United States EPA Region I August 1990
Environmental Protection Waste Management
Agency Division
Land Disposal Restrictions
Summary of Requirements
TREATMENT
LAND DISPOSAL
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^ ^ UNITED STATES ENVIRONMENTAL PROTECTION AGENCY
jgjjf REGION I
J? J.F. KENNEDY FEDERAL BUILDING, BOSTON, MASSACHUSETTS 02203-2211
WW*"
Dear Reader:
The Land Disposal Restrictions (LDR) regulations have been
implemented in a series of five (5) rules. These rules,
promulgated between November, 1986 and May, 1990, restrict the
disposal of hazardous waste in or on the land. All generators of
hazardous waste, as well as treatment, storage, recycling, and/or
disposal facilities, are impacted by the LDR program. Because of
this, it is important for you to examine and understand the
requirements and to determine whether and how each of the LDR
rules applies at your facility.
To help you understand this complex and far-reaching program,
Region I has prepared this information package explaining the
Land Disposal Restrictions rules published since June, 1990. We
encourage you to read this information. It is important to
understand that the LDR requirements, which continue EPA's
philosophy of tracking waste from "cradle to grave" and ensure
that untreated hazardous waste is not land disposed, apply to all
shipments of hazardous waste regardless of the actual treatment
and/or disposal method used. For this reason, you should examine
this document, as well as the regulations, and evaluate all
hazardous wastes handled at your facility to determine LDR
applicability.
This information package provides a brief overview of the
regulations and explains each of the five rules in detail. In
addition, the tables of "treatment standards", which must be
consulted to determine whether a waste is prohibited from land
disposal, have been reprinted in the Appendix to this document
for ease of reference.
Again, please take the time to read this document to ensure your
facility's compliance with these regulations. For any additional
information or clarifications you may need, please contact the
RCRA/Superfund Hotline at (800) 424-9346, Region I's RCRA Support
Section at (617) 573-5750, or Robert Cianciarulo at (617)
573-5778. Written inquiries about this publication or the Land
Disposal Restrictions should be directed to the LDR contact in
the nearest EPA Regional Office or, in Region I, to the address
above, to the attention of Robert Cianciarulo, mail code
HRW-CAN3.
Sincerely,
Merrill S. Hohman, Director
Waste Management Division
PRINTED ON RECVCLED PAPER
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DISCLAIMER
This document presents a brief summary of the Land Disposal Restrictions (LDR) regulations.
It is not meant to be a complete or detailed description of all applicable LDR regulations.
For more information concerning specific requirements, consult the Federal Registers cited
herein and the Code of Federal Regulations, Title 40 Parts 260-271.
Land Disposal Restrictions Work Group
Region I
August 1990
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TABLE OF CONTENTS
Section Page
I. INTRODUCTION 1
II. GENERAL PROVISIONS OF THE LAND DISPOSAL RESTRICTIONS
(LDR) PROGRAM 3
A. Applicability (§268.1) 3
B. Dilution Prohibition (§268.3) 3
C. Storage (§268.50) 3
D. Testing and Recordkeeping (§268.7) 4
1. Generator Responsibilities (§268.7) 4
a. Wastes Not Meeting Treatment Standards 7
b. Wastes Meeting Treatment Standards or Subject to an
Extension 7
c. On-site Treatment of Wastes 8
2. Treatment and Storage Facility Responsibilities (§268.7) 8
3. Land Disposal Facility Responsibilities (§268.7) 9
E. Permit Program 9
1. Interim Status Facilities (§270.72) 9
2. Permitted Facilities (§270.42) 10
F. Variances, Extensions and Exemptions 10
1. National Capacity Variance (§§268.30 - 268.35) 10
2. Case-by-Case Extension (§268.5) 11
3. Treatability Variance (§268.44) 11
4. Equivalent Method Variance (§268.42(b)) 11
5. No Migration Petition (§268.6) 12
6. Surface Impoundment Exemption (§268.4) 12
III. SOLVENT-DIOXIN RULE 13
A. Treatment Standards (§268.40) . 13
B. Solvent Treatment Standards (§268.41) 13
C. Dioxin Treatment Standards (§268.41) 15
IV. FIRST THIRD RULE, SECOND THIRD RULE, THIRD THIRD RULE 15
A. Testing Requirements 16
B. Characteristic Wastes (§268.9) 16
C. Alternative Treatment Standards for Lab Pack Wastes (§268.7(a)) 18
D. Small Quantity Generator Tolling Agreements (§268.7(a)(9)) 18
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TABLE OF CONTENTS (Continued)
Section Page
V. CALIFORNIA LIST RULE 19
A. Applicability 19
B. Regulated Materials 19
1. Halogenated Organic Compounds (HOCs) 20
2. Polychlorinated Biphenyls (PCBs) 20
APPENDICES
A Notification and Certification Requirements A-1
B Treatment Standards B-l
C Lab Packs C-l
FIGURES
Number Page
1 Generator Requirements 6
TABLES
Number Page
1 Land Disposal Regulations 2
2 Appendix B Contents 5
3 Solvent Treatment Standards 14
4 CCW - Constituent Concentrations in Waste 15
5 Technology-Based Standards by RCRA Waste Code 15
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LAND DISPOSAL RESTRICTIONS
Summary of Requirements
I. INTRODUCTION
On November 8, 1984, the President signed into law the Hazardous and Solid Waste
Amendments (HSWA) to the Resource Conservation and Recovery Act (RCRA). Among
other things, these Amendments require EPA to evaluate all listed and characteristic
hazardous wastes according to a strict schedule to determine which wastes should be
restricted from land disposal. This portion of the HSWA is known as the Land Disposal
Restrictions (LDR).
For wastes that are restricted, the Amendments require EPA to set concentration levels or
methods of treatment, both of which are called "treatment standards", that substantially
diminish the toxicity of wastes or reduce the likelihood that hazardous constituents from
wastes will migrate from the disposal site. After the effective date of the restriction, wastes
that do not meet the treatment requirements are prohibited from land disposal. According to
HSWA, if EPA fails to set the treatment standard for a particular waste by the specified
deadline, that waste is automatically subject to land disposal restrictions specified in the
statute.
In the first rule implementing the land disposal restrictions, published on November 7, 1986,
EPA defined land disposal to include, but not be limited to, any placement of hazardous
waste in:
• Landfills
• Surface impoundments
• Waste piles
• Injection wells
• Land treatment facilities
• Salt domes or salt bed formations
• Underground mines or caves
• Concrete vaults or bunkers, intended for disposal
purposes
Information concerning land disposal rules published to date can be found in Table 1.
Federal Registers cited therein can be obtained by contacting the EPA RCRA/Superfund
Hotline at 1-800-424-9346.
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TABLE 1. LAND DISPOSAL REGULATIONS
Date
Federal Register
Contents
May 28, 1986
Nov. 7, 1986
June 4, 1987
July 8, 1987
July 26, 1988
August 16, 1988
August 17, 1988
May 2, 1989
June 23, 1989
September 6, 1989
March 29, 1990
June 1, 1990
51 FR 19300
51 FR 40572
52 FR 21010
52 FR 25760
53 FR 28118
53 FR 30908
53 FR 31138
54 FR 18837
54 FR 26594
54 FR 36967
55 FR 11796
55 FR 22520
provides implementation schedule
solvents & dioxins
corrections to November 7, 1986
rule
"California List Wastes"
(halogenated wastes, certain metal-
bearing wastes, polychlorinated
biphenyls (PCBs), and cyanide and
corrosive wastes)
Underground Injection Control
(UIC): solvents and dioxins
UIC: California List and some
"First Third" Wastes (specific F, K,
P and U wastes)
"First Third" Wastes (see §268.10)
Amendments to "First Third" Rule
"Second Third" Wastes (see
§268.11)
Corrections to August 17, 1988 and
May 2, 1989 rules
Listing of Toxicity Characteristic
Waste Codes D018-D043
"Third Third" Wastes and
Characteristic Wastes (D001-D017)
(see §268.12)
The general provisions of all LDR regulations promulgated as of June 1990 are described in
this booklet. Notations, such as §268.30, appearing in this document, refer to the section of
Title 40 of the Code of Federal Regulations (CFR) in which information pertaining to the
specific subject matter can be found.
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II. GENERAL PROVISIONS OF THE LAND DISPOSAL RESTRICTIONS (LDR)
PROGRAM
A. Applicability (§268.1)
The requirements of the LDR apply to all persons who generate or transport hazardous wastes
and owners and operators of hazardous waste treatment, storage and disposal facilities except
as specifically provided otherwise (e.g., 40 CFR Parts 261 and 268). Wastes disposed of
before November 8, 1986 do not have to be removed from a land disposal unit for treatment.
However, if wastes are removed from a land disposal unit, the wastes must meet the
applicable treatment standard before subsequent placement in or on the land.
Since the LDR became effective, several questions have arisen concerning the applicability of
the restrictions to wastes which are classified as hazardous by State regulation. If a waste
cannot be identified by an EPA hazardous waste code, then that waste is not subject to the
LDR. If, however, a State regulated waste (such as waste paint or waste oil) could also be
characterized by an EPA waste code (e.g., D001, etc.), that waste is subject to the
requirements of the LDR.
B. Dilution Prohibition (§268.3)
The LDR rule prohibits the dilution of restricted wastes as a substitute for adequate treatment.
This provision ensures that no individual avoids the intent of EPA's regulations by simply
diluting, rather than actually treating the waste.
Dilution as a necessary part of the waste treatment process, however, is allowed in the LDR
program. For example, the addition of an acid or base reagent to a waste in a neutralization
tank does not merely dilute the waste into a larger volume of waste; rather, the addition of
the reagent is a normal process of physically or chemically altering the waste to render it less
hazardous. A detailed discussion of the dilution prohibition, as well as several examples of
permissible and impermissible dilution, can be found in the preamble to the Third Third Rule
(55 FR 22520).
C. Storage (§268.50)
Under the LDR program, generators and permitted or interim status treatment, storage, and
disposal (TSD) facilities may store restricted wastes solely for the purpose of accumulating
sufficient quantities of waste to facilitate proper treatment, recovery, or disposal. If the TSD
facility stores a restricted waste for more than one year, it bears the burden of proof that
storage was solely for this purpose. For storage of less than one year, however, EPA bears
the burden of proof.
An exception to this is liquid hazardous waste containing PCBs at concentrations greater than
or equal to 50 ppm; these cannot be stored for more than one year.
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In order for EPA to track the length of time LDR wastes are stored, all containers in storage
must be clearly marked with the date that they entered the facility.
Wastes that are placed in storage prior to the effective date of the restrictions for that waste
are not subject to the restrictions on storage. However, once taken out of storage, these
wastes must meet the applicable treatment standards prior to land disposal.
D. Testing and Recordkeeping (§268.7)
The testing and recordkeeping requirements of the LDR rule reflect EPA's philosophy of
tracking wastes from generation to ultimate disposal. All restricted wastes, whether treated
and disposed on-site or sent off-site to a RCRA treatment, storage, or disposal facility, are
subject to the testing and recordkeeping requirements, which include notification
requirements. These requirements also apply to recycling facilities because the wastes they
receive and the resulting residues may be subject to the LDR.
For example, if a cyanide plating bath is sent to a recycling facility for precious metals
recovery, that waste is still subject to the LDR notification requirements.
Unless specifically excluded from the Part 268 regulations in 40 CFR Part 261 or Part 268,
all shipments of hazardous wastes are subject to the notification requirements of §268.7.
1. Generator Responsibilities (§268.7)
For each hazardous waste that it generates, the generator must determine whether the waste is
subject to the LDR rules.
To assist in this process, the generator should determine:
What regulated constituents and their concentrations are present in the waste;
• All applicable EPA waste codes (see also Section IV: Characteristic Wastes);
• Which treatment standards or prohibition levels apply (depending on the
subcategory of the waste and the treatability group); and
• Whether the waste must be treated or already meets the applicable treatment
standard or prohibition level upon generation.
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The generator can make this determination based on knowledge of the waste, or, as specified
in the regulations, by conducting a total waste analysis or by testing the waste extract
resulting from the Toxicity Characteristic Leaching Procedure (TCLP) (see 40 CFR 268,
Appendix I). If the generator uses his knowledge of the waste to determine whether the
waste is restricted from land disposal, the generator must maintain records at the facility of all
supporting data used to make the determination (§268.7 (a)(5)).
The basic generator requirements can be found in the flowchart (Figure 1) on the following
page. For more information regarding notification requirements, the generator should refer to
the following text, Appendix A of this document, and the applicable regulations.
Numerous tables of treatment standards established for each waste code have been published
in 40 CFR Part 268. Appendix B of this document (see Table 2) provides several of these
tables for ease of reference.
TABLE 2. APPENDIX B CONTENTS
Title
55 FR 40 CFR
Page No. Section
Constituent Concentrations in Waste Extract
Constituent Concentrations for Waste Extracts
Technology-Based Standards by RCRA Waste Code
Technology-Based Standards for Specific
Radioactive Hazardous Mixed Waste
Constituent Concentrations in Wastes
22690
22692
22694
22700
22701
§268.41
§268.41
§268.42
§268.42
§268.43
Since a waste may be listed in more than one table, it is important for generators to examine
every table prior to determining the appropriate treatment standard(s) for each waste
generated.
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Identity Waste:
Chemical CempoeMori; Source
Determine EPA Wnle Code(e) (| 261)
(Include ill Applicable Charaeterletlc and
Lilted Codes)
Determine T re (lability Group and Subcategory
(e.g., waeteweter, non-weete water, etc.)
Look Up Treatment Stendarde
lor Waate Code(»y T reetablllty Qroup(e)
(|368 Subpart D)
Other
Conatltuente
Preaent In Waate which
¦re Not Lifted In Treatment
9tandarde lor
Waate Code(S)
1
DoeeNOT
Exceed
Treatment
Stendarde
For ALL
Conatltuente
Determine
Whether Waate Eiceeda Each
Applicable Treatment Standard
by Knowledge or Testing
(»2««.7(a))
With Each Shipment:
| NOTIFICATION ($268.7(a)(2))
A) Waste Code(s)
B) Applicable Treatment
Standard(s)
C) Manifest Number
D) Waste Analysis Data
(if available)
I CERTIFICATION (|268.7(a)(2XII))
| RECORDKEEPING (|26&7(aK6)>
Retain Copies for S Years
To Treatment, Storage,
Recycling or
Land Dlspoaai Facility
With Each Shipment
No
NOTIFICATION (1268.7(e)(1))
(i) Waste Code(s)
(II) All Applicable Treetment
Stsndards(s)or Prohibition
Levels
(ID) UsnKsst Numbsr
(lv) Wssts Analysis Data
(H available)
RECORDKEEPING (|2M.7(aXI)))
Retain Copiea lor 6 Year*
Yes
1
To Treatment, Storage,
or Recycling Facility
Is
Waste
Eligible for a National
Capacity Variance?
(1266 Subpart C and
Appendix W)
Is
Weals Also
Prohibited Under
the California List (|2M J2, RCRA |MM(d))7
UqddWSeMe: Free Cynldee 2 KMOmgl.
SeilOOmgl TI?1J0mgfl.
Hg^Mmg/L M»1l4m0L
Ae2SMmg/L Cd»100rng/L
CrVUMOmg/L Pb^Mftngl
PCSei MmgfL
pHsJ
HOCeJiOOOmg/l
HOOislHOngAg
Waste la Prohibited Under the California
Liat ($2611.32, RCRA 13004(d)):
LIQUID WASTES:
Free Cyanides 2 1000 mgl
PCBs 2 SO mg/L
Nickel 2134 mg/L
Thalliums 130 mg/L
UQUD AND NON-LIQUID WASTES:
Halogenated Organic Cornpounds|
(not Mdrsssed by Treatment
Standarde)
21000 ppm
THEN
the Waata must meet those Prohibition
Levels as wit and must be Indudad on
the LDR Notification.
With Each Shipment:
| NOTIFICATION (|26t. 7(e)(5))
(I) Waste Code(s)
(I) Applicable Treatment
Standards)
(HI) Manlfeat Number
(hr) Waata Analysis 0(ta
(if svsllable)
(v) Oate the Waate is eubieet
to the prohibitions
1RECORDKEEPING (|2«.7(sX6»
Hstaln Coptsi tor g Years
To TfMtrmnt, Stomp, RoeyeJlr>g or
Lend Dlspoaai Faomty: H Wastes we
Pieced In a Landfill or Surf so*
Impoundment, the lacllty must mset
the minimum technologic^
roqulremente xt |266.»(h)
Figure 1. Generator Requirements
Note: This flowchart can be used as a guide only. For a complete discussion of the
generator's notification requirements, refer to the text of this document as well as the
regulations. Also, since different n 'cations and certifications apply for Characteristic
Wastes which have been treated until rendered non-hazardous and "lab pack" waste,
Section IV of this document and pertinent regulations should be consulted for additional
information.
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a. Wastes Not Meeting Treatment Standards
For restricted wastes that do not meet the applicable treatment standards, (i.e., concentration
levels and/or specified technologies listed in Appendix B), the generator must send a notice
containing the following information with each shipment to the receiving facility
(§268.7(a)(l)). "Receiving facility" includes recyclers, reclaimers and incinerators, since
residues from these facilities may ultimately require land disposal. (§268.7 (a)(1))
1. The EPA Hazardous Waste Number(s);
2. The applicable treatment standard(s);
3. The manifest number associated with the waste shipment; and
4. The waste analysis data (if available).
Item (2) above, "applicable treatment standard(s)", must be reported differently depending on
what wastes are being shipped (§268.7 (a)(l)(ii)):
(a) For waste codes F001-F005, F039, or waste subject to the California List
(§268.32—RCRA §3004d), the treatment standard(s) specific to the
constituent(s) contained in the waste and the treatability group to which it
(they) belong(s) must be listed on the notification.
(b) Treatment standards for all other restricted wastes may be referenced by
including the following information on the notification:
(i) Subcategory of the waste (e.g., ignitable liquids, acid corrosives)
(ii) Treatability group(s) of the waste(s) (e.g., wastewater, nonwastewater)
(iii) CFR section(s) and paragraph(s) where the treatment standards appear
(e.g., 40 CFR §268.41 (a)).
(c) Where the applicable treatment standards are expressed as specified
technologies in §268.42, the applicable five-letter treatment code found in
Table 1 of §268.42 (e.g. INCIN, WETOX) also must be listed on the
notification.
b. Wastes Meeting Treatment Standards or Subject to an Extension
If the waste meets all of the applicable treatment standards, the generator may send the waste
directly to a disposal facility. Regardless of where the waste is being sent, with each
shipment the generator must send a notice that provides the four items outlined above.
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The generator must also provide a certification signed by a representative of the company,
stating that the waste meets the treatment standard(s), and that the information included in the
notice is true, accurate, and complete (see 40 CFR 268.7(a)(2) and Appendix A).
Furthermore, if the treatment standard is not currently applicable, the generator is responsible
for notifying the receiving facility. This notification should include the 4 items listed above
in addition to the date the waste will become subject to the prohibitions (see §268.7(a)(3)).
If wastes subject to an extension to the effective date are disposed in a landfill or surface
impoundment, the unit must meet the minimum technological requirements of §268.5(h).
All shipments of restricted waste are subject to the requirements of 40 CFR 268.7, including
shipments to facilities outside of the U.S. and shipments of waste destined for precious metals
recovery or other recycling method not specifically exempted by §261 or §268.
c. On-site Treatment of Wastes
Generators who treat, store or dispose of restricted waste on-site must comply with the
recordkeeping requirements for treatment, storage and disposal facilities. All information
required on the LDR notification described above, with the exception of the manifest number,
must be recorded in the facility's operating record. (§§264.73, 265.73)
If a generator treats a waste in containers or tanks regulated under 40 CFR 262.34 and has
treated such waste to meet applicable treatment standards, the generator must develop and
follow a written waste analysis plan which describes the procedures the generator will carry
out to comply with the treatment standards. The plan must be kept onsite in the generator's
records and also be filed with the EPA Regional Administrator [see 40 CFR 268.7 (a)(4)].
Shipments of these wastes off-site must comply with the notification requirements of
§268.7(a)(2). If a generator treats the waste, but not so that it meets the treatment
standard(s), no such plan is necessary.
Note: Generators must retain copies of all notifications, certifications, and waste analysis data on-site
for at least five years.
2. Treatment and Storage Facility Responsibilities (§268.7)
Treatment facilities must treat restricted wastes to the level specified by the applicable
treatment standard(s) or use the specified treatment method(s).
Each treatment/storage facility is responsible for the following:
Keeping, in its operating record, a copy of the notice and any available waste
analysis data provided by the generator (§§264.73, 265.73); and
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Maintaining the facility's waste analysis plan (§§264.13, 265.13). This must
include:
(1) procedures used to determine which treatment standards apply,
(2) provisions for testing the waste or extract of the waste to determine if it
meets the treatment standard(s) (Alternatively, data supplied by the
generator can be used if corroborative testing is done in accordance
with the waste analysis plan.), and
(3) other procedures necessary for compliance with the LDR.
The treatment/storage facility, like the generator who ships directly to a disposal facility, must
submit a notice and certification to the disposal facility. When a treatment/storage facility
ships wastes to another facility for additional treatment or storage, the notice requirement also
applies. Even when the treatment residue does not go directly to a land disposal facility, the
facility is responsible for keeping the generator's notice in the operating record and sending a
notice to the next receiving facility.
A more detailed discussion of treatment and storage facility responsibilities (more specifically,
the waste analysis plan) may be found in 55 FR 22520.
3. Land Disposal Facility Responsibilities (§268.7)
Land disposal facilities disposing of restricted wastes must maintain generator and treatment
facility notices and certifications. These facilities must also ensure that incoming wastes,
extracts of waste, or treatment residues arc tested using prescribed methods to ensure that
such waste, extracts, or residues meet(s) applicable treatment standard(s). Such testing must
be performed as specified in the facility's waste analysis plan.
Note: Certification statements required of generators, treatment facilities and land disposal
facilities are included as Appendix A of this booklet.
E. Permit Program
1. Interim Status Facilities (§270.72)
Prior to the July 8, 1987 California List Rule, treatment facilities operating under interim
status could increase their operations provided that the facility alterations and expansions did
not exceed 50 percent of the capital cost of a comparable new facility. Interim status
facilities are no longer limited by the 50 percent ceiling for treatment or storage of restricted
wastes in tanks or containers, provided that such changes are made solely for the purpose of
complying with the LDR.
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2. Permitted Facilities (§270.42)
On September 28, 1988, EPA published a rule (53 FR 37912) which established a new
system of procedures for permittee-initiated permit modifications (§270.42). In §270.42
specific facility changes were classified as either Class 1, 2, or 3 modifications. EPA has
subsequently amended §270.42 to allow, as Class 1 modifications, certain facility changes that
are necessary to comply with the LDR rule. Class 1 modifications are generally allowed
without prior agency approval although, in some cases, prior agency approval is required.
Owners and operators of permitted facilities are permitted to add new waste codes, or a
narrative description, to a permit as Class 1 modifications for disposal under certain
conditions where the added wastes are:
(1) restricted wastes that have been treated to meet applicable Part 268 treatment
standards; or
(2) certain wastewater treatment residues and incinerator ash.
The addition of new treatment processes (as long as those processes are necessary to meet
treatment standards and the treatment processes are to take place in tanks or containers) are
also allowed as a Class 1 modification, with prior EPA approval.
Note: It is important to recognize that a permit issued by EPA or an authorized State does
not shield an owner or operator of a treatment, storage, or disposal facility from meeting
the Land Disposal Restrictions requirements.
F. Variances, Extensions and Exemptions
The statute provides a few limited opportunities for delaying the effective date of prohibitions
or gaining an exemption from the prohibitions.
1. National Capacity Variance (§§268.30 - 268.35)
A national capacity variance is provided when EPA determines that sufficient treatment
capacity for certain waste codes is not available on a nationwide basis. When the effective
date for a waste's prohibition is extended, the new effective date is listed in 40 CFR 268.30-
268.35. Appendix VII of Part 268 also provides a list of LDR effective dates for
surface-disposed waste. These sections should be consulted when determining whether a
waste is subject a national capacity variance.
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2. Case-by-Case Extension (§268.5)
In cases where adequate treatment capacity for a specific waste cannot reasonably be made
available by the effective date of prohibition, interested parties may petition EPA for an
extension of the effective date on a case-by-case basis. EPA may grant a case-by-case
extension of up to one year, renewable once for a total of two years.
To be considered for a case-by-case extension, a petitioner must demonstrate that: (1) a good
faith effort has been made to locate adequate treatment capacity (and no such capacity is
available nationwide), (2) he/she has entered into a binding contract to construct or otherwise
provide adequate capacity and (3) such capacity cannot be made available by the prohibition
effective date due to circumstances beyond the petitioner's control.
All wastes receiving extensions (two-year national capacity or case-by-case) may be disposed
in a landfill or surface impoundment only if such unit meets the minimum technological
requirements (MTR) or is exempt from these requirements. MTR provisions require a double
liner, a leachate collection system, and an adequate ground water monitoring system.
3. Treatability Variance (§268.44)
Generators whose wastes cannot be treated to meet the established treatment standards may
petition EPA for a treatability variance. Wastes that may be eligible for a variance include
unique wastes, wastes formed by inadvertent mixing, and wastes that otherwise are different
in physical or chemical properties from those wastes used to set the treatment standards.
For EPA to grant a variance, a petitioner must not only successfully demonstrate that its
waste is significantly different from the waste evaluated by EPA in setting the treatment
standards, but that its waste cannot be treated to meet the treatment standard. The petitioner
must show that attempts to treat 'he waste by available technologies were unsuccessful or that
the waste cannot be treated by the specified technology. In granting a variance, EPA will
establish a new treatability group for that waste and set a new treatment standard.
4. Equivalent Method Variance (§268.42(b))
Where EPA has specified a method of treatment as the treatment standard for a waste, a
generator or facility may submit an application to the EPA Administrator demonstrating that
an alternative treatment method can achieve performance equivalent to that of the method
specified in the treatment standard. If approved, wastes treated by this method can be land
disposed.
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5.
No Migration Petition (§268.6)
An additional alternative for LDR compliance is the no-migration petition. EPA will consider
allowing land disposal of restricted wastes if a petitioner can demonstrate, to a reasonable
degree of certainty, that such disposal will not allow migration of hazardous constituents from
the disposal unit for as long as the waste remains hazardous. A successful no-migration
petition will allow land disposal of a specific waste at a specific site
Until EPA grants a treatability variance, a case-by-case extension or a no migration petition,
the LDR regulations continue to apply to the petitioner.
EPA Guidance documents describing criteria for case-by-case extensions, variances from the
treatment standards, and no-migration petitions are being prepared. (Facilities with
underground injection wells may want to contact the Federal Office of Drinking Water for
information on no-migration petitions in the (JIC program.)
6. Surface Impoundment Exemption (§268.4)
EPA will exempt treatment of restricted waste in surface impoundments from the LDR under
the following conditions:
• The facility samples and analyzes wastes in surface impoundments according to
the facility's waste analysis plan; and
• Liquid and solid treatment residuals nor meeting the treatment standards must
be removed from the surface impoundment at least once every 12 months.
They must be treated to meet the applicable standards before being disposed of,
and may not be placed in another surface impoundment; and
• The facility keeps all records concerning such sampling and removal of wastes;
and
Evaporation of hazardous constituents is not being used as the principal method
of treatment; and
• The surface impoundment meets minimum technological requirements
including a double liner, leachate collection system and ground water
monitoring system; or
• The surface impoundment is operating under a waiver from the requirement to
retrofit surface impoundments with double liners, or under a double-liner
variance for alternate systems [§§3005(j)(2) and (4), 264.221(d) and (e),
265.221(c) and (d), 264.301(d) and (e), and 265.301(c) and (d) j.
12
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Owners or operators of surface impoundments seeking an exemption for treatment of
restricted wastes must certify to the EPA Regional Administrator that the impoundment meets
the minimum technologies requirements, and must submit a copy of the facility's revised
waste analysis plan that outlines methods for representative sampling and proper testing,
frequency of removal, and methods for removal of restricted residuals.
III. SOLVENT-DIOXIN RULE
In the November 7, 1986 final rule, EPA established the framework for implementing the
land disposal restrictions program. This rule restricted the land disposal of solvent- and
dioxin-containing wastes, and is commonly known as the Solvent-Dioxin Rule.
A. Treatment Standards (§268.40)
The Solvent-Dioxin Rule requires that spent solvent wastes with EPA Hazardous Waste Nos.
F001-F005, and dioxin wastes with Nos. F020-F023 and F026-F028 be treated prior to land
disposal. Only solvents used to solubilize (dissolve) or mobilize other constituents are
covered by the F001-F005 listing. A solvent is considered "spent" when it is discarded
because it is no longer useable without being regenerated, reclaimed, or otherwise
reprocessed. Examples of spent solvents include degreasers, cleaners, fabric scourers,
diluents, extractants, and reaction and synthesis media.
B. Solvent Treatment Standards (§268.41)
Different treatment standards are established for two separate groups of solvent wastes. The
groups of solvent wastes are:
• Wastewaters (defined as solvent-water mixtures containing less than 1 percent
total organic carbon (TOC) by weight or less than 1 percent total solvent
constituents by weight.
• All other spent solvent waste, including wastewaters containing 1 percent or
more TOC, solvent-containing solids and solvent-contaminated soils.
Tables 3, 4, and 5 present solvent treatment standards for waste codes F001-F005. This
information has been extracted for ease of reference from Table CCWE - Constituent
Concentrations in Waste Extract, Table CCW - Constituent Concentrations in Wastes, and
Table 2 - Technology-Based Standards by RCRA Waste Code which are printed in their
entirety in Appendix B. These standards are based on the demonstrated performance of
treatment technologies such as steam stripping, biological treatment, activated carbon
treatment, and incineration.
13
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TABLE 3. SOLVENT TREATMENT STANDARDS'
Constituents of F001-F005
Extract Concentrations"
Spent Solvent Wastes
(me/I)
Wastewater
Otherc
Acetone
0.05
0.59
n-Butyl alcohol
5.00
5.00
Carbon disulfide
1.05
4.81
Carbon tetrachloride
0.05
0.96
Chlorobenzene
0.15
0.05
Cresols (cresylic acid)
2.82
0.75
Cyclohexanone
0.125
0.75
1,2-Dichlorobenzene
0.65
0.125
Ethyl acetate
0.05
0.75
Ethylbenzene
0.05
0.053
Ethyl ether
0.05
0.75
Isobutanol
5.00
5.00
Methanol
0.25
0.75
Methylene chloride"1
0.20
0.96
Methyl ethyl ketone
0.05
0.75
Methyl isobutyl ketone
0.05
0.33
Nitrobenzene
0.66
0.125
Pyridine
1.12
0.33
Tetrachloroethylene
0.079
0.05
Toluene
1.12
0.33
1,1,1 -Trichloroethane
1.05
0.41
1,1,2-Trichloro-1,2,2-trifluroethane
1.05
0.96
Trichloroethylene
0.062
0.091
Trichlorofluoromethane
0.05
0.96
Xylene
0.05
0.15
"For determining the applicable treatment standard, F-solvent wastewaters are defined as
solvent-water mixtures containing less than 1 percent total organic carbon or less than
1 percent total solvent constituents.
bAn extract of the waste is obtained by employing the Toxicity Characteristic Leaching
Procedure (TCLP). The TCLP is an analytical method used to determine whether the
concentrations of hazardous constituents in the waste extract or an extract of the treatment
residual meet the treatment standards.
'Wastewaters that contain >1% TOC, solvent-containing solids, solvent-containing sludges,
and solvent-contaminated soils.
dThe treatment standard for methylene chloride in wastewaters generated from pharmaceutical
plants is .44 mg/1.
14
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TABLE 4. CCW - CONSTITUENT CONCENTRATIONS IN WASTES
Waste Code
Regulated hazardous constituent
Wastewaters
Non-wastewaters
concentration
concentration
(mg/1)'
(mg/kg)'
F001-F005 spent solvents
1,1,2-T richloroethane
0.030
7.6
Benzene
0.070
3.7
"Based on Total Waste Analysis.
TABLE 5. TECHNOLOGY-BASED STANDARDS BY RCRA WASTE CODE
Waste Code
Waste descriptions and/or
treatment subcategory
Technology Coder
Wastewaters
Nonwastewaters
F005
2-Ethoxyethanol
BIODG: or INCIN
INCIN
F005
2-Nitropropane
(WETOX or CHOXD)
INCIN
fb CARBN; or INCIN
fAn explanation of the technology code can be found in Table 1 of Appendix B.
C. Dioxin Treatment Standards (§268.41)
The dioxin standards are based on incineration that achieves a 99.9999 percent destruction and
removal efficiency. These treatment standards can be found in Appendix B, Table CCWE -
Constituent Concentrations in Waste Extract (Waste codes F020-F023 and F026-F028).
IV. FIRST THIRD RULE, SECOND THIRD RULE, THIRD THIRD RULE
Subsequent to the Solvent-Dioxin Rule and the "California List" Rule, EPA published the First
Third rule of the land disposal restrictions program in the August 17, 1988 Federal Register; the
rule became effective August 8, 1988. The regulation is known as the "First Third" rule because it
contains provisions for one-third of the listed RCRA wastes, excluding those wastes covered by
the previous two rules. The three groupings published in the May 28, 1986 Federal Register were
based on toxicity and volume considerations, with the "worst" wastes being restricted first.
Treatment Standards for the Second Third and Third Third wastes were published in the Federal
Register on June 8, 1989 and June 1, 1990, respectively.
15
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EPA does not require that specific technologies be used to attain the concentration-based
treatment standards. Any waste treatment method, except impermissible dilution, may be
used to achieve the required concentrations prior to land disposal of the waste.
As oudined in the Testing and Recordkeeping section, the specific treatment standard must
appear on the LDR notification for waste codes F001-F005. This means that the appropriate
constituents, as well as the appropriate treatability group and concentration level, must be
identified on the notice.
Lists of wastes for which standards have been set are provided in 40 CFR 268.41, 268.42,
and 268.43. As noted earlier in this booklet, several of these treatment standards have been
reprinted in Appendix B for the reader's convenience. To determine all applicable treatment
standards for a specific waste, generators should examine each of these lists.
A. Testing Requirements
The testing requirements for regulated wastes are based on the goals of the technology used
in setting the treatment standards. For example, since stabilization was used to establish the
treatment standards for waste codes listed in §268.41, Table CCWE - Constituent
Concentrations in Waste Extract, the Toxicity Characteristic Leaching Procedure (TCLP)
(extract method) should be used to determine whether the treatment standard has been met.
Conversely, since incineration, a thermal destruction technology, was used to develop the
treatment standards for waste codes listed in §268.43 Table CCW - Constituent
Concentrations in Wastes, a total waste analysis should be used to determine if the treatment
standard has been attained.
In cases where waste mixtures are subject to more than one treatment standard because of the
specific constituents in the mixture, the treatment standards for all the constituents will apply.
In fact, it may be necessary to test a waste using more than one method to certify that all
applicable treatment standards have been met. If a waste mixture is subject to different
treatment standards for the same constituent, however, the more stringent treatment standard
applies.
A generator may also use his/her knowledge of the waste in determining whether or not the
treatment standard has been met. If, however, generator knowledge is used, supporting
documentation must be kept on-site in the generator's file.
B. Characteristic Wastes (§268.9)
The Third Third Scheduled Wastes Rule (55 FR22520) established treatment standards for the
characteristic waste numbers D001-D017.
Wastes which exhibit a characteristic of hazardous waste (40 CFR Part 261 Subpart C) must
be treated prior to land disposal so that they no longer exhibit that characteristic. Special
rules have been established in §268.9 regarding wastes that exhibit a characteristic.
16
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If a waste is listed under both Subpart C (Characteristics of Hazardous Wastes) and Subpart
D (Lists of Hazardous Wastes) of 40 CFR Part 261, a determination must be made concerning
the following:
(1) If the treatment standard for the waste code listed in Subpart D includes a
treatment standard for the constituent that causes the waste to exhibit the
characteristic, then the treatment standard for the listed waste (F, K, P, U
wastes) will operate in lieu of the treatment standard for the characteristic
waste code ("D" wastes).
For example, in an F006 metal-hydroxide sludge also exhibits the toxicity
characteristic for lead (D008), the treatment standard for D008 is not applicable
since the F006 treatment standard in Table CCWE includes a standard for lead.
(2) If the waste exhibits a characteristic not addressed in the treatment standard
specified in Subpart D of Part 268, the treatment standard established for the
characteristic waste code ("D" waste) and the treatment standard for the listed
waste (F, K. P. U wastes) must both be met.
For example, if an F001 spent solvent mixture is contaminated with and
exhibits the characteristics for lead (D008), treatment standards for both the
F001 and the D008 are applicable since the F001-F005 treatment standards, do
not include a standard for lead.
Wastes which are hazardous by characteristics only (i.e. there is no applicable waste code
listed in Part 261 Subpart D) are subject to different LDR requirements:
(1) If a characteristic waste does not meet the Treatment Standards and is being
shipped off-site, the notification requirements of §268.7(a)(l) apply, as they do
with all other wastes.
(2) If the waste is treated so that it no longer exhibits that characteristic and, thus,
is no longer hazardous, the waste may be shipped to a subtitle D facility (non-
hazardous land disposal facility). The generator or the treatment facility need
not send a §268.7 notification to such a facility. However, a notification
containing the following information must be sent to the EPA Regional
Administrator:
(i) the name and address of the Subtitle D facility receiving the waste
shipment;
(ii) a description of the waste as generated (including EPA waste
number(s) and treatability group(s)); and
(iii) the treatment standards applicable to the waste at the time of
generation.
17
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A certification statement which utilizes the language in §268.7(b)(5)(i), signed
by an authorized representative must accompany these notifications.
Also, when the hazardous characteristic is removed prior to disposal, or when the waste is
excluded from the definition of hazardous or solid waste under 40 CFR 261.2 - 261.6, the
requirements of 40 CFR 268.7(a) still apply. For example, if a characteristic waste is not
prohibited because it is discharged from a wastewater treatment system pursuant to an
NPDES permit, some record must still be kept indicating why the waste is not prohibited (i.e.,
a statement that there is no land disposal of this waste in the system should be in the
facility's operating record).
The newly identified "Toxicity Characteristic" (TC) hazardous waste codes D018-D043, have
yet to be restricted under the LDR. For such newly identified wastes, EPA will establish
treatment standards after March 29, 1991. Until such treatment standards are established,
these wastes may be disposed of without prior treatment.
Information about the newly identified wastes may be obtained by contacting the RCRA
Hotline, (800) 424-9346 or Region I's TC Hotline (617) 223-5527.
C. Alternative Treatment Standards for Lab Pack Wastes (§268.7(a))
The Third Third Rule (55 FR 22520) established alternative treatment standards for shipments
of specific lab pack wastes. A "lab pack" consists of miscellaneous laboratory waste
repackaged in larger containers. The two types of lab packs eligible for these alternative
standards are detailed in Appendix IV and V of Part 268, and are also reprinted for
convenience in Appendix C of this booklet. The technology of incineration (INCIN) has been
specified as a treatment standard for these Lab packs.
A notification pursuant to §268.7(a)(l) must be sent with each shipment. This notification
must list all EPA waste numbers for materials contained in the lab pack sent. The applicable
certification statement (§268.7(a)(7) or (8)) must also be signed and included with the
notification. All notifications and certifications must be retained for 5 years.
D. Small Quantity Generator Tolling Agreements (§268.7(a)(9))
Special requirements apply for small quantity generators (SQGs) (100-1000 kg/month)
engaged in tolling agreements pursuant to 40 CFR 262.20(e). A tolling agreement is a
contract between an SQG and a recycling facility where the type of waste and the frequency
of pick-up/shipments are specified in the agreement. All vehicles used to transport the waste
and regenerated material must also be owned by the reclaimer of the waste.
SQGs with tolling agreements must comply with the applicable notification and certification
requirements of §268.7(a) only for the initial shipment of the waste subject to the agreement.
This notification (and certification, if applicable), as well as a copy of the agreement, must be
retained on-site for at least 3 years after the termination of such an agreement.
18
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V. CALIFORNIA LIST RULE
A. Applicability
On July 8, 1987, the EPA promulgated the second phase of the LDR program which restricts
the land disposal of the California List wastes. These hazardous wastes are referred to as the
California List because the State of California developed regulations to restrict the land
disposal of hazardous wastes containing these constituents and Congress adopted these
prohibitions in the 1984 Amendments to RCRA. Since treatment standards for all waste
codes have been established subsequent to the publication of the California List, these newer
standards supercede the California List treatment standards. Therefore, only under the
following circumstances does the California List still apply:
(1) During a period of national capacity variance, the California List still applies.
(If a waste code has a national capacity variance but falls under one of the
California List prohibitions, that waste must be treated to those levels prior to
disposal.)
(2) California List prohibition levels for PCB containing liquid hazardous wastes
and liquid hazardous wastes containing Nickel or Thallium greater than
134mg/l and 130mg/l, respectively, are still applicable.
(3) Halogenated Organic Compounds (HOC)-containing waste identified by a
characteristic property that does not involve HOCs, is subject to the California
List HOC standards for incineration.
B. Regulated Materials
The California List consists of liquid hazardous wastes containing certain metals, free
cyanides, polychlorinated biphenyls (PCBs), corrosives with a pH less than or equal to 2.0,
and liquid and non-liquid hazardous wastes containing halogenated organic compounds
(HOCs) as described below:
(A) Liquid hazardous wastes, including free liquids associated with any solid or
sludge, containing free cyanides at concentrations greater than or equal to
1,000 mg/1.
(B) Liquid hazardous wastes, including free liquids associated with any solid or
sludge, containing any of the following metals (or elements) or compounds of
these metals (or elements) at concentrations greater than or equal to those
specified below:
Arsenic (as As)
Cadmium (as Cd)
500 mg/1
100 mg/1
500 mg/1
500 mg/1
20 mg/1
Chromium (as Cr VI)
Lead (as Pb)
Mercury (as Hg)
19
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Nickel (as Ni)
Selenium (as Se)
Thallium (as Tl)
134 mg/1
100 rag/1
130 mg/1
(C) Liquid hazardous waste having a pH less than or equal to 2.0.
(D) Liquid hazardous wastes containing PCBs at concentrations greater than or
equal to 50 ppm.
(E) Hazardous waste containing HOCs in total concentration greater than or equal
The rule requires that the Paint Filter Liquids Test be used to determine whether a waste is
considered to be a liquid or nonliquid. This procedure is method 9095 in EPA Publication
No. SW-846, "Test Methods for Evaluating Solid Waste."
1. Halogenated Organic Compounds (HOCs)
HOCs subject to the LDR are listed in Appendix III of Part 268. The final rule specifies that
hazardous wastes containing HOCs in total concentrations greater than or equal to 1,000 mg/1,
must be incinerated in accordance with existing RCRA regulations. Again, if the HOC waste
is also subject to the F-solvent restrictions or other listed waste treatment standards, the listed
waste treatment standard applies, not the California List standard.
2. Poly chlorinated Biphenyls (PCBs)
As of July 8, 1987, liquid hazardous wastes containing PCBs in concentrations exceeding 50
ppm must be incinerated or burned in high efficiency boilers in accordance with the technical
standards of 40 CFR 761.70. Additionally, restricted wastes with PCBs must only be stored
for up to one year providing such storage complies with §268.50
to 1,000 mg/1.
20
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APPENDIX A
NOTIFICATION AND CERTIFICATION REQUIREMENTS
Table of Contents
Notification and Certification Requirements Summary Table A-2
Certification Statements Summary A-5
Certification Statements A-6
A-l
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NOTIFICATION AND CERTIFICATION REQUIREMENT SUMMARY TABLE
NOTIFICATION CERTIFICATION
Scenario Notifies How Certifies How Certification
Whom? Often? Notification Must Include to Whom? Often Must include
• Generator manages a
restricted waste that does
not meet the treatment
standards/prohibition
levels; sends if off-site
for storage or treatment
(§268.7(a)(1))
• Generator manages a
restricted waste, determines
waste can be land disposed
without further treatment
(§268.7(a) (2))
• Generator's waste is
subject to a case-by-case
extension under §268.5,
exemption under §268.6, or
a nationwide vanance under
Subpart C (§268.7(a)(3))
Treatment
storage or
recycling facility
Treatment,
storage,
recycling, or
disposal facility
Facility
receiving
waste (MTR
unit)
With each - EPA HW number N/A
shipment - Corresponding treatment standard or
prohibition level
- Manifest number
- Waste analysis data, where available
With each - EPA HW number TSDF
shipment - Corresponding treatment standard or
prohibition level
- Manifest number
- Waste analysis data, where available
With each - EPA HW number
shipment - Corresponding treatment standard and
all applicable prohibitions
- Manifest number
- Waste analysis data, where available
- The date the waste is subject to the
prohibitions
- Statement that waste is not prohibited
from land disposal
N/A
N/A
With each
shipment
Statement that waste
meets applicable
treatment standards/
prohibition levels.
See "A".
• Small quantity generator Recycling
(100-1000 kg/month) subject facility
to tolling agreement pursuant
to §262.20(e)
With initial - EPA HW number Recycling With initial
shipment - Corresponding treatment standard or facility shipment
prohibition level (if waste
- Manifest number meets the
- Waste analysis data, where available treatment
standard)
Statement that
meets applicable
treatment standards/
prohibition levels.
See "A".
A-2
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Notification Certification
Scenario Notifies How Certifies How Certification
Whom? Often? Notification Must Include to Whom? Often Must Include
• Generator sending
lab-pack containing only
wastes listed in §268
Appendix IV or V
• TSDs sending restricted
waste off-site for additional
treatment or storage
(§268.7(b)(6))
• Treatment facilities
sending restricted wastes
off-site to land disposal
facilities (LDFs)
(§268.7(b)(4))
Treatment or
storage facility
With each
shipment
- Ail EPA HW numbers Treatment
- Five letter technology code: INCIN or storage
- Manifest number facility
- Waste analysis data, where available
With each
shipment
Must meet same
notice and
certification
requirements
applicable to
generators
LDFs
With each
shipment
EPA HW number
Corresponding Treatment Standard
Manifest number
Waste analysis data, where available
LDFs
With each
shipment
For Appendix IV
lab-packs, see "D".
For Appendix V
lab-packs, see "E".
For wastes with
treatment standards
expressed as
concentrations, see "B".
For wastes with
treatment standards
expressed as
technologies, see "C".
For wastes which have
been deemed in
compliance with the
treatment standards
based on the analytical
detection limit
alternative specified in
§268.43(c), also include
np»
A-3
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Notification Certification
Scenario Notifies How Certifies How Certification
Whom? Often? Notification Must include to Whom? Often Must Include
• Generator or TSDF
sending characteristic waste
which has been rendered
non-hazardous to a
Subtitle D land disposal
facility (§268.9)
Regional With each - Name and address of Subtitle D
Administrator shipment facility
- Description of waste, as generated
- Treatment standard applicable to
waste at time of generation
Regional With each
Administrator shipment
Statement that waste
meets applicable
treatment standards/
prohibition levels.
See "B".
A-4
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CERTIFICATION STATEMENTS SUMMARY
Certification
Statement
Initiator
Recipient
Description
40CFR
B
Generator
Treatment Facility
Treatment or
Storage Facility
Generator
Generator
Treatment Facility
Treatment, Storage
or Disposal Facility
Land Disposal
Facility
Land Disposal
Facility
Treatment or
Storage Facility
Treatment or
Storage Facility
Land Disposal
Facility
Wastes Meeting § 268.7(a)(2)(ii)
Treatment Standards
Wastes whose § 268.7(b)(5)(i)
Treatment Standards
are listed as
Concentrations
§ 268.41
Wastes whose
Treatment Standards
are listed as
Technologies (§ 268.42)
Appendix IV
Lab Pack Wastes
(organometallics)
Appendix V
Lab Pack Wastes
(organics)
Incinerated wastes
(organic detection
limit)
§ 268.7(b)(2)(ii)
§ 268.7(a)(7)
§ 268.7(a)(8)
§ 268.7(b) (5)(iii)
A-5
-------
CERTIFICATION STATEMENTS
A. I certify under penalty of law that I personally have examined and am familiar with the
waste through analysis and testing or through knowledge of the waste to support this
certification that the waste complies with the treatment standards specified in 40 CFR Part
268 Subpart D and all applicable prohibitions set forth in 40 CFR 268.32 or RCRA
Section 3004(d). I believe that the information I submitted is true, accurate and complete.
I am aware that there are significant penalties for submitting a false certification,
including the possibility of a fine and imprisonment (§268.7(a)(2)(ii))
B. I certify under penalty of law that I have personally examined and am familiar with the
treatment technology and operation of the treatment process used to support this
certification and that, based on my inquiry of those individuals immediately responsible
for obtaining this information. I believe that the treatment process has been operated and
maintained properly so as to comply with the performance levels specified in 40 CFR Part
268, Subpart D, and all applicable prohibitions set forth in 40 CFR 268.32 or RCRA
section 3004(d) without impermissible dilution of the prohibited waste. I am aware that
there are significant penalties for submitting a false certification, including the possibility
of fine and imprisonment. (§268.7(b)(5)(i))
C. I certify under penalty of law that the waste has been treated in accordance with the
requirements of 40 CFR 268.42. I am aware that there are significant penalties for
submitting a false certification, including the possibility of fine and imprisonment.
(§268.7 (b)(5)(H))
D. I certify under penalty of law that I personally have examined and am familiar with the
waste and that the lab pack contains only the wastes specified in Appendix IV to Part 268
or solid wastes not subject to regulation under 40 CFR Part 261. I am aware that there
are significant penalties for submitting a false certification, including the possibility of
fine or imprisonment. (§268.7(a)(7))
E. I certify under penalty of law that I personally have examined and am familiar with the
waste through analysis and testing or through knowledge of the waste and that the lab
pack contains only organic waste specified in Appendix V to Part 268 or solid wastes not
subject to regulation under 40 CFR Part 261. I am aware that there are significant
penalties for submitting a false certification, including the possibility of fine or
imprisonment. (§268.7(a)(8))
F. I certify under penalty of law that I have personally examined and am familiar with the
treatment technology and operation of the treatment process used to support this
certification and that, based on my inquiry of those individuals immediately responsible
for obtaining this information, I believe that the nonwastewater organic constituents have
been treated by incineration in units operated in accordance with 40 CFR Part 264,
subpart O or Part 265, subpart O, or by combustion in fuel substitution units operating in
accordance with applicable technical requirements, and I have been unable to detect the
nonwastewater organic constituents despite having used best good faith efforts to analyze
for such constituents. I am aware that there are significant penalties for submitting a false
certification, including the possibility of fine and imprisonment. (§268.7(b)(5)(iii))
A-6
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APPENDIX B
TREATMENT STANDARDS
Table of Contents
Table CCWE - Constituent Concentrations in
Waste Extract
Table CCWE - Constituent Concentrations for
Waste Extracts
Table 1. - Technology Codes and Description of
Technology-Based Standards
Table 2. - Technology-Based Standards by
RCRA Waste Code
Table 3. - Technology-Based Standards for Specific
Radioactive Hazardous Mixed Waste
Table CCW - Constituent Concentrations in Wastes
40 CFR
§268.41
§268.41
§268.42
§268.42
§268.42
§268.43
55 FR
22690
22692
22693
22694
22700
22701
B-l
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22690
Federal Register / Vol. 55, No. 106 / Friday, June 1, 1990 / Rules and Regulations
Table COME.— Constituent Concfntraticns in Waste Extract
Waste coda
Sea also
Regulated hazardous constituent
CAS number
for regulated
hazardous
constituent
Wastewaters
concentra-
tion (mg/l)
Non-
wastewaters
concentra-
tion (mg/l)
D004
D005
D006
D007
D008
D009 (Low Mercury Subcategory-
less than 260 (Tig/kg Mercury).
001 0
001 1
F0O1-F0C5 spent solvents
F006..
F007..
F008
Table CCW in 268.43
Table CCW in 268 43
Table CCW in 268.43
Table CCW In 268.43
Table CCW in 268.43
Table 2 in 268.42 and Table CCW in
268.43.
Table CCW in 268.43
Table CCW in 268.43
Table 2 in 268.42 and Table CCW in
268.43.
Table CCW in 268.43..
Table CCW in 268.43..
F009..
F011.
F012..
F019
F020-F023 and F026-F026 dtoxin
containing wastes.*.
Tabte CCW in 263.43..
Table CCW in 268.43..
Table CCW In 268.43..
Table CCW in 268.43..
Table CCW in 268.43..
Arsenic
Barium
Cadmium
Chromium (Total)..
Lead
Mercury
Selenium..
Silver
Acetcne...
n-Butyl alcohol
Carbon disulfide
Carbon tetrachlonde
Chlorobenzene
Cresols (3nd cresylic acid)
Cydohexanone
1,2-Dichlorobenzene
Ethyl acetate
EthyttwrowM)
Ethyl ether
Isobutanol
Methanol
Methylene chlonde
Methyl ethyl ketone..—
Methyl isobutyl ketone
Nitrobenzene
Pyridine
Tetrachloroethylene
Toluene
1.1.1-Tnchloroe thane
1.1.2-TrichlOfO-1,2,2-Tetrifluorethane...
Trichloroethytene
TnchloroHuoromethane
Xylene
Cadmium
Chromium (Total)
Lead
Nickel
Silver
Cadmium
Chromium (Total)
Lead
Nickel
Silver
Cadmium
Chromium (Total)
Lead -
Nickel
Silver
Cadmium
Chromium (Total)
Lead
Nickel
Silver
Cadmium
Chromium (Total)
lead
Nickel
Silver
Cadmium
Chromium (Total)
Lead
Nickel
Silver
Chromium (Total)
HxCDD-AII Hex«chlorodlb«nzo-p-diox-
HxCDF-All Hexachlorodfcenzofurans....
PeCDD-AII Pentachlorodibenzo-p-
dioxins.
PeCDF-AII PenUchlorodibenzofurans...
TCDD-AII T etrachkxodlbenzo-p-diox-
ins.
TCDF-AII Tetrachlorodlbenzofurans
2.4.5-Trtchloropheno l
2.4.6-Trichloropheno l
7440-38-2
7440-39-3
7440-43-9
7440-47-32
7439-92-1
7439-97-6
7762-49-2
7440-22-4
67-64-1
71-36-3
75-15-0
56-23-5
108-90-7
108-94-1
95-50-1
141-78-6
100-41-4
60-29-7
76-83-1
67-56-1
75-9-2
78-93-3
108-10-1
98-95-3
110-86-1
127-18-4
108-88-3
71-55-6
76-13-1
79-01-a
75-69-4
7440-43-9
7440-47-32
7439-92-1
7440-02-0
7440-22-4
7440-43-9
7440-47-32
7439-92-1
7440-02-0
7440-22-4
7440-43-9
7440-47-32
7439-92-1
7440-02-0
7440-22-4
7440-43-9
7440-47-32
7439-92-1
7440-02-0
7440-22-4
7440-43-9
7440-47-32
7439-92-1
7440-02-0
7440-22-4
7440-43-9
7440-47-32
7439-92-1
7440-02-0
7440-22-4
7440-47-32
95-95-4
88-06-2
NA
NA
NA
NA
NA
NA
NA
NA
0.05
5.0
1.05
0.05
0.15
2.82
0.125
0.65
0.05
0.05
0.05
5.0
0.25
0.20
0.05
0.05
0.66
1.12
0.079
1.12
1.05
1.05
0.062
0.05
0.05
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
<1 Ppb
<1 ppb
<1 PPb
<1 PPb
<1 PPb
<1 PPb
<0.05 ppm
<0.05 ppm
5.0#
100
1.0
5.0
5.0
0.20
5.7
5.0
0.59
-------
Federal Register / Vol. 55, No. 106 / Friday, June 1. 1990 j Rules end Regulations
22691
Table CCWE.—Constituent Concentrations in Waste Extract—Continued
Waste code
See also
Regulated hazardous constituent
CAS number
tor repuiatsd
hazardous
constituent
Wastewaters
concentra-
tion (mg/l)
N
-------
22692
Federal Register / Vol. 55, No. 106 / Friday, June 1, 1990 / Rules and Regulations
Table CCWE.—Constituent Concentrations in Waste Extract—Continued
'¦Vasts coaa
See also
Regulated hazardous constituent
CAS number
for regulated
hazardous
constituent
Wastewaters
concentra-
tion (mg/l)
Non-
wastewaters
concentra-
tion (rng/f)
K11S _ _
T«r>te CCW
7440-02-0
NA
0.32
•
?—These treatment standards have Been based on EP isacna'.e analysis but mis does not preclude the use of TCLP analysis.
*—Thp;»a waste codes are not suDcategorrzed mto wastewaters and nonwastewaters.
NA—,\or AppicaDte.
Table CCWE.—Constituent Concentrations for Waste Extracts
Waste codo
See also
Commercial chemical name
Regulated hazardous
constituent
CAS number
tor regulated
hazardous
constituent
Wastewaters
concentration
(mg/1)
P010
P011
po;2
F013
P036
P038
PC65 (Low Mercury Subcate-
gory—'«r:"5 than 260 mg/'kq
Mercur>-res»dues from
RMERO.
P065 (Law Me»cury Subcate-
gory—less than 260 mg/kg
Mercury-tnoinerator resi-
dues (and are not residue#
from RMERC;).
P073
P074
P092 (Low Mercury Subcate-
gory—less than 260 mg/kg
Mercury residues from
RMERC).
P092 (Low Mercury Subcate-
gory—less than 260 mg/Kg
Mercury-incinerator resi-
dues (and are not residues
from RMERC)).
P099
P103
P104
P110
P114
U032
U051
U136
U144 —...
U145
U146
U151 (Low Mercury Subcate-
gory—less than 260 mg/kg
Mercury—residues from
RMERC).
0151 (Low Mercury Subcate-
gory—lass than 280 mg/Kg
Mercury—that are not resi-
dues from RMERC).
U204
U205
Table CCW in 268.43
Table CCW in 268.43
Table CCW in 268.43
Tabie CCW in 268.43
Table CCW in 268.43
i Table CCW in 268.43
J Table 2 in 268.42 and Table
CCW in 268.43.
Table 2 in 268.42 and Table
CCW in 268 43.
Table CCW in 268.43....
Table CCW in 268.43
Table 2 in 268.42 and Table
CCW in 268 43.
Table 2 In 268.42 and Table
CCW in 268.43.
Table CCW in 268.43
Table CCW in 268.43
Table CCW In 268.43
Tabie CCW in 268.43
Table CCW in 268.43
Table CCW in 266.43
Table CCW in 268.43
Table CCW in 268.43__
Table CCW in 268.43
Table CCW in 268.43
Table CCW in 268 43
Table CCW in 268.43 and In
Table 2 m 268.42.
Table CCW in 268.43 and
Table 2 in 268.42.
Table CCW in 268.43
Table CCW in 268.43
Arsenic acid
Arsenic pentonde
Arsenic tnoxide
Banum cyanide
Oichlorophenylarsine..
Dietnylarsme
Mercury fulminate
Mercury fulminate..
Nickel caibonyl
Nickel cyanide
Phenyl mercury acetate..
Phenyl mercury acetate..
Potassium siher cyanide -
Selenourea
Silver cyanide.
Tetraethyl lead
Thallium utentto
Calcium chromate
Creosote
Cacodylic acid
Lead acetate
Lead phosphate
Lead subaeetate
Mercury
Mercury..
Selenium dioxide.
Selenium sulfide..
Arsenic.
Arsenic.
Arsenic.
Barium..
Arsenic.
Arsenic.
Mercury
Mercury
Nickel....
Nickel...
Mercury
Mercury
Silver
Selenium
QIim.
anrw,.
Lead
Selenium
Chromium (Total)
Lead
Arsenic
Lead
Lead....-
Lead
Mercury
Mercury ..._
Selenium
Selenium
7440-36-2
7440-38-2
7440-38-2
7440-39-3
7440-38-2
7440-38-2
7439-97-6
7439-97-6
7440-02-0
7440-02-0
7439-97-6
7439-97-6
7440-22-4
7782-49-2
7440-22-4
7439-92-1
7782-49-2
7440-47-32
7439-92-1
7440-38-2
7439-92-1
7439-92-1
7439-92-1
7439-97-6
7439-97-6
7782-49-2
7782-49-2
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
—These treatment standards have been based on EP Leachate analysis but tins does not preclude the i
'—These waste codes are not subcategoreed into wastewaters and nonwastewaters.
NA—Not Applicable.
i ol TCLP analysis.
-------
Federal Register / Vot. 55. No. 106 / Friday. June 1. 1990 / Rules and Regulations
22693
Table 1.—Technology Codes and Description of Technology-Based Standards
Description of techncxjg. -based standard
Venting ot compressed gases into an absorbing or reacting media (i.e., solid or Squid)—venting can be accomplished through physical release utilizing
values/piping: physical penetration of the container; and/or penetration through detonation.
Amalgamation of liquid, elemental mercury contaminated with radioactive materials utilizing inorganic reagents such as copper, zinc, nickel, gold, and
suirur that result in a rxxiiiquid, semi-solid amalgam and thereby reducing potential emissions of elemental mercury vapors to the air.
Biodegradation of organics or non-metallic inorganics (i.e., degradable inorganics that contain the elements of phosphorus, nitrogen, and sulfur) in units
operated under either aerobic or anaerobic conditions sucti that a surrogate compound or indicator parameter has been substantially reduced in
concentration in the residuals (e.g.. Total Organic Carbon can often be used as an indicator parameter for the biodegrsdatton of many organic
constituents that cannot be directly analyzed in wastewater residues).
Carbon adsorption (granulated or powdered) ot non-metallic inorganics, organo-metalllcs, and/or organic constituents, operated such that a surrogate
compound or indicator parameter has not undergone breakthrough (e.g.. Total Organic Carbon can often be used as an indicator para-meier for the
adsorption of many organic constituents that cannot be directly analyzed In wastewater residues). Breakthrough occurs when the carbon has
become saturated with the constituent (or indicator parameter) and substantial change in adsorption rate associated with that constituent occurs.
Chemical or electrolytic oxidation utilizing the following oxidation reagents (or waste reagents) or combinations or reagents: (1) Hypochlorite (e.g.
bleach); (2) chlorine; (3) chlorine dioxide; (4) ozone or UV (ultraviolet light) assisted ozone; (S) peroxides; (6) persuHates; (7) perchtorates; (8)
permangantes; and/or (9) other oxidizing reagents of equivalent efficiency, performed in units operated such that a surrogate compound or indicator
parameter has been substantially reduced in concentration in the residuals (e.g.. Total Organic Carbon can often be used as an indicator parameter
for the ondation of many organic constituents that cannot be directly analyzed in wastewater residues). Chemical oxidation specifically includes what
is commonly referred to as alkaline chlorination.
Chemical reduction utilizing the following reducing reagents (or waste reagents) or combinations of reagents: (1) Sulfur dioxide; (2) sodium, potassium,
or alkali salts of sulfites, bisulfites. metabisuifitea, and polyethylene glycols (e.g.. NaPEG and KPEG); (3) sodium hydrosulftde; (4) ferrous salts: and/
or (S) other reducing reagents of equivalent efficiency, performed In units operated such that a surrogate compound or indicator parameter has been
substantially reduced in concentration in the residuals (e.g.. Total Organic Halogens can often be used as an indicator parameter tor the reduction of
many halogenated organic constituents that cannot be dkectty analyzed In wastewater residues). Chemical reduction Is commonly used for the
reduction of hexavalent chromium to the trivalent state.
Deactivation to remove the hazardous characteristics of a waste due to Ms Ignitability, corrosMty, and/or reactivity.
Fuel substitution in units operated In accordance with applicable technical operating requirements.
Vitrification of high level mixed radioactive wastes In units in compVanoe with all applicable radioactive protection requirements under control of the
Nuclear Regulatory Commissioa
Incineration ol wastes containing organic* and mercury in units operated In accordance with the technical operating requirements of 40 CFR pert 264,
subpart O and 40 CFR part 265, subpart 0. All wasteiwatar and nonwastewater residues derived from this process must than comply with the
corresponding treatment standards per waste code with consideration of any applicable subcategories (e.g* High or Low Mercury Subcategories).
Incineration in units operated in accordance with the technical operating requirements ol 40 CFR part 264, subpart 0 and 40 CFR part 265, subpart O.
Liquid-liquid extraction (often referred to as solvent extraction) of organics Irom liquid wastes into an immiscible solvent for which the hazardous
constituents have a greater solvent affinity, resulting in an extract high in organics that must undergo either Incineration, reuse as a fuel, or other
recovery/reuse and a raffinate (extracted liquid waste) proportionately low in organics that must undergo further treatment aa specified in the
standard.
Macroencapsulation with surface coating materials such as polymeric organics (e.g. resins and plastics) or wrtth a Jacket of Inert inorganic materials to
substantially reduce surface exposure to potential leaching media. Macroencapsulation specifically does not include any material that would be
classified as a tank or container according to 40 CFR 280.10.
Neutralization with the following reagents waste reagents) or combinations of reagents: (t) Adds; (2) bases; or (3) water (inducing wastewaters)
resulting in s pH greater than 2 but less than 12.5 as measured In the aqueous residuals
No land disposal based on recycling.
Chemical precipitation ol metals and other inorganics as Inaotuble precipitates of oxides, hydroxidee, carbonates, sulfides, sulfates, chlorides, ftourides,
or phosphates. The foUowing reagents (or waste reagents) are typically uaad alone or In combination: (1) Lima (I.e, containing oxidea and/or
hydroxides of calcium and/or magnesium; (2) caustic |Le., sodkjm and/or potassium hydroxides; (3) soda ash (i.e., sodium carbonate); (4) aodkjm
sulfide; (5) ferric sulfate or ferric chloride; (6) alum; or (7) sodium sulfate. Additional floculabng. coagulation, or similar reagents/processes that
enhance sludge dewatering characteristics are not precluded from use.
Thermal recovery of Beryllium.
Recovery/reuse of compressed gases Including techniques such ae reprocessing of the gases tor reuse/resale; Wtaring/adsofption of ffnpurtties;
remixing for direct reuse of resale; and use of the gaa aa a fuel source.
Recovery ol acids or basse utilizing one or more ot the following recovery technologies: (1) Distillation (I.e., thermal concentration); (2) ion exchange;
(3) resin or soHd adsorption; (4) reverse osmosis; and/or (5) Incineration tor the recovery of edd—Note: this does not preclude the uee of other
physical phase separation or concentration techniques such as decantation. filtration (inducing ultrafiltration), and oentrNugalion, when used la
conjunction with the above listed recovery technologies.
Thermal recovery of lead In secondary lead smelters.
Retorting or roasting in a thermal processing unit capable of volatMzing mercury and subsequently condensing the volatilized mercury tor recovery. The
retorting or roasting unit (or facility) must be subject to one or more of the following: (a) A National Emissions Standard for Hazardous Air Pollutants
(NESHAP) for mercury; (b) a Beat Available Control Technology (BACT) or a Lowest Achievable Emission Rate- (L^pR) standard for mercury
imposed pursuant to a Prevention of Significant Deterioration (PSD) permit; or (c) a state permit that establishes emission limitation* (within meaning
of Section 302 of the Clean Air Act) for mercury. All waatewatsr and nonwastewater residues derived from Ms process must then comply with the
corresponding treatment standards par waste code with uonaideraUon of any applicable subcategories (e.g, High or Low Mercury Subcategories).
Recovery of metals or Inorganics utilizing one or more of the following dkect physical/removal technologies: (1) Ion exchange; (2) resin or solid (l.e.,
zeolites) adsorption; (3) reverse osmosis; (4) chelation/solvent extraction; (5) freeze crystaltzation; (6) ultrafiltration; and/or 6 simple precipitation (Le.,
ayatallzation)—Note: thia doaa not preclude the uae of other physical phase separation or concentration techniquee such as decantation, filtration
(including ultrafiltration), and centrtfugatton, whan used in conjunction with the above listed recovery technologlee.
Recovery of organics utilizing one or more of the following technotoglee: (1) Distillation; (2) thin flm evaporation; (3) aMtai atilpplng. (4) carbon
adsorption; (5) critical IMd extraction; (6) liquid-liquid extraction; (7) precipitation/crystallization (Including freeze crystallization*; or (8) chemical phase
separation techniques (j.e„ addition of edds. bases, demutsiflsrs, or similar chemicals); Note: This doee not preclude the use of other physical phese
separation techniquea such as. decantation. filtration (including ultrafiltration), and centnfugatton, when used In conjunction with the -above listed
recovery tachnologiee.
Thermal recovery of metals or inorganics from nonwaatewatars In units defined In 40 CFR 260.10, paragraphs (1). (6). (7), (11), and (12), under the
definition of "industrial furnaces'*.
-------
22634
Federal Register / Vol. 55, No. 1G6 / Friday, June 1, 1990 / Rules and Regulations
Table 1.—Technology Codes and Description of Technology-Based Standards—Continued
'! ethn. ilo^y
'.O.hJ
Descnption of technology-based standard
R^INC
STABI
WCTOX
Resroelting in to.- the purcose oi recovery of zinc high temperatiife metal recovery umts.
StaDilization with the following reagents (or waste reagents) or combinations of reagents: (1) Portland cement: or (2) lime/pozzolans (e.g., fly ash and
cement Wn dust)—this does not preclude the addition ot reagents (efl.. :ron salts, silicates, and clays) designed to enhance the set/cure time and/
or compressive strength, or to overall reduce the teachability of the metal or inorganic.
Steam stripping ol organics from liquid wastes utilizing direct application of steam to the wastes operated such that liquid and vapor flow rates, as well
as. temperature and pressure ranges have been optimized, monitored, and maintained. These ooerating parameters are dependent upon the design
parameters o< the umt such as, the number ot separation stagos and the internal column design. Thus, resulting in a condensed extract high in
organics that mor.t undergo either incineration, reuse as a fuel, or other recovery/reuse and an extracted wastewater that must undergo further
tieatment as specified m me standard.
Wei air oxidation performed in units operated such that a surrogate compound or investor parameter has been substantially reduced In concentration
in the residuals (e.g.. Total Organic Carbon can otten be used as an indicator parameter for the oxidation of many organic constituents that cannot
bo diroctty analyzed in wastewater residues).
Controlled reaction with water tor highly reactive inorganic or organic chemicals with precautionary controls for protection of workers from potential
violent reactions as w«i as precautionary controls tor potential emissions of toxic/ignitaote levels of gases released during the reaction.
note 1> .Vlwn a combination of these technologies (i.e., a treatment train) is specified as a single treatment standard, the order of application is specified in
§ MB ^2 Tanie 2 dv indicating tfw five letter technology code that must be applied first, men the designation "fb." (an aooreviation for "followed by"), then the five
tetter tocfwKjlogy code tor tho tacnnoicxjy that must be applied next, and so on.
More 2: When more than one technology lor treatment tram) are specified as alternative treatment standards, the five letter technology codes (or the treatment
trams) are separated by a semicolon I;) with the last technology preceded by the word "OR". This indicates that arty one of these BOAT technologies or treatment
trains can do used tor compliance with the standard.
Fable 2.—Technology-Based Standards by RCRA Waste Code
See also
Waste descriptions and/or treatment subcategory
CAS No. for
regulated
hazardous
constituents
Technology code
Wastewaters
Nonwastewaters
Table CCWE in 268.41
and Table CCW in
268.43.
Table CCWE in 268.41
and Table CCW in
268.43.
Table CCW in 260 43
Taote CCW in 268.43....
Table CCW in 268 43 ...
Table CCW in 268.43..._
Table CCW in 268.43.-_
Table CCW in 268 43
Table CCWE in 268.41
and Taoe CCW in
268.43.
Ignrtable Liquids based on 261.21(a)(1)—
Wastewaters.
Igrntafcle Liquids based on 261.21(a)(1)—Low
TOC ignitable Liquids Subcategory—Less than
10% total organic carbon.
Ignitable Liquids based on 261.21(a)(1)—High
TOC Ignitable Liquids Subcategory—Greater
than or equal to 10% total organic carbon.
Ignitable compressed gases based on
261 21(a)(3)
Ignitable reacttves 261.21(a)(2)—
Oxidizers based on 261 21 (a)(4) — —
Acid subcategory based on 261.22(a)(1) ..
Alkaline subcategory based on 261.22(a)(1)
Other corrosives based on 261.22(a)(2)
Reactive sulfides based on 261.23(a)(5)
Explosives based on 261.23(a) (6), (7), and (8)—
Water reacttves based on 261.23(a) (2), (3). and
(4).
Other reactives based on 261.23(a)(1)
Cadmium containing batteries ......
Lead acid batteries (Note: This standard only
applies to lead acid battenes that are identified
as RCRA hazardous wastes and that are not
excluded elsewhere from regulation under the
land disposal restrictions ot 40 CFR 268 or
exempted under other EPA regulations (see 40
CFR 266.30).).
Mercury: (High Mercury Subcategory—greater
than or equal to 260 mg/kg total Mercury-
contains mercury and organics (and are not
incinerator residues)).
Mercury: (High Mercury Subcategory—greater
than or equal to 260 mg/kg total Mercury-
inorganics (including incinerator residues and
residues from RMERC)).
Endnn
Lindane
Methoxychior
Toxaphene
2.4-0
2.4.5-TP
2-Nitropropane...
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
7440-43-9
7439-92-1
7439-97-6
7439-97-6
72-20-8
56-69-9
72-43-6
8001-35-1
94-75-7
93-72-1
79-46-9
DEACT
NA
NA
NA
NA
DEACT
DEACT
DEACT
DEACT
DEACT
DEACT
NA
DEACT
NA
NA
NA
NA
BIOOG; or INCJN
CARBN; or INON
WETOX; or INCtN
BIOOG: or INCIN
CHOXD; BIODG: or INON
CHOXD: or INCIN
(WETOX or CHOXD) fb CARBN;
or INCIN
NA.
DEACT.
FSUBS; RORGS; or
INCIN.
DEACT* *.
DEACT.
DEACT.
DEACT.
DEACT.
DEACT.
DEACT.
DEACT.
OEACT.
DEACT.
RTHRM.
RLEAD.
IMERC; or RMERC.
RMERC.
NA.
NA.
NA.
NA.
NA.
NA.
INCIN.
-------
Federal Register / Vol. 55, No. 106 / Friday, June 1, 1990 / Rules and Regulations
22695
Table 2 —Technology-Based Standards by RCRA Waste Code—Continued
See also
Waste descriptions and 'or treatment subcategory
CAS No. lor
hazardous
constituent!
Technology code
Wastewaters
Nonwastewaters
Table CCWE in 268.41
and Table CCW in
268.43.
Table CCWE in 268.41
and Table CCW in
268.43.
2-Ethoxyethano!..
Table CCW in 268.43..
Table CCWE in 368.41
and Table CCW in
266.43.
Table CCWE in 268.41
and Table CCW in
288.43.
Distillation bottoms (rorr the production cl nitro-
benzene by the nitration of benzene
Stripping still tails from the production of methyl
ethyl pyridines.
Centrifuge and distillation residues trom toluene
diisocyanate production.
Rite' cake trom the filtration of cfcetnytphosphoro-
dithioc acid in the production of pnorate.
Wastewater treatment sludges from the manufac-
tunng and processing of explosives.
Spent carbon trom the treatment of wastewater
containing explosives.
Pink/red water trom TNT operations
Emission control dust/sludge from the primary
production ol steel in electric furnaces (High
Zinc Subcategory—greater than or equal to
15% totai Zinc).
Emission control dust/sludge from secondary
lead smeltog: Non-Calcium Sulfate Subcatego-
ry
Wastewater treatment sludge from the mercury
cell process in chionne production: (High Mer-
cury Subcategory-greater than or equal to 260
mg/kg total mercury).
Condensed liquid light ends trom the purification
of toluenediamine in tne production of toluene-
diamine vis hydrogenation of dinitrotoluene.
Vianals from the purification of toluenediame in
tne production of toluenediamine via hydrogen-
ebon of dinitrotoluene.
Heavy ends from the purification of toluenediame
In the p'oduction of toluenediamine via hydro-
gens tion of dinitrotoluene.
Organic condensate from the solvent recovery
column in the production of toluene diisocyan-
ate via phosoenation of toluenedianiine.
Warfarin (>0.3%)
t-Aoetyl-2-thiourea
Acrolein
AIM alcohol
Aluminum phosphide
5-Aminoetny! 3-isoxazoicl
4-Aminopyridine
Ammonium picrats
Tmophenol (Benzene thiol)..
Beryllium dust
Bis(chloromethyliether.
Bromoecetone.
Bnjcine
Table CCW in 268.43..
Carbon disulfide
CMoroacetaldehyde.
Mo-Chlorophenyf) thiourea.
3-Chloropropionitrile
Berwyl chloride
110-80-5
NA
NA
NA
NA
IMA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
81-81-2
591-08-2
107-02-8
107-18-6
20859-73-8
2763-06-4
504-24-5
131-74-8
108-98-5
7440-41-7
542-88-1
596-31-2
357-57-3
75-15-0
107-20-0
5344-82-1
542-76-7
100-44-7
BIOOG: or INCIN
INCIN
UEXT lb SSTRP fb CARBN; or
INCIN
INCIN
CARBN; or INCIN
CARBN: or INCIN
DEACT
DEACT
DEACT
NA
NA
NA
CARBN; or INCIN
CARBN: or INCIN
CARBN; or INCIN
CARBN; or INCIN
(WETOX or CHOXD) lb CARBN
or INCIN
(WETOX or CHOXD) 1b CARBN
or INCIN
(WETOX or CHOXD) fb CARBN
•or INCIN
(WETOX or CHOXD) lb CARBN
or INCIN
CHOXD; CHRED; or INCIN
(WETOX or
or INCIN
(WETOX or
or INCIN
CHOXD;
BIODG; or
(WETOX or
or INCIN
NA
(WETOX or
or INCIN
(WETOX or
or INCIN
(WETOX or
or INCIN
NA
(WETOX or
or INCIN
(WETOX or
or INCIN
(WETOX or
or INCIN
(WETOX or
or INCIN
CHOXD) lb CARBN,
CHOXD) lb CARBN;
CARBN;
lb CARBN;
CHRED;
INCIN
CHOXD)
CHOXD)
CHOXD)
CHOXD)
CHOXD)
CHOXD)
CHOXD)
CHOXD)
fb CARBN
to CARBN
fb CARBN
lb CARBN;
fb CARBN;
fb CARBN;
lb CARBN;
INCIN.
INCIN.
INCIN.
INCIN.
FSUBS; or INCIN.
FSUBS; or INCIN.
DEACT.
DEACT.
DEACT.
NLDBR.
RLEAD.
RMERC.
FSUBS; or INCIN.
FSUBS; or INCIN.
FSUBS; or INCIN.
FSUBS: or INCIN.
FSUBS: or INCtN.
INCIN.
FSUBS; or INCIN.
FSUBS; or INCtN.
CHOXD; CHRED; or
INCIN.
INCIN.
INCtN.
FSUBS; CHOXD;
CHRED; or INCIN.
INCIN.
RMETU or RTHRM.
INCIN.
INCIN.
INCIN.
INCtN.
INCIN.
INCIN.
INCIN.
INCIN.
-------
22696
Federal Register / Vol. 55, No. 106 / Friday, June 1, 1390 / Rules and Regulations
Table 2.—Technology-Based Standards by RCRA Waste Code—Continued
Waste
coae
See als>o
Waste descriptions and/or treatment subcategory
CAS No. (or
regulated
hazardous
constituents
Technology code
Wastewaters
Nonwastewaters
P 031
P023
P034
P040
P041
P042
P043
P044
P045
Table CCW in 268.43..
Table CCW in 268.43..
Cyanogen
Cyanogen chlonde
2-Cyclobexyl-4,6-dinitrophenol..
0.0-Diethyl O-pyrezinyl phosphorothioate.
Diethyl-p-nitrophenyl phosphate
Epinephrine
Table CCWE in 268.41
and Table CCW in
288.43.
Table CCWE in 268.41
and Table CCW in
266.43.
Diisopropyltluorophosphate (DFP)..
Dirrethoate
Thiofanox
alpna. alpha-Dimcthylprienemylamine..
4,6-Dinitro-o-cresol salts
2.4-Dithiobiuret
A2indine..
Fluonne
Fluoroacetamide..
Fluoroacetic acid, sodium salt..
Hexaethyltetraphosphate....
Isocyanic acid, ethyl eater..
Mercury fulminate: (High Mercury Subcategory—
greater than or equal to 260 mg/kg total Mer-
cury—either incinerator residues or residues
from RMERC).
Mercury fulminate: (All nonwastewaters that are
not incinerator residues from RMERC; regard-
less of Mercury Content).
Methomyl
2-Methylazihdine..
Methyl hydrazine..
Metnyllactonitnle..
Aldicarb
1 -N»phthyl-2-thiourea..
Nicotine and salts..
Nitric oxide
Nitrogen dioxide..
Nitroglycerin
N-Nitrosodimethylamine
N-Nitrosomethyiwinylamine..
Octamethylpyrophosphoramide..
Osmium ietroxide
| Endomail
Table CCWE in 268.41
and Table CCW in
268.43.
Table CCWE in 268.41
and Table CCW in
268.43.
Phenyl mercury acetate: (High Mercury Subcate-
gory—greater than or equal to 260 mg/kg total
Mercury—either incinerator residues or resi-
dues torn RMERC).
Phenyl mercury acetate: (All nonwastewaters that
are not incinerator residua* and are not resi-
dues from RMERC: regardless of Mercury Con-
tent).
N-Phenylthiouea
Phosgene..
Phosphine..
460-19-5
506-77-4
131-89-5
297-97-2
311-45-5
51-43-4
55-91-4
60-51-5
39196-18-4
122-09-8
534-52-1
541-53-7
151-56-4
7782-41-4
640-19-7
62-74-8
757-56-4
624-83-9
628-86-4
628-86-4
16752-77-5
75-55-8
60-34-4
75-86-5
116-06-3
86-86-4
54-11-5*
10102-43-9
10102-44-0
55-63-0
62-75-9
4549-40-0
152-16-9
20616-12-0
145-73-3
62-38-4
62-36-4
103-85-5
75-44-5
7803-51-2
CHCXD, WETOX; or INCIN
CHOXD; WETOX; or INCIN
(WETOX or CHOXD) fb CARBN;
or INCIN
CARBN; or INCIN
CARBN; or INCIN
(WETOX or CHOXD) fb CARBN;
or INCIN
CARBN; or INCIN
CARBN; or INCIN
(WETOX or CHOXD) fb CARBN:
or INCIN
(WETOX or CHOXD) fb CARBN
or INCIN
(WETOX or CHOXD) fb CARBN
or INCIN
(WETOX or CHOXD) fb CARBN
or INCIN
(WETOX or CHOXD) fb CARBN;
or INCIN
NA
(WETOX or CHOXD) fb CARBN;
or INCIN
(WETOX or CHOXD) fb CARBN;
or INCIN
CARBN; or INCIN
(WETOX or CHOXD) fb CARBN;
or INCIN
NA
NA
(WETOX or CHOXD) fb CARBN
or INCIN
(WETOX or CHOXD) fb CARBN
or INCIN
CHOXD; CHRED; CARSN
BIODG; or INCIN
(WETOX or CHOXD) fb CARBN
or INCIN
(WETOX or CHOXD) fb CARBN
or INCIN
(WETOX or CHOXD) fb CARBN
or INCIN
(WETOX or CHOXD) fb CARBN;
or INCIN
ADGAS
ADGAS
CHOXD; CHRED; CARBN-
BIODG; or INCIN
NA
(WETOX or CHOXD) fb CARBN;
or INCIN
CARBN; or INCIN
NA
(WETOX or CHOXD) fb CARBN;
or INCIN
NA
NA
(WETOX or CHOXD) fb CARBN;
or INCIN
(WETOX or CHOXD) fb CARBN;
or INCIN
CHOXD; CHRED, or INCIN
CHOXD; WETOX; or
INCIN.
CHOXD; WETOX; or
INCIN.
INCIN.
FSUBS; or INCIN.
FSU3S; or INCIN.
INCIN.
FSUBS; or INCIN.
FSUBS; or INCIN.
INCIN.
INCIN.
INCIN.
INCIN.
INCIN.
ADGAS lb NEUTR.
INCIN.
INCIN.
FSUBS; or INCIN.
INCIN.
RMERC.
IMERC.
INCIN.
INCIN.
FSUBS: CHOXD;
CHRED: or INCIN.
INCIN.
INCIN.
INCIN.
INCIN.
ADGAS.
ADGAS.
FSUBS; CHOXD;
CHRED; or INCIN.
INCIN.
INCIN.
FSUBS; or INCIN.
RMETU or RTHRM.
FSUBS; or INCIN.
RMERC.
IMERC; or RMERC.
INCIN.
INCIN.
CHOXD; CHRED; or
INCIN.
-------
Federal Register / Vol. 55, No. 106 / Friday, June 1, 1990 / Kules and Regulations
22697
Table 2.—Technology-Based Standards by RCRA Waste Code—Continued
Waste
code
See also
Waste descriptions and/or treatment subcategory
CAS No. for
regulated
hazardous
constituents
Technology code
Wastewaters
Nonwastewews
Propanuyl alcohol.
Sodium aiiOe
Strychnine and salts
Tetraethyldrthiopyrophosphate-
TetranhTometnane......
Table CCW in 268.43..
Table CCW in 26S.43..
Ttattre oxide..
Thatoum (!) sutfrne..
Thiosemcarbazide
Tnchioromatfianethiol..
Table CCW in 268.43-
Table CCW in 268.43...
Ammonium vanadate
Vanadium pentoxide..
Zmc Phosphide (<10%)
Aeetaldehyde
Table CCW tn 268.43
Acetonltrile
Acetyl Chloride.-.
Aoytamide
Acrylic acid
Mitomycin C.
Amtaole _
Auramme
Azasehne
Bertz(c)acridm«..
Senzal chloride..
Bertzenesultonyl chloride..
Berebdine
Berootrichlorida._
Chtomaphaan
Caibonyl fluoride
Tnchloroacetakfehyde (Chloral)-
Chlorambucil
Table CCW in 268.43..
Table CCW in 268.43..
Chlorobenzilate ............
1-Chtoro-&3-«poxypropane (EpictilorDhydrin)—
£-Chloroethyl vinyl ether
Chtoromethyl methyl ether..
4-Chioro-o-toluidine hydrochloride.
Crotonaldehyde
Cumene
Cydohexane
Table CCW In 268.43.—..
Cydohexanone
Cyclophosphamide..
Daunomycm
Oialtate
1,2,7.8-Dibervtopyrene..
107-19-7
26626-22-8
57-24-9"
3680-24-5
50&-14-8
1314-32-5
7446-18-6
79-1SV-6
75-70-7
7B03-55-6
1314-62-1
1314-84-7
75-07-0
75-05-8
75-36-5
78-06-1
79-10-7
SO-07-7
61-82-5
492-80-8
115-02-6
225-51-4
96-87-3
98-09-S
92-87-5
88-07-7
484-03-1
353-50-4
75-87-6
305-03-3
510-15-6
106-89-8
110-75-6
107-30-2
3165-93-3
4170-30-3
96-62-6
110-62-7
108-94-1
50-18-0
20830-81-3
2303-16-4
189-55-9
(WETOX or CHOXD) fb CARBN
or INCIN
CHOXD; CHRED; CARBN
BIODG; or INCIN
(WETOX or CHOXD) fb CARBN;
or INCIN
CARBN; or INCIN
CHOXD; CHRED; CAR3N;
BIODG; or INCIN
NA
NA
(WETOX or CHOXD) fb CARBN;
¦or INCIN
(WETOX or CHOXD) fb CARBN;
or INCIN
NA
NA
CHOXD; CHRED; or INCIN
(WETOX or CHOXD)
or INCIN
NA
(WETOX or CHOXD)
or INCIN
(WETOX or CHOXD)
or INCIN
(WETOX or CHOXD)
or INCIN
(WETOX or CHOXD)
or INCIN
(WETOX or CHOXD)
or INCIN
(WETOX or CHOXD)
or INON
(WETOX or CHOXD)
or INCIN
(WETOX or CHOXD)
or INCIN
(WETOX or CHOXD)
or INCIN
(WETOX or CHOXD)
or INCIN
(WETOX or CHOXD)
or INCIN
CHOXD. CHRED;
BIODG; or INCIN
(WETOX or CHOXD)
or INCIN
(WETOX or CHOXD)
or INCIN
(WETOX or CHOXD)
or INCIN
(WETOX or CHOXD)
or INCIN
NA
(WETOX or CHOXD)
or INCIN
NA
(WETOX or CHOXD)
or INON
(WETOX or CHOXD)
or INCIN
(WETOX or CHOXD)
or INCIN
(WETOX or CHOXD)
or INCIN
(WETOX or CHOXD)
or INCIN
NA
CARBN; or INCIN
(WETOX or CHOXD)
or INCIN
(WETOX or CHOXD)
or INCIN
(WETOX or CHOXD)
or INCIN
fb CARBN;
fb CARBN;
fb CARBN;
fb CARBN;
fb CARBN;
-------
22698
Federal Register / Vol. 55, No. 106 / Friday, June 1, 1990 / Rules and Regulations
Table 2.—Technology-Based Standards by RCRA Waste Code—Continued
Waste
coae
See also
Waste descriptions and/or treatment subcategory
CAS No. for
regulated
hazardous
constituents
Technology code
Wastewaters
Nonwastewaters
U073
U074
Table CCW in 268 43..
Table CCW in 266.43..
3,3'-Dichlorobenzidine..
cis-1,4-Diohloro-2-butene
trans 1,4-Dichloro-2-butene..
1,2:3,4-Diepoxybutane
N,N-Diethylh"drazine
0.0-0iettiyt S-methyldithicpbosphate..
Diethyl stilbestrot
DihydrosafTote
3,3'-0imethoxy benzidine..
Dimethylamine
p-Dimethylaminoazobenzane
7,12-Dimethyl benz(a)anthracene..
3,3-Dimethylberaidine
a,a-Dimethyl benzyl hydroperoxide -
Oimethylcarbomyl chloride
1,1 -Dimethylhydrazine -
1,2-Dimethylhydrazine
Dimethyl sulfate
1,2-Diphenylhydrazine
Dipropylamme —
Ethyl acrylate
Ethylene bis-dithiocarbarmc acid
Ethylene oxide
Ethylene thiourea
Ethyl methane sulfonate
Formaldehyde
Formic acid -
Furan
Furfural —
Glycidaldehyde -
Hexachlorophenene
Hydrazine -
Hydrogen Flouride
Hydrogen Sulfide -
Lasiocarpine ——
Maleic anhydride —
Maleic hydrazide —
Malononitrile
Melphalan -
91-94-1
1476-11-5
1464-53-5
1615-80-1
3288-58-2
56-53-1
94-58-6
119-90-4
124-40-3
621-90-9
57-97-6
119-93-7
80-15-9
79-44-7
57-14-7
540-73-8
77-78-1
122-66-7
142-84-7
140-8S-5
111-54-6
75-21-8
96-45-7
62-50-0
50-00-0
64-18-6
110-00-9
98-0.1-1
765-34-4
70-30-4
302-01-2
7664-39-3
7783-06-4
303-34-4
108-31-6
123-33-1
109-77-3
148-82-3
(WETOX or CHOXD)
or INCIN
(WETOX or CHOXD)
or INCIN
(WETOX Of CHOXD)
or INCIN
(WETCX or CHOXD)
Or INCIN
CHOXD; CHRED;
BIODG; or INCIN
CARBN; or INCIN
(WETOX or CHOXD)
or INCIN
(WETOX or CHOXD)
or INCIN
(WETOX or CHOXD)
or INCIN
(WETOX or CHOXD)
or INCIN
NA
(WETOX or CHOXD)
or INCIN
(WETOX or CHOXD)
or INCIN
CHOXD; CHRED;
BIODG, or INCIN
(WETOX or CHOXD)
or INCIN
CHOXD; CHRED;
BIODG; or INCIN
CHOXD: CHRED;
BIODG; or INCIN
CHOXD; CHRED;
BIODG; or INCIN
CHOXD; CHRED;
BIODG; or INCIN
(WETOX or CHOXD)
or INCIN
(WETOX or CHOXD)
or INCIN
(WETOX or CHOXD)
or INCIN
(WETOX or CHOXD)
or INCIN
(WETOX or CHOXD)
or INCIN
(WETOX or CHOXD)
or INCIN
(WETOX or CHOXD)
or INCIN
(WETOX or CHOXD)
or INCIN
(WETOX or CHOXD)
or INCIN
(WETOX or CHOXD)
or INCIN
(WETOX or CHOXD)
or INCIN
(WETOX or CHOXD)
or INCIN
CHOXD; CHRED;
BIODG; or INCIN
NA
fb CARBN;
fb CARBN;
fb CARBN;
fb CARBN;
CARBN;
fb CARBN;
fb CARBN
fb CARBN
fb CARBN;
fb CARBN;
fb CARBN;
CARBN;
fb CARBN;
CARBN;
CARBN;
CARBN;
CARBN;
fb CARBN;
fb CARBN;
fb CARBN;
fb CARBN;
fb CARBN;
fb CARBN;
fb CARBN;
fb CARBN;
fb CARBN;
fb CARBN;
fb CARBN;
fb CARBN;
CARBN;
CHOXD; CHRED, or INCIN
(WETOX or CHOXD) fb CARBN
or INCIN
(WETOX or CHOXD) fb CARBN
or INCIN
(WETOX or CHOXD) fb CARBN
or INCIN
(WETOX or CHOXD) fb CARBN
or INCIN
(WETOX or CHOXD) fb CARBN
or INCIN
INCIN.
INCIN
INCIN.
FSUBS; or INCIN.
FSUBS; CHOXD;
CHRED; or INCIN.
FSUBS; or INCIN.
FSUBS; or INCIN.
FSUBS; or INCIN.
INCIN.
INCIN.
INCIN.
FSUBS; or INCIN.
INCIN.
FSUBS; CHOXD;
CHRED; or INCIN.
INCIN.
FSUBS; CHOXD;
CHRED; or INCIN.
FSUBS: CHOXD;
CHRED; or INCIN.
FSUBS; CHOXD;
CHRED; or INCIN.
FSUBS; CHOXD;
CHRED; or INCIN.
INCIN.
FSUBS; or INCIN.
INCIN.
CHOXD; or INCIN.
INCIN.
INCIN.
FSUBS; or INCIN.
FSUBS; or INCIN.
FSUBS; or INCIN.
FSUBS; or INCIN.
FSUBS; or INCIN.
INCIN.
FSU8S; CHOXD;
CHRED; or INCIN.
ADGAS fb NEUTR; or
NEUTR.
CHOXD; CHRED; Of
INCIN.
INCIN.
FSUBS; or INCIN.
INCIN.
INCIN.
INCIN.
-------
Federal Register / Vol. 55, No. 106 / Friday, June 1. 1990 / Rules and Regulations
22699
Table 2 -Technology-Based Standards by RCRA Waste Code—Continued
Waste
code
See also
Waste descriptions and/or treatment subcategory
CAS No. for
regulated
hazardous
constituents
Technology r~-r1e
Wastewaters
Nonwastewaters
U151
U153
U154
U156
U160
U163
U164
U166
U167
U168
U171
U173
U176
U17?
U17B
U182
U184
U186
U189
U191
U1B3
U1M
U107
U200
U201
U202
U206
U213
U214
U215
U216
U217
U218
U219
U221
U222
U223
U234
U236
U237
U238
Table CCWE m 26841
and Table CCW r.
268.43
Table CCW tn 268.43..
Table CCW in 268 43..
Table CCW in 268 .43..
Table CCW in 268.43..
Table CCW in 268 43.......
Mercury. (High Mercury Subcategory—greater
man or equal to 260 mg/kg total Mercury).
Methane thiol
Methanol -
Methyl ctniorocarbonate
Metnyl ethyl ketone peroxide
N-Mettiy! N'-nitro N-Nitrosoguanidme
Mcthytthiouracil
1.4-Naphthoautncme
1 -*iaphthiyamine
2-Naphtnyamine..
2 JMitropropane
N-Nitroso-di-n-etnanolamine
N-Nitroso-N-ethylurea
N-NitrosoN-methylurea
N-Nitroso-N-methylurethane
Paraldehyde
Pentachloroethane
1,3-Pentadiene
Phosphorus sulfide..
2-ftcolirte
1.3-Propane sultone
n-Propyiamine
p-Benzoquinone
Reserpine
Resoicinol
Saccharin and salts
Streptorstocin..
Tetrahydrohiran
Thallium (I) acetate.
"Thallium (I) carbonate.-
Thallium (I) chloride
Thallium (I) nitrate
Thioscetamide
Thiourea..
Toluenediamine
o-Toluid
-------
22730
Federal Register /' Voi. 55, No. 106 / Friday, June 1, 1990 / Rules and Regulations
Tasle 2 —Technology-Based Standards sy RCRA Waste Code—Continued
Waste
ccae
U240
U244
U?46
U2A8
U249
I I CAS No. 'or
¦fe also 1 V, .^ste :;escrv.
•' This waste coae exists tn gaseous form and :s not categonzed as wastewater or nonwastewater forms.
NA—Not ApuhcaDie.
Table 3.—Technology-Based Standards for Specific Radioactive Hazardous Mixed Waste
Waste code
Waste descriptions and/or treatment subcategory
I
CAS Number
Technology code
Wastewaters
Nonwastewaters
D002 ; Radioactive High Level Wastes Generated During trie Reprocessing ot Fuel Rods Subcaie-
[ gory.
C004 Radioactive High Level Wastes Generated During the Reprocessing of Fuel Rods Subcate-
gory.
D005 ! Radioactive High Level Wastes Generated During the Reprocessing of Fuel Rods Subcate-
I gory.
DC06 - ! Radioactive High Level Wastes Generated During the Reprocessing of Fuel Rods Subcate-
gory.
D007 Radioactive High Level Wastes Generated Ouring the Reprocessing of Fuel Rods Subcate-
gory.
D008 Radioactive Lead Solids Subcategory (Note: these lead solids include, but are not limited to,
all farms of lead srnetdmg. and other elemental forms of lead. These lead solids do riot
include treatment residuals such as hydroxide sludges, other wastewater treatment
residuals, or incinerator asnes that can undergo conventional pozzolanic stabilization, rior
do they include organo-Jead materials that can be incinerated and stabilized as ash.).
D008._ Radioactive High Level Wastes Generated Dunng the Reprocessing of Fuel Rods Subcate-
gory.
D009 Elemental mercury contaminated with radioactive materials —
0009 Hydraulic oil contaminated with Mercury Radioactive Materials Subcategory
0009 Radioactive High Level Wastes Generated Dunng the Reprocessing of Fuel Rods Subcate-
gory.
D010 Radioacfive High Level Wastes Generated Dunrg the Reprocessing of Fuel Rods Subcate-
gory.
D011 Radioactive High Level Wastes Generated During the Reprocessing of Fuel Rods Subcate-
gory
U151 Mercury: Elemental mercury contaminated with radioactive materials ... -—
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA.
7439-92-1
NA
NA
NA
7439-97-6.
NA
7439-97-6
NA
NA._
NA.
NA
NA
NA
NA
7439-37-6
NA.
HLVIT
HLVIT
HLVIT
HLVIT
hlvit
macro
HLVIT
AMLGM
INClN
HLVIT
hlvit
HLVIT
AMLGM
NA—Not Applicable.
-------
Federal Register / Vol. 55, No. 106 / Friday, June 1, 1990 / Rules and Regulations
22701
Table CCW.—Constituent Concentrations in Wastes
Waste code
See also
Regulated hazardous constituent
CAS No. tor
regulated
hazardous
constituent
Wastewaters
concentration
(mg/t)
D0C3 (Reactive cyanides subcatego-
ry—tiased on 261.23(a)(5)).
D004
D005 -
D006
D007
D00B — -
D009
0010
D012 -
D013 - -
D014
DC 15 -
0016 -
D017 - -
F001-F005 spent solvents
F001-F005 spent solvents (Pharma-
ceutical industry wastewater sub-
category).
F006
Table CCWE in 268.41
Table CCWE in 268.41
Table CCWE in 268.41
Table CCWE in 266.41
Table CCWE in 268.41
Tabte CCWE in 268.41
Table CCWE In 268.41
Tabte CCWE in 268.41 _..._
Table 2 in 268.42
Table 2 in 268.42
Table 2 in 268.42
Table 2 in 268.42
Table 2 in 268.42...
Tabte 2 in 268.42
Table CCWE in 268.41 and Table 2
in 268.42.
Table CCWE in 268.41.
F007..
Table CCWE in 268.41..
Fooe.
Table CCWE in 268.41.
FOOD..
Table CCWE in 268.41.
F010-.
FOU-
Table CCWE In 266.41.
F012..
Table CCWE In 268.41.
F019-
F024..
Tabte CCWE in 268.41..
Table CCWE In 268.41 and Table 2
In 268.42 (Note: F024 organic
standards must be treated via In-
cineration (INCIN)).
Cyanides (Total)
Cyanides (Amenable)..
Arsenic
Barium
Cadmium
Chromium (Total)
Lead
Mercury
Selenium
Silver
Endrin
Lindane
Methoxychlor
Toxaphene
2.4-D
2,4,5-TP Silvex
1,1,2-Trichloroethane...
Benzene
Methylene chloride
Cyanides (Total>
Cyanides (Amenable).
Cadmium
Chromium.
Nickel-
Cyanides (Total)
Cyanides (Amenable) ¦
Chromium (Total)
Lead
Nickel
Cyanides (Total)
Cyanides (Amenable).
Chromium
Nickel..
Cyanides (Total)
Cyanides (Amenable)..
Chromium
Lead—
Nickel....
Cyanides (Total)
Cyanides (Amenable).
Cyanides (Total).
Cyanides (Amenable).
Chromium (Total)
Nickel
Cyanides (T otal)
Cyanides (Amenable).
Chromium (Total)
Nickel
Cyanides (Total)
Cyanides (Amenable)
Chromium (Total)
2-CWoro-1,3-butadiene..
3-CMoropropene
1.1-Oichkxoethane. .
1.2-Dtchkxoethan e
1 ,2-DicMoropropane
cls-1,3-Dichtoropropeoe
trans-1,3-Dichloropropene..
57-12-5
57-12-5
7440-38-2
7440-39-3
7440-43-9
7440-47-32
7439-92-1
7436-97-6
7762-49-2
7440-22-4
720-20-8
56-89-9
72.43-5
8001-35-1
94-75-7
93-76-5
71-55-6
71-43-2
75-09-2
57-12-6
57-12-5
7440-43-9
7440-47-32
7439-92-1
7440-02-0
57-12-5
57-12-5
7440-47-32
7439-92-1
7440-02-0
57-12-5
57-12-5
7440-47-32
7439-92-1
7440-02-0
57-12-5
57-12-5
7440-47-32
7439-92-1
7440-02-0
57-12-5
57-12-5
57-12-5
57-12-5
7440-47-32
7439-92-1
7440-02-0
57-12-5
57-12-5
7440-47-32
7439-92-1
7440-02-0
57-12-6
57-12-5
7440-47-32
126-99-8
107-05-1
75-34-3
107-06-2
78-67-6
10061-01-5
10081-02-6
Reserved
0.66
5.0
100
1.0
5.0
5.0
0.20
1.0
5.0
NA
NA
NA
NA
NA
NA
0.030
0.070
0.44
1.2
0.86
1.6
0.32
0.040
0.44
1.9
0.1
0.32
0.04
0.44
1.9
0.1
0.32
0.04
0.4
1.9
0.1
0.32
0.04
0.44
1.9
0.1
1.9
0.1
0.32
0.04
0.44
1.9
0.1
0.32
0.04
0.44
1.2
0.86
0.32
• 0-28
•0.28
• 0.014
• 0.014
• 0.014
•0.014
• 0.014
-------
22702
Federal Register / Vol. 55, No. 106 / Friday, June 1, 1990 / Rules and Regulations
Table CCW.—Constituent Concentrations in Wastes—Continued
Waste code
S«e also
Regulated hazardous constituent
CAS No. for
regulated
hazardous
constituent
Wastewaters
concentration
(mo/l)
F025 (Light ends subcategory)....
F025 (Seen! filters/ aids and desic-
cants subcategory).
F039..
Table COME in 268.41 _
Bis(2-ethyihexyl)phtfialate 117-81-7
Hexacnloroethane 67-72-1
Chromium (Total _...! 74.10-47-32
Nickel - ] 7440-02-0
Chloroform _ j 67-66-3
1,2-Oichlorcwthane I 107-06-2
1,1-Oicnloroethylene j 75-35-4
Methylene chloride ! 75-9-2
Carbon tetrachloride i 56-23-5
1,1,2-Trtcnloroethane i 79-00-5
Trichlcroethylene - | 79-01-6
Vinyl chloride „ _ ¦ 75-01-4
Chloroform i 67-66-3
Methylene cMorioe
Carbon tetrachloride __
1,1.2-Trichloroetftane
Tnchloroethyiene _
Vinyl chloride
HaxacWorobenzene
HexachloroDutaOiene
Hexachloroethane
Acetone
Acenaphtalene
AcenapWhene
Acetonitnle -
Acetophenone —
2-Acetylaminofluorene —
Acrytonitrile
Aldnn._ -
4-Aminobipbenyt
Aniline
Anthracene-
Arodor 1016..
Arodor 1221..
Arodor 1232..
Arodor 1242..
Arodor 1248..
Arodor 1254.
Arodor 1260..
alpha-8HC—
be la BHC
detta-8HC..
gamma-BHC
Benzene
Benzo
-------
Federal Register / Vol. S>, No. 106 / Friday. June 1, 1990 / Rales and Regulations
22703
Table CCW.—Constituent Concentrations in Wastes—Continued
Watte eoda
See atao
Regulated haiatdous constituent
CAS No. tor
regulated
hazardous
constituent
Wastewaters
concentration
(mg/l)
Non-
wastewaters
concentration
Img/kg)
Creeot (m- and p-isomers)
*0.77
"3.2
Cyclohexanone
108-94-1
*0.36
NA
1,2-Ditoromo-3-chloropropane
96-12-8
"0.11
•15
1,2-Otbromoethane (Ethylene dibro-
106-93-4
' 0.02B
• 15
mide).
Dtbrofftome thane
74-95-3
*0.11
• 15
2.4-DtcWoroph0noxyacetic acid (2,4-
94-75-7
*0.72
"10
U|-
o,p"-ODD
53-19-0
"0 023
* 0.087
p,p'-0DD
72-54-8
" 0.023
• 0.067
o,p'-DDE
3424-82-6
* 0.031
• 0.087
p.p'-DDE
72-55-9
'0.031
•0.067
0,p'-DOT
789-02-6
10.0039
• 0.087
p,p'-DDT
50-29-3
' 0.0039
•0087
Dlber«o(a.h)antnracene
53-70-3
* 0.055
•8.2
m-OicrtOfObenzene
541-73-1
' 0.036
•6.2
o-DicMorobenzeiie
95-50-1
"0.088
*6 2
p-Wchlorobenzene
106-46-7
"0.090
*6.2
Dichloroditluoromethane
75-71-8
•0.23
•7.2
1.1-Dtchtoroethane
75-34-3
• 0.058
4 7.2
1,2-Otchtoroethane
107-06-2
*0.21
"7.2
1. t-DtchtOfoethylene
75-35-4
"0 025
•33
trane-1,2-Dichloroethene
•0.054
•33
2.4-OicMcrophonol
120-83-2
"0.044
• 14
2.6-Oiehlorophenol
87-65-0
*0.044
• 14
1,2-Dict)loropropane
78-87-5
"0.85
•18
cta-1,3-Oichloropropene
10061-01-5
* 0.036
~ 18
trara-T.l-Oichloropropene
10061-02-6
• 0.036
• 18
Dieldrtn
60-57-1
"0.017
•0.13
Diethyl phthalate
84-66-2
'0.20
•28
p-Oimethylaminoazobenzene
60-11-3
'0.13
NA
2,4-Dimethyl phenol...-
105-67-8
"0.036
• 14
Dimethyl phthalate
131-11-3
'0.047
•28
Di-»>-btityt phthalate
84-74-2
• 0.057
•28
1,4-DMitrebenzene
100-26-4
"0.32
*2.3
4,6-OMtro-CK»eaai
534-52-1
"0.28
•160
2,4-DWtrophenol
51-28-5
"0.12
• 160
2,443Mrotoiuene
121-14-2
"0.32
• 140
2,6-OWtrotoluene
606-20-2
"0.55
•28
Dwveetyt phthalate
117-84-0
' 0.017
•28
Di-f ,
'0.000063
•0.001
HexeeMoroethene
67-72-1
' 0.065
•28
1 Hexeehloropropene
1888-71-7
'0.005
•28
Indenod ,2,3,-c,d)pyr»ne
193-39-5
•0.0055
•8.2
lodomethane
74-88-4
"0.019
•65
isobutanol
78-83-1
'5.6
•170
leodrin
465-73-6
"0021
•0066
leoevfroie.
120-58-1
"0.081
•2.8
Kapone
143-50-8
"0.0011
•0.13
MethaerytonitrUe
126-98-7
'0.24
•84
MethepyWene
91-80-5
'0.081
•1.5
-------
22704 Federal Register / Vol. 55, No. 106 / Friday, June 1. 1990 / Rules and Regulations
Table CCW.—Constituent Concentrations in Wastes—Continued
Waste code
See also
Regulated hazardous constituent
CAS No. tor
regulated
hazardous
constituent
Wastewaters
concentration
(mg/l)
Non-
wastewaters
concentration
(mg/kg)
Methoxychlor
72-43-5
* .0.25
•0.18
3-Metfiylcfioianmrene
56-49-5
• 0.0055
• 15
4.4-Metftv)ene-&s-{2-chloroaniline)
101-14-4
'0.50
•35
Methylene chlonde
75-09-2
* 0.089
•33
Methyl ethyl ketone
78-93-3
"0.28
•38
Methyl isobutyl ketone
108-10-1
*0.14
•33
Methyl nethacrylate
80-62-6
'0.14
• 160
Methyl methansulfonate
*0.018
NA
Methyl parathion
29S-00-0
"0.014
• 4.6
Naphthalene
91-20-3
* 0.059
•3.1
2-Naphtytamine
91-59-8
*0.52
NA
p-Nitroaniline
100-01-6
' 0.028
•28
Nitrobenzene
98-95-3
"0.068
• 14
5-Nitro-o-toluiamo _...
99-55-8
*0.32
•28
4-Nitrophenol
100-02-7
"0.12
•29
N-Nitrosodiethvlamine
55-18-5
"0.40
•28
N-Nrtrosodimethylamine
62-75-9
"0.40
NA
N-Nitroso-di-fi-t>utylamine
924-16-3
*0.40
•17
N-Nitrosomethytethylamine
10595-95-6
*0.40
•2.3
N-Nitrosomorpnoline
59-69-2
' 0.40
•2.3
N-Nltrosopipendine
100-75-4
*0.013
•35
N-Nitrosopyrrolidme
930-55-2
"0.013
•35
Parathion -
56-38-2
*0.017
•4.8
Pentachlorobenzene
608-93-5
' 0.055
•37
* 0.000035
•0.001
'0.000063
' 0.001
Pentachloronitrobenzene...
82-68-8
* 0.055
• 4.B
PentacMorophenol
87-86-5
' 0.089
•7.4
Ptienaceon
62-44-2
*0.081
• 16
Phenanthrene
85-01-8
* 0.059
•3.1
Phenol
108-95-2
*0.039
•6.2
Phorate
298-02-2
" 0.021
•4.8
Propanenitrile (ethyi cyanidel
107-12-0
" 0.24
•360
Pronamide -
23950-58-5
*0.093
• 1.5
Pyrene
129-00-0
*0.067
•8.2
Pyridine
110-86-1
*0.014
•18
Safrote
94-59-7
*0.061
• 22
SHvex (2.4,5-TP)
93-72-1
*0.72
•7.9
2.4,5-T
93-76-5
•0.72
•7.9
1 .2,4.5,-T etrachiorobenzene
95-94-3
' 0.055
• 19
Tetrachkxodibenzo-turana
'0.000063
•0.001
'0.000063
•0.001
'0.000063
NA
1.1,1.2-Tetrachloroethane
630-20-6
' 0.067
•42
1.1,2.2-T etrachkxoethane
79-34-6
• 0.057
•42
Tetraehkxoethene
127-18-4
'0.056
•5.6
2,3,4,6-T etracniofophenot
58-90-2
'0.030
•37
Toluene
106-88-3
'0.080
•28
Toxaohene
8001-35-1
*0.0095
• 1.3
1,2,4-T richiorooenzene
120-62-1
* 0.055
• 19
1.1,1-Tnchloroethane
71-55-6
*0.054
•5.6
1.1,2-T hchloroethane
79-00-5
'0.054
•5.6
Triehtoroethyiene
79-01-6
*0.054
•5.8
2.4,5-Trichlorophenol
95-95-4
"0.18
•37
2.4,6-T ricntorophenol
88-06-2
* 0.035
•37
12,3-T ncnloropropane
96-18-4
*0.85
•28
1,1^-TnchlofO-1.2.2-tnfluOfoeman«
76-13-1
• 0.057
•28
Vinyl chloride
75-01-4
¦0.27
•33
* 0.32
" 28
Cyanides (Total)
57-12-5
*1.2
• 1.8
Cyanides (Amenaole)
57-12-5
'0.86
NA
Fluoride
16964-48-6
¦36
NA
Sulfide -
8496-25-8
' 14
NA
Antimony
7440-36-0
•1.9
NA
AWJie.
7440-36-2
•8.0
NA
Barium
7440-39-3
"1.2
NA
Beryllium
7/.40-41-7
*0.82
NA
Cadmium
7440-43-9
•0.20
NA
7440-47-32
*0.37
NA
7440-50-8
' 1.3
NA
Lead
7439-92-1
'0.28
NA
Mercury
7439-97-6
'0.15
NA
Nickel
| 7440-02-0
'0.55
NA
Selenium
I 7782-49-2
*0.82
NA
Silver
7440-22-4
'0.29
NA
Vanadium _
! 7440-62-2
'0.042
NA
labteCCWE in 268.41
Naphthalene
I 91-20-3
• 0.0-11
•1.8
-------
Federal Register / Vol. 55, No. 106 / Friday," June 1, 1990 / Roles and Regriatfora
22705
Table CCW—Constituent Concentrations tw Wastes—Continued
Sw tiao
Regulated hazardoue conetHuant
CAS No. for
regelated
hazardoue
Weetewatare
conoentratlorr
(mQ/l)
Non-
' wastewaters
concentration
conatttuent
(mo/kg)
S7-8&-5
•0.031
•1.5
85-01-8
• 0.031
•\S
129-00-ff
•0.028
•1.5
108-86-3
•0.028
•28
•0.032
•33
NA
7439-92-T
~0.037
7440-47-32
*2.9
NA
7439-82-1
*3.4
NA
7440-47-32
*2 J»
NA
7439-82-1
'3.4
NA
7440-47-32
*2.9
NA
7439-82-1
*3.4
NA
7440-47-32
•2.9
NA
7439-82-1
'3.4
NA
57-T2-5
•0.74
rr
7440-47-32
*2.8
NA
7439-82-1
NA
7440-47-32
'2.9
NA
7439-82-1
*3.4
4 NA
57-12-6
*0.74
7440-47-32
*2.9
NA
7439-82-1
'3.4
NA
67-66-3
0.1
•6.0
67-66-3
0.1
6.0
75-05-8
38
1.8
107-13-1
0.06
1.4
79-06-1
19
23
71-43-2
0.02
0.03
57-12-6
21
57
75-06-8
38
•1.8
107-13-1
0.06
•1.4
78-06-1
19
•»
71-43-2
0.02
•0.03
57-12-6
21
57
75-05-6
38
•1.8
107-13-1
0.06
•1.4
79-06-1
19
•23
7T-43-2
OJBZ
•0.03
57-12-6
21
57
120-13-7
1.0
•3.4
98-87-3
0.28
•6J
205-89-2
207-08-8
0.029
3.4
85-01-8
0.27
•3.4
106-88-3
015
•6.0
7440-47-32
0.32
NA
7440-02-0
0.44
NX.
TT8-74-1
*•0.033
•28
t87-88-3
•0.007
•5.6
77-47-4
•0.007
• 5.6
67-72-1
•0.033
•28
127-18-4
•0.007
•ao
78-87-6
0.85
•i*
8ft-18-4
•O 0.85
• a.
TM-44-4
*,e 0.033
•72
75-00-3
•0.007
•6.0
75-34-3
•0.007
•6.0
107-06-2
•0.007
•6.0
87-72-1
•0.007
• 28
87-88-3
•0.033
•5.6
67-72-1
•0.007
•28
76-01-7
•0.007
•5.6
71-55-8
•0.007
•6.0
111-44-4
•0.007
•5.6
106-80-7
•0.008
•6.0
67-86-3
• 0.007
•6.0
106-46-7
•0.008
NA
107-06-2
•0.007
•6.0
86-73-7
•0.007
NA
67-72-1
•0.033
•28
*1-20-3
•O.OOTT
•5.6
85-01-8
•0.007
• &e
85-94-3
•0.017
NA
127-18-4
•0.00T
• &0
taO-88-T
•0.023
•t»
71-55-6
•0.007
*6.0
100-83-4
•0.007
•6.0
KD02.
K0C3.
K004.
K005..
K006..
K007 .
K008..
K009..
K010..
K01T..
Table CCWE i»26a;41
Tsbte CCWE In 268.41
Table CCWE In 266.41
Table CCWE in M8.41
Table CCWE m 266.41
Table CCWE —
Table CCWE li» 268-41._
K013.
KD14.
K0T5..
Table CCWE w 26&41
Kate
K01.7..
kots..
K019.
Pentachkxopbenol _
Phenanthrene
Pyrene.... —
Tetoene
Xylene* (Total) —
teed
Chromium (Total)..
Lead
Chromium (Total)..
Lead
Chromium (Total).
Chromium (Total)....
Lead..- - -
Cyenide* fTotaft
Chromium (Total) -
Chromium (Total)
Lead
Cyanides (Total)
Chromium (Total)
Lead...
Chloroform
Chloroform
Aeetonttrile
Acrytonitriie
Aerylamide
Cyanide (Total)
Aeetonttrile
Acrytonitriie
Acrytamlde
Benxena..
Cyanide (Total)...
Aeetonttrile
Acrytonitriie
Aerytunlde
Cyanide (Total)....
Anthracene ......
Benzal chloride. _
Sam of Benzo(b)fluoranthene
Beflzo(k)fluoranthene.
and
Toluene
Chromium (Total).
HojuuMurubemane
Hanachiwcbuladleno
Hexechioroethene...
TetrecNoroethene
t i-Dchtoropropane......
T,2,3-TrtcWoropropeno..
Bla(2^etMoroetriyf)ether..
CNeraathan*
I.SOicMoroethane
1,2-Ochloroetrwne
Haxaehioroethane
HexeeNorefcuiadiene
Homehtareethane
PontacNoroethane
1.1,1-Trtchtoroethane
BW2iChloroethyl)ether..
CMorsboraone...._..
Chloroform....................
p-OWMoroberttene
1,2^3iehioroethane
FHjorene
Koao..
ftienamtneiie ............—....
r.2,4>Te>acliiuioOenmie...
Taliaahioraethewe.
1^,4-TrteMorebenzene
i ,t,t" niUiMtmnviv>M ....•»
t,*Olehioroethane
-------
22706
Federal Register / Vol. 55, No. 106 / Friday, June 1. 1990 / Rules and Regulations
Table CON.—Constituent Concentrations in Wastes—Continued
Waste code
See also
Reg Dialed hazardous constituent
CAS No. for
regulated
hazardous
constituent
Wastewaters
concentration
(mg/l)
Non-
wastewaters
concentration
(mfl'kfl)
79-34-6
•0,007
•5.5
127-18-4
•0,007
•6.0
67-66-3
'0.046
•6.2
56-23-5
* 0.057
• 6.2
7440-36-0
"0.60
NA
106-68-3
'o.oeo
• 0.03-4
96-06-2
0.010
• 1t
22-36-4
•0.52
NA
86-30-e
•0.40
NA
NA
• 13
108-95-2
0.039
*12
7440-47-32
0.35
NA
7440-02-0
0.47
NA
85-44-6
•0.54
•28
85-44-9
•0.54
• £8
75-34-3
•0.007
•«.0
•0.033
•6.0
87-66-3
•0.007
• S.6
67-72-1
•0.033
•28
76-01-7
•0.033
•5.6
630-20-6
•0.007
•5.6
76-34-6
•0.007
•56
71-55-6
•0.007
•6.0
79-00-5
•0.007
•6.0
127-18—*
•0.007
•6.0
7440-43-9
6.4
NA
7440-47-32
0.35
NA
7439-92-1
0.037
NA
7440-02-0
0.47
NA
67-66-3
0.46
•6.0
107-06-2
Oil
•6.0
75-35-4
0.025
•6.0
71-55-8
0.054
•6.0
75-01-4
0.27
•6.0
96-50-1
•0.008
NA
106-46-7
* 0.008
NA
87-68-3
•0.007
•5.6
67-72-1
•0,033
• 28
1888-71-7
NA
•19
608-93-5
NA
•29
76-01-7
•0.007
•5.6
95-94-3
•0.017
•14
127-18-4
•0.007
•6.0
120-62-1
•0.023
•19
7440-38-2
0.79
NA
77-47-4
•0.067
•l*
57-74-9
*0.0033
•0.26
76-44-8
* 0.012
•0.066
1024-57-3
* 0.016
•0.066
77-47-4
"0.067
•ZA
77-47-4
•0.067
•2.4
83-32-9
NA
•3.4
120-12-7
NA
•3.4
56-55-3
*0.059
•3.4
50-32-8
NA
•3.4
218-01-8
'0.059
•3.4
53-70-3
NA
•3.4
206-44-0
'0.066
•3.4
86-73-7
NA
•3.4
193-39-5
NA
•34
'0.77
NA
91-20-3
'0.069
•3.4
95-46-7
•0.11
NA
85-01-6
'9.069
•3.4
106-95-2
0.039
NA
129-00-0
'0.067
•6.2
296-04-4
' 0.025
•0.1
298-04-4
' 0.02S
•0.1
108-88-3
*0.060
• 26
298-02-2
0.029
•0.1
298-02-2
0.089
•0,1
8001-36-1
'0.0094
•24
95-94-3
'0.066
•4.4
95-50-t
'POM
•4.4
K021..
K022.
K023.
K024-
K028.
K029.
K090-
K031 _
K032.
K033.
K034 ..
K035..
K038.
K037..
KD36.
K040-
K041.
K042.
Table CCWE in 268.41.
Table CCWE *268.41.
Table CCWE in 268.41.
Table CCWE in 268.41.
1,1,2.2-T etrachloroethane j
Tetrachloroethene J
Chloroform J
Catoon telracntonde
Antimony I
Toluene j
Acetophenone i
Diphenylamine J
Diphenylnitrosamme J,
Sum ot Diphenylamine and Dtpnenyt- i
nitrosamine |
Phenol
Chromium (Total) j
NicKe). - - j
Ptithalic anhydride (measured as I
Phthate: acid). j
Phthalie anhydride (measured as i
Pmhaiic acid). I
1,1-Gicntoroethane J
trans-1,2-Dicnloroemane _...,
Hexacttlorooutadiene J
Hexachloroethane — i
PemacMoroethane
1,1,1,2-T atrachtoroethane _i
1,1 ^.Z-Jatrachtoroafmne |
1,1,1 -Tnchioe thane j
1,1.2-Tnchlorethane
TatracNoroetftylene —
Cadmium
Chromium (Total)
J i
Nickel— - ..
Chloroform —
1,2-Oichloroflthane
1.1 -Dichloroethylene —
1,1,1-Tnchtoroethane
Vinyl chloride
o-OicMorobenzene
p-Otchtoroberaene
Hexachlorotxitadiene
Hexachtorobutadiene
Hexachloropropene
PantacMorotwnzene
PantachloroMhane
1,2.4,5-T atracMorobenzane
Tetrachloroethane
1,2.4-Tnchtorobenzene
Arsenic
Hexachkxopentadtene..
Chiorflane
HapttctHor.-
Heptadilor epoode...
HwacMorocydopentadiene..
HexacMorocyciopemadtene..
Aoanaphthene
Benztalanthracene
Benzo(a)pyrene
Chryaene...'—
Oibenz
-------
Federal Register / v/ol. 55, No. 106 / Friday, June 1. 1990 / Rules and Regulations
22707
Table CCW.—Constituent Concentrations in Wastes—Continued
Waste code
See also
Regulated hazardous constituent
CAS No. for
regulated
hazardous
constituent
Wastewaters
concentration
(mg/l)
Non-
wastewaters
concentration
(mfl/kg)
106-46-7
*0.090
•4.4
608-93-5
• 0.055
•4.4
120-82-1
*0.055
•4.4
120-83-2
•0.049
•0.38
87-65-0
•0.013
•0.34
95-95-4
•0.016
•8.2
88-06-2
• 0.039
•7.6
•0.018
•0.68
87-66-5
•0.22
•1.9
79-01-6
•0.006
•1.7
• 0.001
•0 001
•0.001
•0.001
•0.001
•0.001
•0.001
•0.001
•0.001
•0.001
•0.001
•0.001
7439-92-1
0.037
NA
71-43-2
•0.011
•14
50-32-8
•0.047
• 12
117-61-7
•0.043
•7.3
218-01-9
•0.043
• 15
84-74-2
•0.06
•3.6
100—41-4
•0.011
• 14
86-73-7
• 0.05
NA
91-20-3
• 0.033
•42
65-01-6
•0.039
•34
108-95-2
•0.047
•3.6
129-00-0
•0.045
•36
106-88-3
•0.011
•14
• 0.011
• 22
57-12-5
•0.028
•1.8
7440-47-32
0.2
NA
7439-92-1
0.037
NA
120-12-7
• 0.039
•26
71-43-2
•0.011
•14
50-32-6
•0.047
•12
117-81-7
•0.043
~7.3
75-15-0
•0.011
NA
2216-01-9
•0043
•15
105-67-9
•0.033
NA
100-41-4
•0.011
•14
91-20-3
•0.033
•42
85-01-8
•0.039
•34
108-85-2
•0.047
•3.6
129-00-0
•0.045
•36
106-86-3
•0.011
•14
•0.011
• 22
57-12-6
• 0.028
•1.8
7440-47-32
0.2
NA
7439-92-1
0.037
NA
50-32-6
•0.047
•12
108-95-2
•0.047
•3.6
57-12-5
•0.028
•1.8
7440-47-32
0.2
NA
7439-92-1
0.037
NA
208-96-8
•0.06
NA
120-12-7
•0.039
•28
71-43-2
•0.011
•14
50-32-6
•0.043
•20
117-81-7
•0.047
•12
75-15m
•0.043
•7.3
2216-01-9
•0.043
•16
. 105-67-9
•0.06
•3.6
. 100-41-4
•0.011
•14
86-73-7
•0.05
•NA
. 91-20-3
•0.033
•42
85-01-8
•0 039
•34
108-96-2
• 0.047
•36
. 129-00-0
•0.045
•36
. 108-66-3
• 0.011
•14
•0.011
•22
. 57-12-5
•0.028
•1.8
. 7440-47-32
0.2
NA
. 7439-92-1
0.037
NA
. 71-43-2
•0.011
•14
. 50-32-8
•0.047
•12
. 96-46-7
•0.011
•6.2
KCM3..
K046..
K048..
Table CCWE in 268 41..
Tabic CCWE In 268.41..
K049..
Table CCWE In 268.41..
K050..
Table CCWE in 268 41..
K051.
Table CCWE in 268.41.,
K052.
Table CCWE In 268.41..
p-Dichloroberaene
Pentachlorobenzene
1.2.4-Trichiorobenzen e
2,4-Oichiorophenoi
2,6-Oichlorophenoi
2.4.5-Trichloropheno l
2.4.6-Trichloropheno l
Tetrachiorophenols (Total)..
HexacMorodibenzo-p-flioxms...
Hexachtorodibenzo-turans —
Pentachlorodtoenzo-jMliownj..
Pentachlorodibenzo-turan*
Tetnchiorodlbenzo-p-dioxtns...
Tetrachlorodiberrco-furans
Lead
Benzene _
Benzo(a)pyrene
Bls(2-ethylhexyl)phthalate
Chiysene
OMvbutyt phthalats
Ethylbenzene
Fktorene
Naphthalene
Phenanthrene
Phenol
Pyrene -
Toluene —
Xylene**)
Cyanide* (Total)
Chromium (Total). ....
Lead
Anthracene .....
Benzene
Benzo
-------
22708
Federal Register / Vol. 55, No. 106 / Friday, ]une 1, 1990 / Rules and Regulations
Table CCW.—Constituent Concentrations in Wastes—Continued
Regulated hazardous constituent
MM
CAS No. for
regulated
hazardous
constituent
Wastewaters
concentration
(mo'l)
Non-
wastewaters
concentration
(mg/kg)
p-Cresol
106-44-5
•0.011
•6.2
2,4-Dimethylphenol
105-67-9
• 0.033
•NA
Ethylbenzene
100-41-4
• 0.011
•14
Naphthalene
91-20-3
•0.033
•42
Phenanthrene
85-01-8
• 0.039
•34
Phenol
108-96-2
•0.047
•3.6
Toluene
108-88-3
• 0.011
•14
Xylenes
•0.011
• 22
Cyanides (Total)
57-12-5
• 0.028
• 1.8
Chromium (Total) _
7440-47-32
0.2
NA
Lead
7439-92-1
0.037
NA
Benzene
71-43-2
0.17
• 0.071
Benzo(a)pyrene
50-32-8
• • 0.035
•3.6
Naphthalene —
91-20-3
*¦• 0.028
•3.4
Phenol
108-95-2
0.042
•3.4
Cyanides (Total)
57-12-5
1.9
1.2
Cadmium
7440-43-9
1.61
NA
Chromium (Total)
7440-47-32
0.32
NA
Lead- -
7439-92-1
0.51
NA
NicKei
7440-02-0
0.44
NA
Chromium (Total)
7440-47-32
0.32
NA
Lead-
7439-82-1
0.04
NA
Nickel -
7440-02-0
0.44
NA
Cadmium
7440-43-9
1.6
NA
Lead-
7439-02-1
0.61
NA
Mercury
7439-97-6
0.030
NA
Carbon tetracnlonde
56-23-5
"0.057
•6.2
Chloroform
67-66-3
"0.046
*6.2
Hexachlor oethane
67-72-1
' 0.055
•30
Tetrachloroethene
127-18-4
*0.056
•6.2
1,1,1-Tnchloroethane.-
71-55-6
"0.054
•6.2
8enznne
71-43-2
"0.14
• 6j8
Aniline
62-53-3
•'o:8i
•14
Diphenylamme
22-39-4
*0.52
NA
Diphenylnitrosamine
86-30-6
"0.40
NA
Sum of Diphenylamine and Diphenyl-
rxtroeamine.
NA
• 14
Nitrobenzene
98-95-3
'0068
•14
Phenol —
108-95-2
0.039
•5.6
Cyclohexanone
106-94-1
0.38
•30
Nickel -
7440-02-0
0.47
NA
Arsenic
7440-38-2
0.79
NA
Benzene
71-43-2
"0.14
•4.4
Chiorobenzene -
108-90-7
"0.067
•4.4
o-Oichlorooenzene
95-50-1
"0.068
•4.4
m-Dichlorobenzene
541-73-1
"0.036
•4.4
p-Oiehlorobenzene
106-46-7
'0.090
•4.4
1,2,4-Trichlorobenzene
120-82-1
"0.055
•4.4
1,2.4,5-T etrachlorobanzene
95-84-3
" 0.055
•4U
Pentaehlorobenrene —
608-93-5
0.055
•4.4
Hexachlor ooanzene
116-74-1
" 0.065
•4.4
Aroclor 1016 -
12674-1, 2
"0.013
•0.92
Aroolor 1221 -
11104-26-2
"0.014
•0.92
Aroclor 1232
11141-16-5
"0.013
• 0.92
Aroclor 1242
53469-21-9
"0,017
•0.92
Aroclor 1248
12672-29-6
'0.013
•0.92
Aroclor 1264
110B7-69-1
"0.014
•1.6
Aroclor 1260
11096-62-5
'0.014
• 1.8
Acetone
67-64-1
0.28
• 160
Acetophenone -
96-66-2
0.010
•9.7
Bia(2-ethylhexyi)phthalale
117-81-7
' 0.26
• 28
n-Butyl alcohol -
71-36-3
5.6
•2.6
Butylbenzylphthalate
85-66-7
"0.017
• 7.1
cyclohexanone
108-94-1
0.36
NA
1,2-Dichlorobenzene
96-50-1
0.088
• 6,2
Diethyl phthalate
84-66-2
"0,20
•28
Dimethyl phthalate
131-11-3
"0.047
•28
Dt-n-butyl phthalate
84-74-2
" 0.057
•26
Dw>-octyl phthalate
117-64-0
"0.017
•28
Ethyl acetate
141-78-6
'0.34
• 33
Ethylbenzene
100-41-4
"0.057
•6.0
Methanol
67-56-1
* 8.6
NA
Methyl isobutyl ketone.
108-10-1
0.14
•39
Methyl ethyl ketone -
78-93-3
0.20
• 36
Methylene ehlonde „
75-08-2
'0.088
•33
Waste code
See also
KQ6C.
K061.
K062.
K069.
K071..
K073..
KQ63 ¦
K084.
KQS6.
xoae.
Table CCWE in 268.41
in 268 42.
and Table 2 !
Table CCWE in 268.41 ....
Table CCWE In 268.41
in 268.42.
and Table 2
Table CCWE in 268.41..
Table CCWE in 268.41..
Table CCWE in 268.4.1.
-------
Federal Register / Vol. 55, No. 106 / Friday, June 1. 1990 , Rules and Regulations 22709
Table CCW.—Constituent Concentrations in Wastes—Continued
CAS No. tor
regulated
hazardous
constituent
Wastewaters
concentration
(mg/i)
Norv
wasteweters
concentration
(mg/kg)
91-20-3
* 0.059
•3.1
86-85-3
'0.068
•14
108-86-3
"0.080
•28
71-65-6
*0.054
•5.6
70-01-6
*0.054
•5.6
*0.32
•28
57-12-5
1.9
1.5
7440-47-32
0.32
NA
7439-02-1
0.037
NA
206-96-6
• 0.028
3.4
71-43-2
• 0.014
• 0.071
218-01-9
•0.028
•3.4
206-44-0
• 0.028
•3.4
193-39-5
• 0.028
*3.4
91-20-3
•0.028
•3.4
65-01-6
• 0.028
•3.4
108-86-3
•0.008
•0.65
• 0.014
•0 07
7439-92-1
0.037
NA
65-44-9
•0.54
•28
85-44-9
•0.54
•28
630-20-6
0.057
•5.6
79-34-6
0.057
•5.6
127-18-4
0.056
•6.0
79-00-5
0.054
•6.0
79-01-6
0.054
•5.6
67-72-1
0.055
•28
76-01-7
0.055
•5.6
630-20-6
0.057
•5.6
79-34-6
0.057
•5.6
127-18-4
0.056
•6.0
79-00-5
0.054
•6.0
79-01-6
0.054
•5.6
541-73-1
0.036
•5.6
76-01-7
0.055
•5.6
120-82-1
0.055
•19
77-47-4
'0.057
2.4
57-74-9
*0.0033
•0.26
76-44-6
'0.0012
•0.066
1024-57-3
'0.016
•O.066
8001-35-1
*0.0095
•2.6
94-75-7
»1
•1
•0.001
•0.001
•0.001
•0.001
•0.001
•0.001
•0.001
•0.001
•0.001
•0.001
•0.001
•0.001
7440-43-9
1.6
NA
7440-47-32
0.32
NA
7439-92-1
0.51
NA
•0.27
* 14
7440-38-2
079
| NA
7440-43-9
0.24
1 NA
7439-92-1
0.17
! NA
7439-97-6
0.082
| NA
I • 0.028
! * 13
. 7440-38-2
j 0.79
i NA
. 7440-43-9
0.24
NA
7439-92-1
017
! NA
7439-97-6
i 0.082
| NA
62-53-3
| * 4.5
' 5.6
•| 71-43-2
| *0.15
: "6.0
•| 51-28-5
• 061
-5.6
96-95-3
* 0.07:.
•5.6
., 106-95-2
* 1.4'
'56
.; 92-53-3
* 4,f
•5.6
71-43-2
•0.15
* 6
¦j 51-28-5
•0.61
5.6
.; 96-95-3
•0.073
'5.6
.' 106-95-2
• 1.4
' 5.6
.! 57-12-5
2./
• 1.8
. 71-43-2
OK
' <4
.1 106-90-7
0.05'/
• a 4
•! 95-50-1
0 08f
* 4.4
Waatecode
SnMo
Regulated hazardous constituent
K087.
Table CCWE in 288.41..
K093.
K094.
K095.
K096.
K097.
K096.
K099.
K100..
K101 ..
K102.
K103 .
K104
K105.
Tabic CCWE in 266.41..
Tabie CCWE in 266.41.
Naphthalene
Nitrobenzene
Toluene
1.1.1-Trichloroethan e
Trichloroethylene
Xylenes (Total)
Cyanides (Total)
Chromium (Total)
Lead
Acenaphthalene
Benzene
Chryaene
Fluoranthene
lndeno(1,2,3-ed)pyrene
Naphthalene
Phenanthrene
Toluene
Xylenes
Lead
Phthalic anhydride (measured I
Phthalic acid).
Pnthakc anhydride (measured i
Phthalic acid).
1,1,1,2-T etrachloroethane
1,1,2.2-T etrachloroethane
Tetrachloroethene
1.1.2-Trichloroethan e —
Trichloroethylene
Haxaehtoroethane
Pentachloroethane ...
1,1,1,2-T etrachloroetnane
1,1,2,2-T etrachloroethane
TetracMoroethene ....
1,1,2-Trichloroethane
Trichloroethene ......
1.3-Dichk>robenzen e -..
Pentachloroethane
1,2.4-Trichiorobenzene
Hexachiorocyctopentadiena
CNordane
HepwcWor
Heptachlor epoxide -
Toxaghene
2.4-Dchiorophenoxyacetic acid
Hexachtorodibenzo-p-dKWtns
Hexachlorodibenzolurans
P«raachlorodibenzo-o-dK»ins
Pentachlorodibenzofurans
Tetrachlorodib«nzcn>-dioMns
Tetrachtorodiben2oturans
Cadmium
Chromium (Total)
O-Nttroanihne..
Arsenic
Cadmium
Mercury
o-Nitrophenol..
Arsenic
Cadmium
Lead
Nitrobenzene.
Benzene..
Nitrobenzene.
Benzene
Chtarobenzene
o-Dwhtorobenzene..
-------
22710
Federal Register / Vol. 55, No. 106 / Friday, June 1, 1990 / Rales and Regulations
Table CCW.—Constituent Concentrations in Wastes—Continued
Waste code
See also
Regulated hazardous constituent
CAS No. tor
requtaied
hazardous
constituent
Wastewaters
concentration
(mfl/l)
Non-
wastewaters
concentration
(mg/kg)
p>Dichiorobenzene -
106-48-7
0.090
•4.4
2,4,5-Tnchloropftenol
95-95-4
0.18
•44
2,4.6-TncWorophenol
88-06-2
0.035
•4.4
2-Chlorophenol
95-57-8
0.044
•4.4
Phenol
106-95-2
0.030
*4.4
K*06 -
Table CCWE in 268.41 and Tabic 2
7439-97-8
0.030
NA
in 260.42.
K11S
Table CCWP in _
7440-02-0
0.47
NA
I
* Treatment standards tor ttiis organic constituent were established based uoon incineration in units operated in accordance witti the technical requirements of 40
CFR Part 264 Subpart O or Part 265 auopart O, or oaseo upon comoustion in fuel suDsmunnn units operating in accordance with applicable technical requirements. A
facility may cermv compliance witn these treatment standards according to provisions in 40 CFR Section 2S8.7.
' Based on anaivss ot composite samples.
' As analyzed us>nq SW-846 Method 9010; sample size: 0.5-10; distillation time: one hour to one hour and fifteen minutes.
NA—Not Applicant.
Table CCW.—Constituent Concentrations in Wastes
Commercial chemical name
See also
Regulated hazardous constituent
CAS No. for
regulated
hazaraous
constituent
Wastewaters
concentra-
tion (mg/l)
Aldrtn
Arsenic acid —
Arsenic pentoxide
Arsenic tnoxide
Banum cyanide
2-sec-ButyM.6-dinitrophenol (Dinoaab)..
Calcumryarude
Table CCWE in 268.41
Table CCWE m.268.41
Table CCWE in 268.41
Table CCWE in 268.41
Carbon -disulfide
ChCNoroaniline
Coppercyamde
Table 2 in 288.42
Cyantdes'(soluble salts and complexes^.
Dichloicphenytarsine..
Oieldnn
Diethylaraine
Disulfoton—
4,6-Dinrtroo-cresol.....
2,4-Dimtrophenol
Endosulfan
Table CCWE in 288.41..
Table CCWE in 288.41..
Aldnn
Arsenic
Arsenic
Arsenic
Cyanides (Total)
Cyanides (Amenable)
2-sec-ButyM,6-dini«ropftenof (Dinoseb)..
Cyanides (Total) -
Cyanides (Amenable) _
Carton disulfide __
p-Chioroaniline
Cyanides (Total)
Cyanides (Amenable) —
Cyanides (Total) -
Cyanides (Amenable)
Arsenic
Oieldnn -
Arsamc
Disulfoton.. -
Endrtn..
Fluoride -
Heptachtor..
Table 2 in 268.42..
Isodrin
Hydrogen cyanide..
Mercury fulminate..
Methyl perathion..
Nickel carbonyt....
Nickel cyanide
Table CCWE in 268.41
and Table 2 in 288.42.
Table CCWE m 268.41..
Table CCWE in 268.41..
p-Nitroantline
N-Nitrosodimethylarmne....
Parathion
Phenyimercury acetate
Table 2 in 268:42..
Table CCWE m 268.41
and Table 2 in 268.42.
Phorate
Famphur—
Potassium cyantOe
Potassium silver cyanide..
Ethyl cyanide (PropanenMa).
Selenourea —
Table CCWE m 288.41..
Table CCWE in 268.41..
4.8-Dinitro-o-creaol..
2.4-Dimtrophenoi
Endosulfan I
Endosulfan II
Endosulfan sulfate...
Endnn
Endrin aldehyde
Fluoride
Heptachtor..
Heptactilor epoxide
isodrin
Cyanides (Total)
Cyanides (Amenable).,.
Mercury -
Methyl parathion
Nickel
Cyanides (Table)
Cyanides (Amenable)
Nickel
p-Nitroaniltne
N-Nttrosodimethylamine..
Parathion-
Mercury
Phofita
Famphur
Cyanides (Total)
Cyanides (Amenable)
Cyanides (Total)
Cyanides (Amenable)
Sliver
Ethyl cyanide (PropanenttrHe)...
Selenium
308-00-2
7440-38-2
7440-38-2
7440-38-2
57-12-5
57-12-5
88-85-7
57-12-5
57-12-5
75-15-0
108-47-8
57-12-5
57-12-5
57-12-5
.57-12-5
7440-38-2
60-57-1
7740-38-2
298-04-4
534-58-1
51-26-5
939-98-8
33213-8-5
1031-07-8
72-20-8
7421-93-4
16064 48 8
76-44-8
1024-57-3
485-73-8
57-12-5
57-12-5
7439-97-8
298-00-0
7440-02-0
57-12-5
57-12-5
7440-02-0
100-01-6
82-75-9
58-38-2
7439-97-8
298-02-8
52-85-7
57-12-5
57-12-5
57-12-5
57-12-S
7440-22-4
107-12-0
7782-49-8
*0.21
0.79
0.79
0.79
1.9
0.1
0.066
1.9
0.1
0.014
0.46
1.9
0.1
1.9
0.1
0.79
'0.017
0.79
0.017
"0.28
*0.12
" 0.023
'0.029
'0.029
'0.0028
*0.025
35
'0.0012
' 0.016
'0.021
1.9
0.10
0.030
0.025
0.44
1.9
0.10
0.44
*'0.028
*0.40
0.025
0.030
0.026
0.025
1.9
0.10
1.9
0.1
029
' 0.24
'1 0
-------
Federal Register / Vol. 55. No. 106 / Friday, June 1. 1990 / Rules and Regulations
22711
Table CCW.—Constituent Concentrations in Wastes—Continued
Commercial cltemicel name
See also
Regulated hazardous constituent
CAS No. tor
regulated
hazardous
constituent
Wastewaters
jemra-
(mg/l)
0063
U066
U067
U068
U069
U070
U071
U072
U07S
11076
UQ77
U078
U079
U080
uoei
U0B2
Silver cyanide..
Table CCWE in 268.41.
Sodium cyanide....
Tetrsetbyl lead
T naiiic oxide
Thallium selenite
Thellium(l)sut(ate
Ammonia vanadate ...
Vanadium pentoxida..
Zinc cyanide
Table CCWE In 266.11
and Table 2 ir> 286.42.
Table 2 m 268.42
Table CCWE In 268.41
Table 2 m 268.42
Table 2 in 268.42
Table 2 in 268.42
Cyanides (Total)
Cyanides (Amenable)..
Silver
Cyanides (Total)
Cyanides (Amenable)-
Thallium
Selenium
Thallium
Vanadium
Vanadium
Cyanides (Totsl)..
Toxaphene..
Acetone
Acetonitrile
Acetophenone
2-AcetylaminofluOfene
Acrylonrtrila
Aniline...
Benzlalantnracene
Benzene ....
Benzolaipyrene
Bis(2-chloroethoxy)methane_
6isi2-chloroethyl)ether-
Tabte 2 *>268.42.
Cyanides (Amenable) _
Toxaphene
Acetone
Acstonitnle
Acetophenone
Bis(2-chloroiscpropyl) ether..
Bis(2-ethylhexyl) pthalata -
Bromomathane (Methyl bromide)..
4-Bromophenyl phenyl ether
rvButyi alcohol
Calcium chromate
Table CCWE In 268.41.
Chlordane (alpha and gamma) -
Chlorobenzene _____
Cnlorobenzilaie
p-Chlonwivcresol — —
2-Chloroethyl vinyt
Vinyl chloride
Chloroform
Table 2 In 26842-
Table 2 in 268.42
Chloromethane (Methyl chloride).
2-Chlororiaphthaiene
2.Chtofophenol
Chryaane
Creosote
Table CCWE m 268.41._
i Gesols (Cresylic tod)
Cyciohexanone.
ODD
Table 2 In 26842...
DOT.
D;Danzo(t.h)antnracen«
I 1,2-Dibromo. 3-cMoiop»oparte
j 1.2-Oibromoethar.e (EthylenedHxoffMa).
| Dibromonethane -
j On-buty! phtnalate
I o-Ditfhlorobertzene _...
j ro-DiChlorooenzene
I p-Dichlorobenzene
| Dtchtorodifluorometnarta...—
j 1 l-Dichioroethane
| 1,2-Diehtaroe thane..
1.1-Dichloroethylen e
1.2-Dichloroethylen e
Methylene chionde
2,4-Dichlorophenol
i 2 6-Oehloroohenol
2-Ao»tylamino(luorene
Acrytomtiiie
AWtota
Benz(a)anthrac9ne
Benzene
Benzolaipyrene..
Bis(2-chloro0t]ioxy)methane.-
BW2-chloroethy!)emar
B«(2-chlorotsopropy1) ether „.
Bts)2-«thylhexyl) ptnalate.
Bromomathane (Methyl bromide)..
4-Bromophenyl phenyl ether
n-Butyl alcohol
Chromium (Total)....
57-12-5
57-12-5
7440-22-4
57-12-5
57-12-5
7439-82-1
7440-28-0
7782-4£-2
7440-26-0
7440-62-2
7440-62-2
57-12-5
57-12-5
8001-35-1
67-64-1
75-05-8
08-86-2
53-66-3
107-13-1
62-5S-3
56-55-3
71-43-2
50-32-8
111-91-1
111-44-4
38638-32-9
Chlordane (alpha and gamma).
Chlorobenzene
CMorobereitaie
p-Chtoro-m-cresol.
2-Chloroethyl vinyl..
Vinyl chloride
Chloroform..
Chloromethane (Methyl chloride) ....
2-CMoronaphthalene
2-Chiorophenoi
Chrysene
Naphthalene
Pantachlorophenol—
Phenanthrana
Pyrane
Toluene
Xylenes (7 otal;
o-Craaol
Crawls (m- and p- isomers).
Cytiohexanone
04)'-DDD..
p^'-DDD.
o.p'-DDT
PJl'-ODT
oji'-DOD
P4)'-DOC
041-ODE
W-ODE
Dibenzo(a.h)antmacene..
1 J-Otoromo^.eWoroprooane
1^-Dibromoethane (Ethylene dlbromide)..
Dibromonethane
Di-rvbutyl phthaiate -
o-Dicniorobanzane
m-DtcHorobenzene. -
p-Oichtorobenzene
DtcNorodHluorometnane
1.1-Oichloroetnan e —
1.2-Oichioroethane —
1,1-Dtchtoroetnylene
trans-1 ^-Dicnloroethylene
Methylene chloride
2.4-Dtchlorophenol
2,0-OicNoropr«nol
117-81-7
74-83-9
101-56-3
71-36-3
7440-47-32
57-74-9
108-90-7
51&-15-8
59-50-7
110-75-8
75-01-4
67-86-3
74-87-3
91-56-7
95-57-8
218-01-9
91-20-3
87-86-5
65-01-8
129-00-0
106-66-3
7438-92-1
95-46-7
106-94-1
53-19-0
72-54-8
789-02-6
5C-29-3
63-19-0
72-54-8
3424-82-6
72-55-9
53-70-3
96-12-8
106-93-4
74-95-3
84-74-2
96-50-1
541-73-1
104-46-7
75-71-8
76-34-3
107-0&-Z
75-35-4
156-60-5
75-09-2
120-63-2
61-65-0
1.9
0.10
0.29
1.9
0.10
0.040
*0.14
1.0
"0.14
"28
*28
1.9
0.10
'0.0095
0.26
017
• 0.010
*0.059
" 0.24
o.ei
*0.059
*0.14
*0.061
0.036
0.033
'0.055
•0.54
'0.11
*0.055
5.6
0.32
*0.0033
*0.057
*0.10
*0.018
0.057
* 0.27
*0.046
*0.19
*0.055
*0.044
*0.059
•0.031
•0.18
•0.031
•0.028
•0.028
•0.032
• 0X137
*0.11
*0.77
o.se
0.023
0.023
'0.0039
'0.0039
*0.023
' 0.023
*0.031
*0.031
*0.055
*0.11
*0.028
*0.11
•0.54
*0.088
0.036
*0.090
" 0.23
*0.059
*0.21
' 0.025
" 0.054
•0.089
•0.044
*0.0*4
-------
22712
Federal Register / Vol. 55, No. 106 / Friday, June 1, 1990 / Rules and Regulations
Table CCW.—Constituent Concentrations in Wastes—Continued
Waste
coda
Commercial chemical name
See also
Regulated hazardous constituent
CAS No. for
regulated
hazardous
constituent
Wastewaters
concentra-
tion (mg/l)
U083
U064
1.2-Dichloropropan e
1.3-Dichtoropropen e
j Diettiyf phthalate
I p-Dimethytammoazobenzene..
2,4-Dimethylpneno(
l Dimethyl phthalate
' 2.4-Dinitrotoluene
j 2,6-Oinitrotohiene
Dwvoctyl phthalate
1,4-Dioxane
Di-r»-propylnitrosoamine
Ethyl acetate
Ethyl ether
Ethyl methacrylate..
Table 2 in 268.42
Fluoranthene
T richloromonofluoromethane -
i Hexachlorobenzene _
Hexachlorobutadiene
Lindane
Hexachlorocydopentadiene _
Hexachtoroethane
Hydrogen fluoride
Gacodylic acid..
Table 2 in 268.42
Table CCWE in 268.41.
Indenof 1,2,3-c,d)pyrene _
lodomethane
Isobutyl alcohol
Isosatroie
Kepone..
Lead acetate..
Lead phosphate..
Lead subacetate..
Mercury
Methacrytonttriie..
Methapynlene..
Table CCWE in 268.41....
Table CCWE in 268.41....
Table CCWE In 268.41
Table CCWE in 268.41
and Table 2 in 268.42.
3-Methytchloanttvene_
4.4'-Methytenebis<2-chtoroaniline)..
Methyl ethyl ketone
Methyl isobutyl ketone
Methyl methacrylate..
Naphthalene
2-Naphthyl amine
Table 2 in 268.42
4-Nitrophenol..
rvNrtrosodwvbutytamine .
N-Nitroaodietnylanmne
N-Nitroaopipendine..
N-Nitroaopyrn>Mine
5-Nitro-o-loluidine
Pentachlorobenzene
Pentachlororwrobenzene..
Phenacetin
PhthaHc anhydride (measured as
ic add).
Pronamide
Pyridine
Salrole—
Selenium dioxide.-.
Selenium aulftde..
1,2,4,5-Tetrachlorcbenzen*-
Table CCWE in 268.41
Table CCWE m 268.41
1,1,1,2-Tetrachforoethane
i. 1,2,2-Tetrachloroemane.
Tetrachloroethyiene.
Carbon tetrachloride..
TaUiumOlacetate..
Th«Mium(l)cafbonate—
ThaHium(l)chtonde
ThaHium(l)nitrata ...
Toluene...
Table 2 in 268.42....
Table 2 in 268.42...
Table 2 in 268.42....
Table 2 in 268.42....
Tribromomethane (Bromoform)._
1.1.1-TricWoroemen e __
1.1.2-T nchioroethane
12-Oichloropropane
c»-1,3-Oicf)loropropytene
trans-1,3-Dichloiropropylene.—
Diethyl phthalate
p-Oimethyiaminoazoberaene....
2.4-Oimethytphenof
Dimethyl phthalate
2,4-Oinitrotoiuene
2,6-Oinitrotokjene
Dwvoctyl phthalate
1,4-Oioxane
Di-n-propylnitrosoamine -
Ethyl acetate —
Ethyl ether
Ethyl methacrylate
Fluoranthene
TnchlofomonoNuoromethane
Hexachlorobenzene
Hexachlorobutadiene
alpha-BHC
beta-8HC
Delta-8HC
gamma-BHC (Lindane)
Hexachtorocydopentadiene....
Hexachloroethane
Fluoride
Arsenic
lndeno( 1,2.3-c,d)pyrene—
lodomethane........
Isobutyl alcohol
Isosafrole
Kepone...
Lead
Lead
Mercury..
Methacrytonitnle-
Methapyrilene..
3-Methyfcholanthrane...
4.4'-Methytenebis(2-cnioroaniline)..
Methyl ethyl ketone
Methyl isobutyl ketone
Methyl methacrylate
Naphthalene...
2-Napnthyiamne
Nitrobenzene
4-Nitrophenol.. ~
n-Nrtrosodwvtxjtylamine —
n-Nitrosodiethytarmna -
n-Nitrosopipehdine
rvNitroaopyrrotidiM
5-Nitro-o-toloKJin e
Panlachlorobenzene
Pentachloronitrodenzene
Phenacetn
Phenol ...
Phthalic anhydnoe (measured as Phth al-
io acid).
Pronamide J
Pyridine J
Safrola..
=|
Selenium
Selenium
1 ,2.4.5-TetracMorooenzene..
1,1,1.2-TetracWoroethane
1.1 A2-Tetracmoro#thane j
TetraohkNoathvfene. _
Carbon tetrachloride
Thallium J
Thallium —
Thallium J
Thallium J
Toluene ................. J
Tribromomethane (Bromotorrn) i
1.1, l -T nchioroethane —
1.1,2-T nchioroethane !
78-87-5
10061-01-5
10061-02-6
84-66-2
80-11-7
105-67-8
131-11-3
121-14-2
806-20-2
117-64-0
123-91-1
621-64-7
141-78-8
60-29-7
97-63-2
206-44-0
75-66-4
118-74-1
87-68-3
319-84-8
319-85-7
319-86-8
58-89-9
77-47-7
67-72-1
16964-48-8
7440-38-2
193-39-5
74-88-4
78-83-1
120-68-1
143-50-8
7439-62-1
7436-92-1
7439-92-1
7439-97-6
126-98-7
91-80-5
56-40-5
101-14-4
78-93-3
108-10-1
80-62-8
91-20-3
91-59-8
96-95-3
100-02-7
924-16-3
55-18-5
100-75-4
930-56-2
99-5W
606-93-6
82-68-4
62-44-2
108-96-2
85-44-9
23950-58-8
110-86-1
94-59-7
7782-49-2
7782-49-2
86-94-3
630-20-6
79-34-5
127-18-4
56-23-5
7440-28-0
7440-26-0
7440-26-0
744O-26-0
108-68-3
75-25-2
71-55-6
79-00-5
•0.85
' 0.036
• 0.036
' 0.54
•0.13
¦0.036
' 0.54
•0.32
•0.55
' 0.54
•0.12
•0.40
•0.34
•0.12
•0.14
•0.068
•0.020
• 0.055
• 0.055
•0.00014
0.00014
0.023
0.0017
• 0.057
•0.055
35
0.70
> 0.0055
•0.1B
8.6
0.081
0.0011
0.040
0.040
0.040
0.030
•0.24
0.081
•0.0055
•0.50
0.28
0.U
0.14
• 0.059
•0.52
•0.068
•0.12
•0.40
•0.40
• 0.013
•0,013
>0.32
•0.055
•0.088
0.081
0.039
>0(4
0.093
•0.014
0.081
1.0
1.0
*0.065
0,067
•0.057
•0.086
•0.067
•0.14
• 014
• 0.14
•0.14
•0.080
•0.63
•0.064
•0.064
-------
Federal Register / Vol. 55, No. 106 / Friday. June 1, 1990 / Rules and Regulations 22713
Table CCW.—Constituent Concentrations in Wastes—Continued
Waste
code
Commercial chemical name
See also
Regulated hazardous constituent
CAS No. tor
regulated
hazardous
constituent
concentra-
tion (mg/l)
concentra-
tion (mg/kg)
L'228
U235
U239
U240
U243
U247
Trichloroethytsne
WM2,3-[>bromopropyt)-phoepWrte _
Xylenes.
g.i-Oichlorophenoxyaoetic add-
Hexachkrapropene
Methoxyehlor
Trichtoroethytene
trM2.3-Dihioinopropyt>-phoaphate...
Xylenes.
2,4-Oichlorophenoxyaoetic acid..
HexacNoropropene
Methoxyehlor.
79-01-8
126-72-7
94-75-7
1868-71-7
72-43-6
*0.064
0.026
*0.32
0.72
>0.035
»0i6
'5.6
'0.10
'28
> 10
28
'0.18
> Treatment standards for ttta organic constituent (were established based won Incineration in units operated m accordance with the technical requirements of 40
CFP Part 264 Subpart 0 or Part 266 Subpart 0, or based upon combustion in fuel substitution units operating in accordance with applicable technical requirements. A
facility may certify compliance with these treatment standards according to previsions in 40 CFR Section 268.7.
* Based on analysis of composite samplea.
' As analyzed using SW-848 Method 9010; sample size: 0.5-10: distMatlon lime: one hour to one hour fifteen minutes.
NA—Not Applicable.
-------
APPENDIX C
LAB PACKS
Appendix IV—Orgaoonrwtallic Lab
Pack*
Hazardous waste with the following
EPA waste codes may be placed in an
"organometallic" or "Appendix IV lab
pack:"
P001, P002, P003, P004, P005, P006, POO7,
P008, P009, P013, POM, P015, P016,
P017, P018, P020, P022, P023, P024,
P025, PO20, P027, P028, P031, P034,
P03B, P037, P038, P039, POM, P041,
P042, P043, P044, P045, P047, P048,
P049, P050, P051. POM, P056, P057,
P058, P0S9, P060, P062, P063, P064,
P065, P066, P067, P088, P069, P070,
P071. P072, P073, P074, P075, P077,
P081, P082, P084, P085, P087, P088,
P089, PO02, P093, P094, P095. PD96,
P097, P098, P099, PlOl, P102, P103,
P104, P105, Pi 08, P109, P110, P112,
P113, P114, P115, P116, P118, P119,
PI 20, P122, PI 23
U001, U002, U003, U004, U005, U008.
U007, U008, U009, U010, U011, U012,
U014, U015, U016, U017, U018, U019,
U020, U021, U022, U023, U024, U02S,
U026, U027, U028, U029, U03a U031.
U032, U033, U034, U035, U036, U037,
U038, U039, U041, U042, U043, U044,
U045, U046, U047, U048, U049, U050,
U0S1, U052, U053, U055, U056, U057,
U058, U059, U060, U061, U062, U063,
U064, U086, U067, U088, U069, U070,
U071, U072, U073, U074, U075, U076,
U077, U078, U079, U080, U081, U082.
U083, U084, U085, UO08, U087, U088,
U089, U090, U091, U092, U093, U094,
U095, U096, U097, U098, U099, U101,
U102, U103, U105, U106, U107, U108,
U109, UUO, Ulll, U112, U113, U114,
U115, U116, U117, U118, U119, U120,
U121, U122, U123, U124, U125, U128,
U127, U128, U129, U130, U131, U132,
U133, U134, U135, U138, U137, U136,
U137, U138, U139, U140, U141. U142,
U143, U144, U145, U146. U147, U148,
U149, U160, U152. U164, U153, U154,
U165. U156, U157, U158, U1S9. U16a
U1B1, U162, U164. U185, U186, U167,
U188 U1B9, U170, U171, U172, U173,
U174, U176, U177. U17B. U179, U180,
Ulfll, U182, U183, U184, U185. U166
U187, U188, U189, UlflO, U191, U192,
U193, U1B4, U196, U197, U200, U201,
U202, U203, U204, U205, U206, U207,
U20B, U209, U210, U211, U213, U214,
U215, U216, U217, U21B, U219, U220,
U221, U222, U223, U225, U220, U227,
U228, U234, U235, U236, U237, U238,
U239, U240, U243, U244, U248, U247,
U248, U249, U328, U353, U359
F001, F002, F003, F004, F005, F006, F010,
F020, F021, FD23, F024, F026, FO27.
F028
KOOl, K002, K008, K009, KOIO, KOll,
K013, K014, K015, K016, K017, KOI 8,
K019, K020, K021, K022, K023, K024,
K025, K028, K027, K028. K029, K030,
K031, K032, K033, K034, K035, K038,
K037, K038, K039, K040, K041, K042,
K043, K044, K045, K048, K047, K048,
K048, K050, K051, K052, K054, K060,
KO01, K064, K065, K066, K089, K071,
K073, K083, K084, K085, K086, K087,
K093, K094, K095, K096, K097, K098,
K099, K101, K102, K103, K104, K105,
Kill. K112, K113. K114, K115, K110.
K117, K118, K123, K124, K125, K128,
K136
D001, D002, D003, D004, D005, D006,
D007, D008, D010, D011, D012, D013,
D014, D015, D016, D017
U032. U136, U144, U145, U146, U163,
U214, U215, U216, U217
14. Appendix V is added to part 268 to
read as follows:
Appandix V—Organic Lab Packs
Hazardous wastes with the following
EPA Hazardous Waste Code No. may be
placed in an "organic" or "Appendix V:"
P001, P002, P003, P004, POOS, P006, P007,
P008, P009, P013, P014, P01S, P018,
P017, P018, P020, P022, P023. P02S.
P024, P026, P027, P028, P031, P034,
PO30. P037, P038. P03B, P040. P041,
P042, P043, P044. P045, PO40, P047,
P048, P049, P050, P051, POM. P057.
P058, P059, P060, P0S2, P083, P064,
P064, P06S, P066, P067, P068, P069,
P070, P071, P072, P073, P074, P075,
P077, P081, P082, P084, P085, P087,
P088, P089, P092, P093, P094. P085,
P096, P097, P098, P099. PlOl, P102.
P103. P104. P10S, P108, PI09, P110,
Pill, P112, P113, P114, P115. P116,
P118, P119. PI 20, P122. P123
U001, U002, U003, U004, U005, U006,
U007, U008. U009, U010, U011, U012,
U014, U015, U018, U017, U018, U019,
U020, U021, U022, U023, U024, U025,
U026, U027, U028, U029, U030, U031,
U033. U034, U035, U036. U037, U038,
U039, U041, U042. U043, U044. U04S.
U048, U047, U048. U049, U050, U0S1.
U052, U053, U055, U056, U057. U058.
U059, U060, UOfll. U0B2. U083, U084,
U066, U067, U068, U0S9, U070, U071,
U072. U073, U074. U07S, U078, U077.
U078. U079, U080, U081, U082, U083,
U084, U08S, uoas, U0B7, U088. U089,
U090, U091, U092. U093, U094, U098,
U096, U097, U09B, U099, U101. U102,
U103, U10S, U1O0, U107, U108, U109,
una Ulll. U112, U113, UlU. U115,
U11B, U117, UUS. U119, U120. U121.
U122. U123, U124. U125, U126. U127,
um U129, Ul3a U131, U132, U133,
U135, U137, U138, U139. U140. U141.
U142, U143, U147. U148. U149, U1SO.
U153, U154, U155, U156, U157, U158,
ui59, uieo, mei, uie2, um uih.
U165. U106. U167, U168 U169. Ul7a
U171. U172. U173, U174, U176, U177.
U178, U179, U180, U181, U182. U183.
U184, U185, U188 U187. U188. U189.
U190, U191, U192, U193. U194. U196,
U197, U200, U201. U202. U203, U205.
U206, U207, UZ08, U209, U210. U211,
U213, U214, U218. U219, U22a U221.
U222. U223. U225, U228, U227, U228.
U234, U235. U236. U237, U238. U239,
U240, U243. U244, U246, U247. U248,
U249, U328, U353. U359
FOOT, F002, F003, F004, F005, FOIO, F020.
F021, F023, F024, F028. F027, F028
KOOl. K009, K010. KOll, K013. K014.
K015, K010. K017. K018. K019, K02a
K021. K022, K023, K024, K02S, K028,
K027, K029. K030, K031, K032. K033.
K034, K035, K036. K037, K038. K039.
K040, K041. K042, K043, K044, K04S.
K048, K047, K04& K049, KOSO, K051,
K052. K054, K060, K06S. K073, K083.
K084. K08S. K086, K087, K093, K094.
K09S. K096, K097, K098. K099. K101.
K102. K103. K104, K10S, Kill. K112,
K113. K114, K11S, K118, K117. K118.
K123, K124. K125, K128, K130
DQ01,0012. D013.0014. D015. D016.
D017
C-l
Printed on Recycled Paper
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OCLC 1141781889 Held by EHA - no other holdings
Rec stat n Entered 20200225 Replaced 20200225
Type a ELvl K Srce d Audn Ctrl
BLvl m Form Conf 0 Biog MRec
Lang eng
Ctry mau
Cont GPub f LitF 0 Indx 0
Desc i Ills a Fest 0 DtSt s Dates 1990
040 EHA *b eng +e rda *c EHA
088 EPA 901-S-90-001
099 EPA 901-S-90-001
049 EHAD
245 0 0 Land disposal restrictions : *b summary of requirements / *c United States Environmental Protection
Agency, Region I, Waste Management Division.
264 1 [Boston, MA]: *b United States Environmental Protection Agency, Region I, Waste Management
Division, *c 1990.
300 iv, 20, A6, B25, C1 pages : *b figures, tables ; *c 28 cm
336 text #b txt *2 rdacontent
337 unmediated *b n +2 rdamedia
338 volume *b nc +2 rdacarrier
500 Cover title.
500 "August 1990."
650 0 Hazardous wastes *x Law and legislation *z United States.
710 1 United States. *b Environmental Protection Aaencv. *b Region I. *b Waste Management Division.
*e issuing body.
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