738. The land
disposal of
hazardous waste
is
generally prohibited,
except where
the
activity
constituting land
disposal is
cpccficallysoeciticallv
allowed,
pursuant
to
this
Part or 40 CFR
738.
BOARD NOTE:
The Board
added this definition
based
on
the preamble discussions
at
51 Fed. Reg.
40572,
40573-74
(November
7,
1986)
and 53
Fed. Reg. 28118,
28119-20
(July 26,
1988)
.
The USEPA
publication
“Terms of Environment
Glossary,
Abbreviations,
and Acronyms”
(December
1997),
USEPA,
Communications,
Education,
and Public
Affairs,
EPA 175/3-97-001,
defines
“land
disposal restrictions”
as
follows:
“Rules that
require
hazardous wastes
to be
treated before disposal
on
land to
destroy
or immobilize
hazardous
constituents
that
might migrate
into
soil and
ground
water.”
“Nonwastewaters”
are wastes that
do not meet
the
criteria for “wastewaters”
in
this Section.
“Polychlorinated
biphenyls”
or “PCBs” are
halogenated organic
compounds defined
in accordance
with federal 40
CFR 761.3
(Definitions),
incorporated
by reference
in 35 Ill.
Adm.
Code
720.111(b)
“ppm”
means
parts per million.
TT
RCRA corrective
action”
means corrective
action
taken
under
35
Ill. Adm.
Code
724.200 or
725.193, federal
40 CFR
264.100 or 265.93,
or
similar regulations
in
other states
with RCPA programs
authorized
by USEPA
pursuant
to
40 CFR 271.
“Soil”
means
unconsolidated
earth material
composing
the superficial
geologic
strata
(material
overlying
bedrock),
consisting
of clay,
silt, sand,
or gravel
size
particles,
as
classified
by
the United States
Natural
Resources
Conservation
Service,
or a mixture
of such materials
with liquids,
sludges,
or
solids
that
is inseparable
by simple mechanical
removal
processes
and
which
is
made
up
primarily
of soil
by
volume
based
on visual
inspection. Any
deliberate
mixing
of
prohibited
waste with
debris that changes
its
treatment classification
(i.e.,
from
waste
to
hazardous
debris)
is not allowed
under
the dilution
prohibition
in Section 728.103.
“Underlying
hazardous
constituent”
means any constituent
listed in
Table
U of
this Part,
“Universal
Treatment Standards
(UTS) ,“ except
fluoride, selenium,
sulf ides,
vanadium,
and
zinc, that can
reasonably
be
expected
to be present
at
the
point
of
generation
of
the hazardous waste
at a
concentration
above
the
constituent-specific
UTS treatment
standard.
“USEPA
T
’
or
“U.S. EPA
means the United
States
Environmental
Protection Agency.
“Wastewaters”
are wastes that
contain less than
one
percent by
weight total
organic
carbon
(TOC)
and
less than
one percent
by
weight total suspended
solids
(TSS)
(Source:
Amended at 33 Ill.
Reg.
,
effective
ILLINOIS
REGISTER
I
POLLUTION
CONTROL
BOD
I
NOTICE
OF
PROPOSED 1ENDMEN
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