OOOR94101
UNITED STATES ENVIRONMENTAL PROTECTION AGENCY
PCB Q & A MANUAL
An EPA TSCA assistance document designed to provide the regulated
community with Agency interpretations to frequently posed
questions.*
Prepared by:
OPERATIONS BRANCH
CHEMICAL MANAGEMENT DIVISION
OFFICE OF POLLUTION PREVENTION AND TOXICS
1994 EDITION
* This publication is an informal document, and persons are
directed to the PCB final rules at Title 40 of the Code of
Federal Regulations part 761 (40 CFR part 761) except where
otherwise noted for specific legal requirements. This document
provides information on the regulatory requirements for
polychlorinated biphenyls that have been reflected in.final
regulations published through December 31, 1990. Any past
versions of this document either final or in draft form are now
obsolete.
U S. Environmental Protection Agency
Region 5, Library (PL-12J)
77 West Jackson Boulevarjj, 12tn Floor
Chicago, IL 60604-3590
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--FOREWORD--
The PCB Q & A Manual has been prepared to assist the user in
answering frequently asked questions on the PCB regulations. It
is a quick source of information that will be updated as new
rules and policies become final. The looseleaf style and
pagination within chapters will facilitate updating as needed.
Each time a new chapter is added, a new table of contents and a
new alphabetical list of chapters will also be generated. All
persons to whom EPA has sent the PCB Q & A Manual will
automatically receive updates with instructions to add and/or
replace pages already in the binder. Please complete the
following Update Request Form and mail this entire page to:
Environmental Assistance Division (7408), Environmental
Protection Agency, 401 M St. S.W., Washington, DC 20460, or call
the TSCA Assistance Information Service at 202-554-1404 to
receive the PCB Q & A Manual Updates and Revisions.
- PCB Q & A MANUAL -
Update Request Form
FACILITY:
STREET ADDRESS:
CITY: STATE : ZIP:
ATTENTION:
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TABLE OF CONTENTS
Introduction i
History of the PCB Regulations iii
PCBs in the Workplace ix
Regional PCB Branch Offices xiv
CHAPTER i
I.
Transformers
A. NonRailroad
B. Railroad
II. Capacitors
III.
IV.
V.
VI.
VII.
VIII.
IX.
X.
XI.
XII.
XIII.
XIV.
XV.
XVI.
XVII.
XVIII.
XIX.
A.
B.
Large
Small
Heat Transfer and Hydraulic Systems
Natural Gas Pipelines
Electromagnets, Switches, and Voltage Regulators
Circuit Breakers, Reclosers, and Cable
Research and Development
Microscopic Mounting Medium, Immersion Oils, Optical
Liquids
Carbonless Copy Paper
Excluded PCB Products
Recycled PCBs and Excluded Manufacturing Processes
PCB Storage Requirements
PCB Disposal Requirements
PCB Spill Cleanup Policy
Recordkeeping and Reporting
PCB Testing Procedures
Import and Export
PCB Transformer Fire Related Requirements
PCB Notification and Manifesting Rule
Appendix I - Code of Federal Regulations
Appendix II - Commercially Permitted PCB Disposal Companies
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ALPHABETICAL LIST OF CHAPTERS
*
CHAPTER:
Appendices
II. Capacitors
A. Large
B. Small
IX. Carbonless Copy Paper
VI. Circuit Breakers, Reclosers, and Cable
V. Electromagnets, Switches, and Voltage Regulators
X. Excluded PCB Products
III. Heat Transfer and Hydraulic Systems
XVII. Import and Export
VIII. Microscopic Mounting Medium, Immersion Oils, Optical
Liquids
IV. Natural Gas Pipelines
XIII. PCB Disposal Requirements
XIX. PCB Notification and Manifesting Rule
XIV. PCB Spill Cleanup Policy
XII. PCB Storage Requirements
XVI. PCB Testing Procedures
XVIII. PCB Transformer Fire Related Requirements
XV. Recordkeeping and Reporting
XI. Recycled PCBs and Excluded Manufacturing Processes
VII. Research and Development
I. Transformers
A. NonRailroad
B. Railroad
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- INTRODUCTION -
The term PCB is an acronym for polychlorinated biphenyl. PCBs
are produced by attaching one or more chlorine atoms to a
biphenyl molecule. As one of the most stable organic compounds
known, their properties made them useful as dielectric fluid in
various types of electrical equipment and heat transfer systems.
Monsanto Corporation was the principal manufacturer of PCBs for
use as a fire-resistant or nonflammable insulating fluid in
electrical and heat transfer equipment. In 1977, Monsanto
voluntarily ceased production of PCBs because of widespread
environmental concerns about the chemical.
PCBs were sold under the trade name "Aroclor." However,
companies that used PCBs in the manufacture of transformers and
capacitors, and for other uses, often used other trade names.
Common trade names for PCBs include the following:
COMMON TRADE NAMES
Aroclor Chlorinol Fenclor Nonflammable Liquid
Arochlor B Chlorphen Hyvol Phenoclor
ALC Clophen Inclor Pydraul
Apirolio Clorinol Inerteen Pyralene
Asbestol Diaclor Keneclor Pyranol
ASK DK Kenneclor Pyroclor
Askarel* Dykanol Magvar Saf-T-Kuhl
Adkarel EEC-18 MCS 1489 Santotherm
Capacitor 21 Elemex No-Flamol Santovac 1 and 2
Chlorextol Eucarel Nepolin
*Askarel is also the generic term used for nonflammable
insulating liquid in transformers and capacitors.
"Askarel" PCBs are chemical mixtures containing many different
PCB congeners. They have a heavy, liquid, oil-like consistency,
and weigh 10 to 15 pounds per gallon. They are very stable,
exhibit low water solubility, low vapor pressure, low
flammability, high heat capacity, low electrical conductivity,
and have a favorable dielectric constant for use in electrical
equipment.
When PCBs were manufactured as dielectric fluid for transformers,
they were often mixed with certain organic solvents such as
chlorinated benzenes. Therefore, the dielectric fluids present
in the electrical transformers containing PCBs are usually not
pure PCB. The presence of these other chemicals influences the
physical/chemical properties of the Askarel fluid.
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PCBs are also produced as byproducts and process impurities in
certain chemical manufacturing processes. They may vary from a
single isomer to a variety of congeners and display different
physical and chemical properties, depending on the number of
isomers and the degree of chlorination (the number of chlorine
atoms attached to the biphenyl molecule). PCBs with fewer
chlorine atoms are, in general, less persistent, more water
soluble, and more flammable than PCBs with more chlorine atoms.
HEALTH EFFECTS
PCBs are toxic and persistent. Available laboratory animal
studies indicate an oncogenic potential whose degree varies with
exposure. Epidemiological data are not now adequate to confirm
or negate oncogenic potential in humans. Further epidemiological
research is needed to correlate human and animal data. However,
EPA finds no evidence to suggest that the animal data would not
predict an oncogenic potential in humans.
PCBs can enter the body through the lungs, gastrointestinal
tract, and skin. They circulate throughout the body and are
Stored in the body's fatty tissue. EPA finds that PCB exposure
may cause negative reproductive effects and developmental
toxicity in humans. Available data show that some PCBs have the
ability to alter reproductive processes in mammals, sometimes
even at doses that do not cause other signs of toxicity. Animal
data and limited available data on humans suggest that prenatal
exposure to PCBs can result in various degrees of developmental
effects. Postnatal effects have been demonstrated on immature
animals, following exposure to PCBs prenatally and via breast
milk.
In some cases, chloracne may occur in humans exposed to PCBs.
Severe cases of chloracne are painful and disfiguring, and may be
persistent. Although the effects of chloracne are reversible,
EPA considers these effects to be significant. For more
information on the health effects of PCBs, The Response to
Comments on the Health Effects of PCBs submitted by the Chemical
Manufacturers Association and the Edison Electric Institute is
available from the TSCA Assistance Information Service at 202-
554-1404.
In addition to the toxic effects related to exposure to PCBs
alone, EPA is very concerned about the toxicity of the chemicals
produced when PCBs are involved in fire-related incidents. These
chemicals include polychlorinated dibenzofurans (PCDFs) and
polychlorinated dibenzo-p-dioxins (PCDDs), both of which are
believed to be much more toxic than PCBs themselves. Toxico-
logical effects of these chemicals include embryotoxicity,
teratogenicity, reproductive effects, and oncogenicity. Other
compounds of toxicological significance may also be produced and
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released from fires involving PCB equipment. For further
information on ttte health effects of dioxins, The Ambient Water
Quality Criteria For 2.3,7,8-Tetrachlorodibenzo-p-dioxin is
available from the TSCA Assistance Information Service at 202-
554-1404.
ENVIRONMENTAL EFFECTS
Certain PCB congeners are among the most stable chemicals known
and decompose very slowly once they are released into the
environment. They remain in the environment and are taken up and
stored in the fatty tissue of organisms. EPA has concluded that
PCBs can be concentrated in freshwater and marine organisms.
Available data show that PCBs affect the productivity of
phytoplankton and the composition of phytoplankton communities.
PCBs also cause deleterious effects on environmentally important
freshwater invertebrates and impair reproductive success in birds
and mammals.
PCBs are toxic to fish at very low exposure levels and can
adversely affect their survival rate and reproductive success.
The literature shows that various sublethal physiological effects
on bone development and reproductive organs are attributed to
exposure to PCBs. Phytoplankton are the primary food source
directly or indirectly of all sea organisms. Also, phytoplankton
are a major source of oxygen in the atmosphere. The transfer of
PCBs up the food chain from phytoplankton to invertebrates, fish,
and mammals can result in human exposure through consumption of
PCB-containing food sources.
- HISTORY OF THE PCB REGULATIONS -
In recognition of the risks associated with PCBs and their
widespread distribution throughout the environment, in 1976, the
United States Congress enacted the Toxic Substances Control Act
(TSCA), which banned with limited exceptions the manufacture,
processing, distribution in commerce, and use of PCBs other than
in a "totally enclosed manner". Section 6(e) of TSCA also
required EPA to promulgate regulations for the proper disposal of
PCBs and develop clear and adequate warnings and instructions
with respect to their processing, distribution in commerce, use
and disposal. Section 16 of TSCA provides for penalties up to
$25,000 a day per violation of section 6(e) of the Agency's PCB
regulations.
PCB marking and disposal regulations were published in the
Federal Register on February 17, 1978 (43 FR 7150). The PCB "Ban
Rule" (Federal Register May 31, 1979) included provisions banning
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the manufacture, processing, distribution in commerce, and use of
PCBs which became effective on July 2, 1979 (44 FR 31514).
The May 31, 1979 Rule:
• Designated all intact, nonleaking capacitors,
electromagnets and transformers, other than railroad
transformers, as "totally enclosed," which allowed
their use without restrictions or conditions;
• Established a 50 ppm PCB regulatory cutoff for
manufacturing, processing, distribution in commerce,
and use; and
• Authorized the use of PCBs under specific conditions
and time constraints for 11 activities. These
activities were:
• Servicing transformers (other than railroad
transformers),
Use in and servicing of railroad transformers,
Use in and servicing of mining equipment,
Use in heat transfer systems,
Use in hydraulic systems,
Use in carbonless copy paper,
Use in pigments,
Use in and servicing of electromagnets,
Use in natural gas pipelines,
Use in small quantities for research and
development, and
• Use as a mounting medium in microscopy.
The Environmental Defense Fund (EDF) challenged several
provisions of the May 1979 rule, and in October of 1980, the U.S.
Court of Appeals for the District of Columbia ruled that there
was insufficient evidence in the record to support several
provisions of the May 1979 rule. Specifically, the Court struck
down the classification of transformers, capacitors, and
electromagnets as "totally enclosed," and the regulatory cutoff
at 50 ppm for the manufacture, processing, distribution in
commerce, and use of PCBs. The 11 use authorizations contained
in the May 1979 rule remained in effect. EPA, EDF, and certain
industry representatives filed a joint motion seeking a stay of
the Court's mandate until further rulemaking could be completed.
The Court granted the stay.
On August 25, 1982, EPA issued a final rule governing the use and
servicing of electrical equipment containing PCBs (47 FR 37342).
This final rule was issued as a result of the Court's decision to
strike down the May 1979 rule's classification of transformers,
capacitors, and electromagnets as "totally enclosed." In the
August 25, 1982 rule, EPA authorized the use of electrical
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equipment containing PCBs with certain conditions and
restrictions intended to minimize human and environmental
exposures to PCBs.
On October 21, 1982, EPA issued part one of a two-part rule to
address the 50 ppm regulatory cutoff (47 FR 46980) . This final
rule addressed closed and controlled waste manufacturing
processes. EPA submitted a plan to the Court on November 1,
1982, that requested a further extension of the- stay of mandate
for the 50 ppm cutoff and presented plans for the completion of
the rulemaking on this issue. (The October 21, 1982 rule was
superseded later by the "Uncontrolled PCB's Rule" issued on July
10, 1984.)
In addition to issuing rules as a result of the Court decision in
October 1980, EPA also promulgated an amendment to the Use
Authorization for Railroad Transformers which originally appeared
in the May 1979 rule. On January 3, 1983, EPA published a final
rule amending and extending the use authorization for PCB
railroad transformers (48 FR 124).
On March 30, 1983, EPA promulgated a procedural change in the
approval process for mobile and non-unique disposal facilities
(48 FR 13181). The authority for granting or denying approval of
these facilities was transferred from the regions to EPA
headquarters.
On July 10, 1984, several rulings were made final. One rule
addressed individual and class petitions for exemption from the
prohibition against the manufacture, processing, and distribution
in commerce of PCBs (49 FR 28154). The use of small quantities
of PCBs for use in research and development was authorized
indefinitely.
On July 10, 1984, EPA also issued an amendment to the October 21,
1982 rule (49 FR 28172). This "Uncontrolled PCB's Rule"
completed part two of EPA's earlier 1982 rulemaking regulatory
cutoff for PCBs, which was overturned in the 1980 Court decision.
This rule excluded additional processes from regulation based
upon EPA's determination that these processes do not present an
unreasonable risk of injury to human health or to the
environment. Among other things, the rule permitted the
manufacturing, processing, distribution in commerce, and use of
inadvertently generated PCBs and recycled PCBs under limited
circumstances. This amendment replaced the terms "Closed
Manufacturing Process" and "Controlled Waste Manufacturing
Process" with "Excluded Manufacturing Process." PCBs with
concentrations below 50 ppm, under certain conditions and
restrictions, were authorized for use in hydraulic and heat
transfer fluid and in the compressors and liquid of natural gas
pipeline systems.
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On November 8, 1984, a final rule was issued that revised the
definition of "Totally Enclosed Manner" (49 FR 44634). It
changed from "any manner that will ensure that any exposure of
human beings or the environment to any concentration of PCBs will
be insignificant, that is, not measurable or detectable by any
scientifically acceptable method" to "any manner that will ensure
no exposure of human beings or the environment to any
concentration of PCBs."
The "PCB Transformer Fires Rule" was published on July 17, 1985
(50 FR 29170). This final rule amended portions of the August
25, 1982 electrical equipment rule by placing additional
restrictions and conditions on the use of PCB Transformers
(electrical transformers containing 500 ppm or greater PCBs).
This rule prohibited the use of higher secondary voltage (480
volts and above) network PCB Transformers in or near commercial
buildings after October 1, 1990. By October 1, 1990, it required
the installation of enhanced electrical protection on lower
secondary voltage network PCB Transformers and radial PCB
Transformers in use in or near commercial buildings. It
prohibited further installation of PCB Transformers in or near
commercial buildings after October 1, 1985 and required the
registration by December 1, 1985 of all PCB Transformers with
fire response personnel and building owners. Further, the ruling
required, by December 1, 1985, the marking of the exterior of all
PCB Transformer locations and the removal of all stored
combustibles located near PCB Transformers.
This rule also required owners of PCB Transformers involved in
fire-related incidents to immediately notify the National
Response Center and to take measures as soon as possible to
contain any potential releases of PCBs or incomplete combustion
products to water.
A clarification of the July 17, 1985 rule was published on
December 31, 1986 (51 FR 47241). It addressed the following
areas of the regulation:
the PCB Transformer registration requirement,
the requirement for the removal of stored combustibles,
the requirement to notify the National Response Center
of fire-related incidents,
the definition of commercial building,
the status of mineral oil transformers found to have
over 500 ppm PCBs,
the ban on the installation of PCB Transformers in or
near commercial buildings,
the requirement for labelling of exterior access to PCB
Transformer locations.
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The PCB Spill Cleanup Policy was published on April 2, 1987 (52
FR 10688) . The Policy establishes methods of cleanup and cleanup
levels of spills containing PCBs at concentrations of 50 ppm or
greater. EPA uses the Policy standards to determine the adequacy
of cleanup for penalty purposes. It specifies cleanup of PCBs to
different levels depending on the spill location, the potential
for exposure to residual PCBs remaining after the cleanup, the
concentration of the PCBs initially spilled and the nature and
size of the population potentially at risk of exposure. The
Policy imposes the most stringent requirements on areas where
there is the greatest potential for human exposure to spilled
PCBs; less stringent requirements where the type and degree of
contact present lower potential exposure; and even less stringent
requirements where there is little potential for any direct human
exposure.
While the Policy applies to the majority of spill situations, it
does provide for exceptional situations that may require
additional cleanup or less stringent standards at the discretion
of the EPA regional office.
On June 27, 1988, EPA published final amendments to the
"Uncontrolled PCBs Rule" (Federal Register July 10, 1984) which
excluded additional materials containing less than 50 ppm PCBs
from regulation (53 FR 24206). The amendments did the following:
1) eliminated the requirement that maintenance workers wear
VitonR elastomer gloves when servicing heat transfer and
hydraulic systems; 2) allowed the use of and distribution in
commerce of certain equipment and materials that have been
adequately decontaminated in accordance with the applicable PCB
spill cleanup policies in effect at the time of the cleanup;
3) maintained the 3 parts per billion (ppb) water discharge limit
from paper processing mills or allowed an equivalent mass-based
limitation for water discharges to be met; 4) prohibited the
burning for fuel of oil containing 2 to 49 ppm PCBs in
nonindustrial boilers and furnaces; and 5) excluded from the ban
on processing, distribution in commerce, and use certain products
containing less than 50 ppm PCBs. Remaining prohibitions on PCBs
less than 50 ppm are as a dust control agent, sealant, coating,
inert ingredient in pesticides or herbicides, road oiling agent,
use as a rust preventative, and use as a fuel in nonindustrial
boilers and furnaces. Readers should consult with their State
Department of Environmental Quality or equivalent to determine if
there are any additional regulations the State may have for PCBs
less than 50 ppm. A document titled "Summary of State PCB
Management Programs" is available through the TSCA Assistance
Information Service (202-554-1404).
On July 19, 1988, EPA published amendments (53 FR 27322) to the
"PCB Transformer Fires Rule" (Federal Register July 17, 1985).
The amendments include: 1) modifying the enhanced electrical
protection provision for nonsidewalk lower secondary voltage
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network PCS Transformers; 2) prohibiting the use, as of October
1, 1993, of all lower secondary voltage network PCB Transformers
located in sidewalk vaults; 3) allowing the installation of PCB
Transformers in or near a commercial building only for
reclassification or emergency purposes; 4) allowing the use under
certain limited conditions of an alternate label (other than ML)
on the exterior of PCB Transformer locations; and 5) setting up a
schedule of compliance for mineral oil transformers thought to be
PCB contaminated (i.e., 50-499 ppm) and later determined to be a
PCB Transformer (i.e., a 500 ppm).
The 1985 PCB Transformer Fires Rule regulated the use of
transformers in an attempt to reduce fire-related risks posed by
the use of these transformers. After publication of the August
21, 1987 proposed amendment to the PCB Transformer Fires Rule, ,
EPA received comments indicating that complete deenergization of
the transformer would not be necessary to prevent transformer
rupture. The comment stated that deenergization of the faulted
phase (partial deenergization) would be sufficient to prevent
transformer rupture. After further review, EPA determined that
partial deenergization may be acceptable electrical protection
for low voltage radial PCB transformers under some circumstances.
By final rule dated November 26, 1990 (55 FR 49043) EPA amended
the regulations concerning enhanced electrical protection
requirements for low voltage radial transformers containing PCBs
and extended the deadline for compliance for these types of
transformers to February 25, 1991. This rule did not alter any
other enhanced electrical protection requirements. It provided
that partial deenergization, i.e., deenergizing only the faulted
phase(s) in a low voltage radial transformer, may, in some
circumstances, be equivalent to total deenergization of such
transformers in the event of a high current fault. This rule
states that partial deenergization will be equivalent to total
deenergization only if the transformer configuration and
associated safety factors demonstrate that partial deenergization
is consistent with EPA's goals of avoiding fault related
failures, tank rupture, and fires in PCB Transformers. Owners
and operators of low voltage radial transformers in or near
commercial buildings who wish to utilize partial deenergization
are required to install this type of electrical protection using
good engineering practices.
There had been increasing concern on the part of Congressional
oversight committees about certain aspects of EPA's disposal
program for polychlorinated biphenyl (PCB) wastes. In
particular, the most frequently cited concerns were: (1) the
lack of an effective tracking system that would track PCB wastes
in a "cradle-to-grave" fashion; and (2) the lack of sufficient
oversight of the activities and qualifications of the PCB waste
brokers and other intermediate storers who may store the PCB
wastes owned by others.
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The PCB Notification and Manifesting rule published on December
21, 1989 (54 FR 52716) adds to the TSCA disposal regulations a
PCB waste tracking system based on the RCRA model for the
tracking of hazardous wastes. At the heart of the tracking
system are the requirements that PCB waste handlers (disposers,
commercial storers, transporters, and generators with PCB storage
areas) notify EPA of their PCB waste activities, and use the RCRA
Uniform Manifest in connection with their shipments of regulated
PCB wastes.
Second, this rule adds to the existing PCB storage facility
standards a requirement that certain commercial storers of PCB
wastes obtain written approvals from the EPA Regional
Administrators. The issuance of these commercial storer
approvals is conditioned on an evaluation of the applicant's
qualifications to engage in the business of PCB waste storage,
and the submission of closure plans and proof of financial
responsibility for proper closure of PCB storage areas.
In addition, the rule includes additional recordkeeping and
reporting requirements that will complete the PCB waste tracking
function, as well as facilitate EPA's enforcement of the PCB
disposal regulations.
On November 2, 1990 (55 FR 46470) EPA proposed a rule which
addresses the method by which permits issued under 40 CFR Part
761 are to be revoked or suspended. The criteria and procedures
for suspensions and revocations, proposed in the PCB Permit
Revocation Rule, will apply to those approvals required by the
1989 Notification and Manifesting rule, as well as to the
disposal approvals which are currently required by the
regulations. At the time of publication of this document, the
Permit Revocation rule had not been published in final form.
- PCBs IN THE WORKPLACE -
There are Occupational Safety and Health Administration (OSHA)
regulations governing PCBs in the workplace. OSHA has in place
two 8-hour time-weighted averages (TWAs) for chlorodiphenyl. For
chlorodiphenyl containing 42 percent chlorine, the TWA is 1.0
mg/m3 of workplace air. For chlorodiphenyl containing 54 percent
chlorine, the TWA is 0.5 mg/m3 of workplace air. An employee's
exposure to PCBs in any 8-hour workshift of a 40-hour week cannot
exceed these concentrations. Further, employers are required to
ensure a safe workplace under OSHA regulations. If specific
standards are not applicable, this general requirement for a safe
workplace would apply.
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The National Institute for Occupational Safety and Health (NIOSH)
recommends a more stringent air standard for worker exposure of
1. 0 /xg/m3 .
EPA's rules do not directly regulate workers, but the rules do
restrict or prohibit certain PCB activities and reduce the amount
of PCBs in the workplace. Therefore, as a result of EPA's PCB
rules the number of workers exposed to PCBs has been dramatically
reduced. EPA rules prohibit PCB Transformer rebuilding (except
for railroad transformers) that involves removal of the
transformer's coil. Prohibitions have terminated activities that
could result in the major long-term occupational exposure to high
concentrations of PCBs. However, worker exposure can still occur
as a result of PCB spills and authorized servicing operations for
PCB Transformers.
PROTECTIVE CLOTHING
The type of protective clothing that should be worn when working
with PCBs depends on the individual circumstances. Protective
clothing and equipment for workers is intended to prevent skin
and eye contact and to control respiratory exposure.
In any operation where workers may come into contact with PCBs,
protective clothing impervious to PCBs should be worn. Gloves,
boots, overshoes, and bib-type aprons that cover boot tops should
be provided, when necessary.
Nonporous gloves and boots and heavy overalls can usually protect
the skin. For major spill cleanup activities, a full suit of
nonporous clothing may be appropriate. Also, nonporous aprons
can be effective in reducing contamination of worker clothing.
The following tables rate comparable materials used to protect
against dermal exposure to PCBs.
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COMPARATIVE TABLES ON MATERIALS USED
TO PROTECT AGAINST DERMAL EXPOSURE TO PCBs
*Table 1. Recommendations for Protection Against Aroclor
1254 Undiluted and Paraffin Oil
Highly Recommended Recommended Not Recommended
Viton Teflon*3'c Surgical rubber
Viton SF Polyvinyl alcohol Polyethylene
Vitrile Nitrileb
Neoprene
Saranex*3
Butylb
*Table 2. Recommendations for Protection Against Aroclor
1254 in Trichlorobenzene: a 58 percent Arochlor
1254a
Highly Recommended Recommended Not Recommended
Vitrol Teflon Saranex
Viton SF Nitrile Butyl
Polyvinyl alcohol Neoprene
Vitrile Polyethylene
Surgical rubber
a- "Highly Recommended" materials showed no breakthrough
in 24 hours. Breakthrough time was 8 to 24 hours for
the "Recommended" category. Breakthrough time was less
than 8 hours for the "Not Recommended" category. These
recommendations assume comparable thickness, thus are
based on normalized breakthrough times.
"• Investigators noticed what appeared to be defects in
both Butyl and Saranex-laminated tyvek and nitrile; in
one Teflon thumb, penetration appeared to occur through
a seam.
c• Teflon is not highly recommended because when it is
flexed, as it would be when worn, permeation sometimes
takes place due to physical defects which flexing
produces.
*From the EPA/OTS TSCA Public Files; Versar, Inc. OPTS 62017
PCBs Controlled Wastes Communication N 23 File.
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*BREAKTHROUGH TIMES FOR VARIOUS PROTECTIVE GARMENT
MATERIALS EXPOSED TO PCBs
TYPE OF MATERIAL THICKNESS (mils) TIME (min)
Homogeneous. nonbonded
Butyl rubber 22 2.5
Neoprene rubber latex 23 0.5
Nitrile rubber latex 8 1.0
Nitrile rubber milled 12 0.8
Polyethylene, medium density 2 0.6
Poly(vinyl alcohol),
unsupported 15 0.3
Surgical rubber latex 8 #
Teflon, crumpled 2 #
Teflon, noncrumpled 2 60.0
Viton elastomer 10 0.3
Coated, bonded**
Butyl-coated nylon*** 15 3
Polyethylene-coated
Tyvek 5
Tyvek toward H20
Polyethylene toward H2O
Polyethylene-coated nylon 4 0.5
Poly(vinyl chloride)-coated
nylon 10 0.5
* From the EPA/OTS TSCA Public Files; Versar Inc. OPTS
62017 PCB Controlled Wastes File. Weeks and McLeod
1980.
** These are also referred to as composite or multilayered
materials.
*** Mil C-12189
# Testing was not performed.
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EYE PROTECTION/RESPIRATORY EXPOSURE CONTROL
Eye protection (chemical safety goggles, face shields with
goggles or safety glasses with side shields) should be worn
during any operation in which PCBs are present. If liquid
or solid PCBs contact the eyes, they should be irrigated
immediately with large quantities of water and then a
physician or other responsible medical personnel should
examine them.
Respiratory exposure control (whether individual protection
or workplace control) is most relevant for long-term
production operations or major spills, when concentrations
of airborne PCBs may exceed the recommended occupational
exposure limit. PCB Transformer spills can pose respiratory
problems when solvents, such as trichlorobenzene, are mixed
with PCBs. Small spills, such as capacitor failures, seldom
pose respiratory problems, but protection should be provided
for incidents in confined areas. The following chart
outlines the National Institute for Occupational Safety and
Health (NIOSH) recommendations for respiratory protection
from PCBs. EPA also recommends the use of dust masks
(surgical type) for use during soil cleanup.
*Respirator Selection Guide
Concentration of PCBs
Respiratory Type Approved
Under Provisions of 30 CFR 11
Greater than 1.0 cubic m
or Emergency (entry into
areas of unknown
concentration)
(1) Self-contained breathing
apparatus with full
facepiece operated in
pressure-demand or
other positive
pressure mode.
(2) Combination Type C
supplied air respirator
with full facepiece
operated in pressure-
demand or other positive
pressure mode and an
auxiliary self-contained
breathing apparatus
operated in pressure demand
or other positive pressure
mode.
*Source: NIOSH Recommendation USDHEW 1977
Xlll
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REGIONAL PCB BRANCH OFFICES
USEPA Region I (ME, NH, VT, MA, RI, CT)
Pesticides and Toxic
Substances Branch (ATC)
John F. Kennedy Federal Bldg.
Boston, MA 02203
(617-565-3257)
USEPA Region II (NY, NJ, PR, VI)
Pesticides and Toxic
Substances Branch (MS-105)
2890 Woodbridge Ave.
Edison, NJ 08837
(908-906-6817)
USEPA Region III (PA, DE, MD, VA, WV, DC)
Toxics and Pesticides Branch
841 Chestnut Bldg.
Philadelphia, PA 19107
(215-597-7668)
USEPA Region IV (KY, TN, NC, SC, GA, AL, MS, FL)
Pesticides and Toxic
Substances Branch
345 Courtland St. N.E.
Atlanta, GA 30365
(404-347-1033)
USEPA Region V (OH, IN, IL, MN, WI, MI)
Pesticides and Toxic
Substances Branch (SP-14J)
77 West Jackson Blvd.
Chicago, IL 60604
(312-886-7061)
xiv
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USEPA Region VI (AR, LA, OK, TX, MM)
Pesticides and Toxic
Substances Branch (6T-PT)
1445 Ross Avenue
Suite 1200
Dallas, TX 75202-2733
(214-655-7290)
USEPA Region VII (IA, KS, MO, NE)
Toxics and Pesticides Branch (TOPE)
726 Minnesota Avenue
Kansas City, KS 66101
(913-551-7394)
USEPA Region VIII (ND, SD, MT, WY, UT, CO)
Pesticides and Toxic
Substances Branch
One Denver Place
Suite 500
999 18th Street
Denver, CO 80202-2466
(303-293-1686)
USEPA Region IX (CA, NV, AZ, HI, Guam)
Pesticides and Toxic
Substances Branch (A-4-4)
75 Hawthorne St.
San Francisco, CA 94105
(415-744-1094)
USEPA Region X (WA, OR, ID, AK)
Pesticides and Toxic
Substances Branch (AT-083)
1200 6th Avenue
Seattle, WA 98101
(206-553-7369)
xv
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CHAPTER I
PART A
TRANSFORMERS
(NONRAILROAD)
Manufacturing (page 1-3)
Processing (page 1-4)
Distribution in Commerce (Sale of Transformers) (page 1-4)
Exemptions to Manufacture, Process, and Distribute
PCBs in Commerce (page 1-6)
Marking/Labeling (page 1-6)
Phaseout Requirements (page 1-7)
Use Conditions (page I-10)
(1) PCB Transformer Emergency Installations (page 1-10)
(2) PCB Transformer Reclassification Installations
(page I-11)
(3) Electrical Protection Requirements (page 1-12)
(4) Registration Requirements (page 1-13)
(5) Combustible Materials (page 1-15)
(6) Inspections (page 1-16)
(7) Leaking PCB Transformers (page 1-17)
(8) Fire-Related Incidents (page 1-17)
(9) Discovery of a Mineral Oil PCB Transformer (page I-18)
Servicing and Reclassification Conditions (page 1-20)
Storage for Reuse (page 1-22)
Storage for Disposal (page 1-22)
Disposal (page 1-23)
Recordkeeping (page 1-25)
Spills (page 1-26)
-------
PART A
- TRANSFORMERS -
Transformers are used to raise and lower voltage. As
voltage is transmitted from a generating facility through
transmission and distribution systems, it may be raised or
lowered a number of times depending on the technical
configuration of the system and the varying voltage
requirements of the customer.
A large transformer may be several times the size of an
automobile and contain hundreds or even thousands of gallons
of oil or other dielectric fluid. Such transformers are
typically located in generating facilities or substations.
However, the vast majority of transformers are considerably
smaller.
Between the extremely large transformers used to transmit
power and the extremely small overhead transformers used to
bring power into homes, there are numerous transformers of
assorted size and voltage ratings used to adjust voltage to
the requirements of all types of commercial and industrial
customers. Prior to EPA's regulations of PCBs, when these
transformers were located indoors, fire codes often
encouraged the use of PCBs as an insulating fluid.
Today, for purposes of regulation, EPA classifies
transformers into three basic categories - "PCB," "PCB-
Contaminated," and "Non-PCB." A "PCB Transformer" is one
which contains 500 parts per million (ppm) or greater PCBs.
A "PCB-Contaminated Transformer" is one which contains 50-
499 ppm PCBs. And finally, a "Non-PCB Transformer" contains
less than 50 ppm PCBs.
EPA also categorizes transformers by their type, location,
and secondary voltage. As these various categories of
transformers are regulated to different degrees, it is
important to know the type of transformer in question.
Ql: Do transformers have to be tested to determine their PCB
concentration? If not, how can I determine the equipment's
classification?
Al: The regulations do not require that these types of equipment
be tested to determine the PCB concentration in their fluid.
However, in the absence of a test, certain assumptions must
be made about the equipment. For example, if the nameplate
indicates that the equipment contains PCB dielectric fluid
(see table of trade names on p.i), or, if there is any
reason to believe that the equipment at one time contained
PCB dielectric fluid, or, if there is no nameplate on the
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equipment or other information to indicate the type of
dielectric fluid, then the equipment must be assumed to be a
PCB Transformer (500 ppm or greater). Transformers which
are known to contain mineral oil dielectric fluid and whose
PCB concentration is unknown, must be assumed to be PCB-
Contaminated Electrical Equipment (50-499 ppm) and must be
treated as such. However, if the PCB concentration has ever
been known or if a person has reason to know the
concentration equalled or exceeded 500 ppm PCBs, the
transformer must be treated as a PCB Transformer. These
"assumption rules" effectively apply to all regulatory
requirements relating to the equipment including: use and
servicing, leaks and spills, sale for reuse, storage for
disposal, and disposal.
Q2: Can screening tests, such as Clor-n-Oil™, be used to
determine the PCB concentration of a transformer? If so,
can "Certified Non-PCB" labels be used to classify
transformers based upon a screen test?
A2: Currently, the regulations do not require that any
particular testing method be utilized when determining the
PCB concentration in transformers. However, because EPA
does not recognize the results of such field concentration
screening tests for purposes of classifying transformers,
transformer owners should prudently scrutinize PCB testing
options, as there are significant differences in the
integrity and accuracy of various testing methods. It
should be noted that, in most situations, EPA will utilize
laboratory gas-chromatography (GC) testing to determine PCB
concentrations during facility inspections. EPA recommends
that owners of electrical equipment choose testing methods,
and practice sampling procedures, which are analytically
accurate, reproducible, assure quality control, and are
certifiable.
The use of non-PCB labels is unregulated by EPA. That is to
say, there are no prohibitions or requirements to place non-
PCB labels on transformers. However, if non-PCB labels are
used to indicate the classification of equipment, then
owners should be able to provide documentation such as test
results or manufacturer's letters along with historic
service records which will substantiate the non-PCB
classification. A criminal action could be pursued for
someone intentionally using non-PCB labels on known or
assumed PCB Items.
Q3: Can I batch test oil samples from several transformers and
classify each unit based upon one test result?
A3: The only place in the regulations where "batch testing" is
allowed is under testing procedures for disposal of PCBs
[761.60(g) ]. It is only owners or users of mineral oil
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dielectric fluid electrical equipment who may take advantage
of the batch testing provision. However, batch testing to
classify equipment for continued use of PCBs is also
allowable provided that known or assumed dilution does not
take place. That is, mineral oil that is assumed or known to
contain 50 ppm or greater PCBs must not be mixed with
mineral oil that is known or assumed to contain less than 50
ppm PCBs to reduce the concentration of PCBs in the batch.
While there is no requirement to individually test mineral
oil transformers, if test results of the drained carcass(es)
show a concentration of greater than 500 ppm PCBs,
that/those transformer(s) tested as a batch must be treated
as a PCB (>500 ppm) and the batch tested oil must be treated
as containing greater than 500 ppm PCBs for purposes of
disposal.
Q4: Many pole-mounted distribution transformers have no
information on their nameplate indicating that they do, in
fact, contain mineral oil dielectric fluid. Without this
nameplate information, am I required to assume that these
units are "PCB" classification (500 ppm or greater)?
A4: The regulations allow "oil-filled" electrical equipment
whose PCB concentration is unknown to be assumed less than
500 ppm (PCB-Contaminated, 50-499 ppm). EPA has received
numerous comments from the electric utility industry and
others indicating that significant numbers of pole-mounted
utility distribution transformers have no nameplate
information stating the type of "oil" in the unit. In the
absence of this direct indication, the owner may still make
the assumption of "PCB-Contaminated" if the purchase record,
or manufacturer's literature or other specific
documentation, identifies the transformer as oil-filled, or
if manufacturer's nameplate codes correlate with oil-filled
status. However, in the absence of direct nameplate
information or secondary documentation, any such transformer
must be considered as "PCB" unless tested and proved
otherwise.
MANUFACTURING
The manufacture of PCBs, regardless of concentration, for
any use including transformers is prohibited without an EPA
exemption [TSCA section 6(e) and 761.20(b)].
Q5: Most of the transformers our facility purchases today
indicate "Non-PCB" on the equipment's nameplate. Does this
mean that companies can still manufacture transformers with
15, 20, or even 30 ppm PCBs in the oil?
A5: No. The manufacture of transformers containing any PCBs 2
ppm or greater is prohibited.
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PROCESSING
The processing of PCBs, 50 ppm or greater, for use in
transformers is prohibited without an EPA exemption
[761.20 (c)]. However, PCBs at concentrations less than 50
ppm may be processed for use in transformers (under specific
conditions) in accordance with the definition of "Excluded
PCB Products" [see 761.3 for specific examples]. Also, PCBs
at any concentration may be processed (i.e., prepared and/or
packaged for distribution in commerce) for purposes of
disposal in accordance with the requirements of 761.60
[761.20(c) (2)] .
DISTRIBUTION IN COMMERCE (Sale of Transformers)
The distribution in commerce of PCBs, 50 ppm or greater, for
use in transformers is prohibited without an EPA exemption
[761.20(c)]. However, PCBs at concentrations less than 50
ppm may be distributed in commerce' for use in transformers
(under specific conditions) in accordance with the
definition of "Excluded PCB Products" [761.3] . Also, PCBs
at any concentration may be distributed in commerce for
purposes of disposal in accordance with the requirements of
761.60 [761.20 (c) (2)]. Disposal, in this context, means the
termination of the useful life of the PCB or PCB-
Contaminated Transformer.
The distribution in commerce (sale) of transformers which
contain PCBs in concentrations of 50 ppm or greater (known
or assumed) for purposes of reuse is allowed provided:
• the transformer was originally sold for use before
July 1, 1979;
• the transformer is intact and nonleaking at the
time of sale; and
• no PCBs are introduced into the transformer.
Q6: Does this mean that I can sell a PCB or PCB-Contaminated
Transformer?
A6: Yes. If the transformer was originally sold for use before
July 1, 1979, and is now being sold for reuse (i.e.,
continued use). Also, the transformer must be totally
enclosed, intact and nonleaking. EPA recommends that the
buyer be advised that he is purchasing a PCB or PCB-
Contaminated Transformer.
Q7: What does intact and nonleaking mean?
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A7: Intact and nonleaking means that the transformer is
structurally sound with all fluid intact and there are no
PCBs on the external surface of the transformer.
Q8: Can I sell drained PCB-Contaminated Transformer carcasses
{known or assumed 50-499 ppm) to a rebuilder for reuse as
parts in repair and remanufacturing activities?
A8: No. Selling drained 50-499 ppm carcasses for reuse is an
unauthorized distribution in commerce of PCBs and is
prohibited without an EPA exemption. On the other hand,
non-PCB carcasses (less than 50 ppm) can be sold for reuse
(under specific conditions) in accordance with the
definition of "Excluded PCB Products" [761.3].
Q9: Can I sell drained PCB-Contaminated Transformer carcasses
(known or assumed 50-499 ppm) to a scrap or salvage dealer
for metals recovery?
A9: Yes. The sale of drained 50-499 ppm carcasses for scrapping
or salvaging is generally considered distribution in
commerce for purposes of disposal and is allowed with
certain limitations. To qualify as disposal, the scrapping
practice must be one which will "...terminate the useful
life of PCBs or PCB Items" [761.3]; or, in other words, will
destroy any residual PCBs found in the drained carcasses.
Salvaging aimed at reclamation of the metals found in the
case and coil generally constitutes disposal, because any
residual PCBs are destroyed by the high temperatures
employed in the smelting process. However, where salvaging
merely consists of disassembling the drained equipment to
obtain parts for reuse in other equipment, the useful life
of the equipment has not been fully terminated and thus is
not considered disposal. In sum, the scrapping/salvaging of
50-499 ppm drained equipment is unregulated to the extent
that: (1) the carcass has been drained of all free-flowing
liquid, (2) scrapping practices do not result in leaks,
spills, or other uncontrolled discharges of PCBs, and (3)
any PCB-contaminated components are not reintroduced into
commerce.
Q10: Can I export drained PCB-Contaminated Transformers for
recovery of metal?
A10: No. PCB-Contaminated Transformers may not be exported for
recovery of metal since this is considered disposal unless
they have been reclassified to non-PCB status, i.e., to <50
ppm. Section 761.20 (c) permits distribution in commerce for
purposes of disposal, although this exception refers to
domestic disposal only. PCB-Contaminated Transformers may
be reclassified to the non-PCB status and then exported for
purposes of disposal if the transformer meets the definition
of "Excluded PCB Products". (See Chapter X for further
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explanation of this definition.) The process of
reclassification is discussed below under "Servicing and
Reclassification Conditions."
EXEMPTIONS TO MANUFACTURE. PROCESS. AND DISTRIBUTE PCBs IN
COMMERCE
Exemptions to manufacture, process, and distribute in
commerce PCBs may be granted only by rulemaking on a case-
by-case basis. The EPA Administrator may set terms and
conditions for an exemption and may grant an exemption for
not more than one year. EPA interim procedural rules for
processing and distribution in commerce exemptions describe
the required content of processing and distribution in
commerce exemptions petitions and the procedures EPA follows
in rulemaking on exemption petitions. Those rules were
published in the Federal Register of May 31, 1979 (44 FR
31558) and are codified at 40 CFR 750.30 through 750.41.
MARKING/LABELING
All PCB Transformers must be marked in accordance with EPA
marking and labeling requirements [761.40]. All
marks/labels must comply with EPA marking formats which
specify size, color, and design [761.45].
• All PCB Transformers (500 ppm or greater) must be
marked individually with the mark ML (PCB label)
[761.40(a)(2) and (c)(1)].
• The marking of PCB-Contaminated Transformers (50-
499 ppm) is not required [761.40(a)(2)]. If an
owner chooses to mark a PCB-Contaminated
Transformer, it is recommended that the PCB mark
ML not be used.
• Transport vehicles loaded with one or more PCB
Transformers (500 ppm or greater) must be marked
on each end and each side with the mark ML (PCB
• label) [761.40(b)].
• All marks/labels must be placed in a position on
the exterior of the transformer so that the mark
can be easily seen by persons inspecting the
transformer [761.40(h)].
PCB Transformer locations must also be marked/labeled in
accordance with 761.40(j).
• As of December 1, 1985, the vault door, machinery
room door, fence (including a chain-linked fence),
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hallway, or other means of access (other than
grates and manhole covers) to a PCB Transformer
must be marked with the mark ML (PCB label)
[761.40(j) (1)] .
A mark other than the mark ML may be used to identify a PCB
Transformer in certain circumstances/locations, provided all
of the following conditions are met:
• The program using such an alternative mark was
initiated prior to August 15, 1985, and can be
substantiated with documentation
[761.40(j) (2) (i)] .
• Prior to August 15, 1985, coordination between the
transformer owner and the primary fire department
occurred, and the primary fire department knows,
accepts, and recognizes what the alternative mark
means, and that this can be substantiated with
documentation [761.40 (j) (2) (ii)] .
• The EPA Regional Administrator in the appropriate
region was informed in writing of the use of the
alternative mark by October 3, 1988 and was
provided with documentation that the program began
before August 15, 1985, and documentation that
demonstrates that prior to that date the primary
fire department knew, accepted, and recognized the
meaning of the mark, and included this information
in the firefighting training [761.40(j)(2)(iii)].
• The Regional Administrator approved in writing the
use of an alternative mark within 30 days of
receipt of the documentation of a program
[761.40(j) (2) (iv)] .
PHASEOUT REQUIREMENTS
• After October 1, 1985, the use and storage for
reuse of PCB Transformers (500 ppm or greater)
that pose an exposure risk to food or feed is
prohibited [761.30(a)(1)]. It is the owner's
responsibility to determine whether a PCB
Transformer poses an exposure risk to food or
feed.
• After October 1, 1985, the installation of PCB
Transformers in or near commercial buildings is
prohibited. However, as of September 1, 1988, PCB
Transformers may be installed in or near
commercial buildings in an "Emergency Situation"
or "For Purposes of Reclassification" in
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accordance with 761.30(a)(1)(iii)(B) and (C) and
(D) .
In or near a commercial building means inside, on,
or within 30 meters of a nonindustrial, non-
substation building. Commercial buildings are
accessible to the public as well as employees.
Examples include schools, hospitals, office
buildings, stores, apartment buildings, churches,
and transportation terminals and stations.
Emergency installations, in or near a commercial
building, was permitted until October 1, 1990.
However, the use of any PCB Transformer installed
on such an emergency basis is permitted only for
one year from the date of installation or until
October 1, 1990, whichever is earlier
[761.30(a) (1) (iii) (B) (2)] .
Also, installation of a retrofilled PCB
Transformer, in or near a commercial building, was
permitted for reclassification purposes until
October 1, 1990. However, the use of a
retrofilled PCB Transformer installed for
reclassification purposes is limited to 18 months
after installation or until October 1, 1990,
whichever is earlier [761.30(a)(1)(iii)(C)(2)(i)].
(Note: Retrofilled mineral oil PCB Transformers
may be installed in or near a commercial building
for reclassification purposes indefinitely after
October 1, 1990.)
Also, as of October 1, 1990, the use of network
PCB Transformers with higher secondary voltages
(480 volts or greater, including 480/277 volt
systems) in or near commercial buildings is
prohibited. In addition, network PCB Transformers
with higher secondary voltages which are removed
from service in accordance with this requirement
must either be retrofilled and reclassified or
placed into storage for disposal or disposed of
[761.30(a) (1) (ii)] .
Lower secondary voltage (below 480 volts) network
PCB Transformers (not located in sidewalk vaults)
may be used in or near commercial buildings beyond
October 1, 1990 provided: (1) they are equipped
with electrical protection as specified under
761.30(a)(1)(iv)(A) by October 1, 1990 (see
Electrical Protection Requirements); or (2) in
lieu of electrical protection, the transformers
must be registered in writing with the appropriate
EPA Regional Administrator by October 1, 1990.
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(See Registration Requirements on page 1-14.)
Subsequently, those PCS Transformers which the
owner chooses to "register" versus equip with
electrical protection must be removed from service
by October 1, 1993 [761.30(a)(1)(iv)(B)].
• As of October 1, 1990, all higher secondary
voltage radial PCB Transformers, in use in or near
commercial buildings, that have .not been removed
from service, must be equipped with electrical
protection to avoid transformer ruptures caused by
high current faults [761.30 (a) (1(iv)] .
• As of February 25, 1991 all lower secondary
voltage radial PCB Transformers, located in or
near commercial buildings, that have not been
removed from service, must be equipped with
electrical protection to detect sustained high
current faults and provide for the complete
deenergization of the transformer or the faulted
phase of the transformer [761.30(a)(1)(iv)(E)].
• Finally, as of October 1, 1993, all lower
secondary voltage (below 480 volts) network PCB
Transformers located in sidewalk vaults in or near
commercial buildings must be removed from service
[761.30(a)(I) (iv)(D)].
Qll: Should a person consider catastrophic failure, such as
ruptures, explosions, or fire when trying to determine
whether a PCB Transformer poses an exposure risk to food or
feed?
All: One must consider the location of a specific PCB Transformer
in relation to food or feed products, and all other
available information. If there is a reasonable possibility
of contact between PCBs and food or feed, the transformer
must be considered a risk. In evaluating the exposure risk,
it is useful to consider a hypothetical situation in which
PCBs are discharged in any way from the transformer, such as
through a. rupture or a leak. The question to be asked is
whether contact between food or feed and PCBs is reasonably
possible. PCB Items that are located adjacent to or above
food or feed products pose an exposure risk, unless there is
secondary containment or another physical structure that
prevents discharges from contaminating the food or feed.
For purposes of determining if a transformer poses exposure
risks to food or feed, it is not necessary to consider rare
events. The standard to be applied is a reasonable
possibility of contamination of food or feed by PCBs.
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Q12: The phaseout requirements indicate that certain types of PCB
Transformers must be removed from service by a specific
date. Can a PCB Transformer be retrofilled and reclassified
to meet this phaseout requirement?
A12: Yes. A PCB Transformer that has been retrofilled and
reclassified to PCB-contaminated or non-PCB status in
accordance with the PCB regulations meets the requirement
for phaseout of a PCB Transformer. However, for practical
purposes, PCB Transformer owners must allow sufficient time
for proper reclassification to reach at least the PCB-
contaminated status by the phaseout date.
USE CONDITIONS
PCB and PCB-Contaminated Transformers (other than in
railroad locomotives and self-propelled railroad cars) may
be used for the remainder of their useful lives subject to
the following conditions:
1) PCB Transformer EMERGENCY INSTALLATIONS: Installation of
a PCB Transformer in or near a commercial building was
permitted when done in accordance with the definition of
"Emergency Situation" [761.3] including:
• Those who install PCB Transformers in or near a
commercial building in an emergency situation must
maintain documentation to support the reason for
the emergency installation. This documentation
must be completed within 30 days after
installation of the PCB Transformer and maintained
at the owner's facility [761.30(a) (1) (iii) (B) (1) .
The documentation must include: the type of
transformer that requires replacement, the type of
transformer that must be used for replacement, the
date of the transformer failure, the date of
subsequent replacement, the type of transformer
installed as a replacement, and a statement
describing actions taken to locate a non-PCB or
PCB-Contaminated Transformer replacement
[761.30(a) (1) (iii) (B) (1) (i) through (vi)] .
• Such emergency installation was permitted until
October 1, 1990, and the use of any PCB
Transformer installed on such an emergency basis
is permitted for 1 year from the date of
installation or until October 1, 1990, whichever
was earlier [761.30(a)(1)(iii)(B)(2)].
• PCB Transformers installed for emergency purposes
may be subsequently reclassified; however, the
transformer must be effectively reclassified to a
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non-PCB or PCB-contaminated status within 1 year
after installation or by October 1, 1990,
whichever was earlier because the transformer was
initially installed in an emergency situation
[761.30(a) (1) (iii) (B) (3)] .
NOTE: Owners who installed PCB Transformers in
emergency situations between October 1, 1985 and
September 1, 1988 were required to notify the Regional
Administrator in writing by October 3, 1988 of such
installation.
2) PCB Transformer RECLASSIFICATION INSTALLATIONS:
Installation of a retrofilled PCB Transformer in or near a
commercial building for reclassification purposes is
permitted when it is done in accordance with the following:
• Those who install PCB Transformers in or near a
commercial building for reclassification purposes
must maintain on the owner's premises, completed
within 30 days of installation, the following
information: the date of installation, the type
of transformer installed, the PCB concentration
(if known) at the time of installation, and the
retrofill and reclassification schedule
[761.30(a)(1)(iii)(C)(1)3 .
The installation of retrofilled PCB Transformers in or near
commercial buildings for purposes of reclassification was
permitted only until October 1, 1990, with the following
exceptions:
The use of a retrofilled PCB Transformer (a PCB Transformer
that has been drained and refilled to lower its PCB
concentration) installed in or near a commercial building
for reclassification purposes was limited to 18 months after
installation or until October 1, 1990, whichever is earlier
[761.30(a) (1) (iii) (C) (2) (i)] .
• Retrofilled mineral oil PCB Transformers may be
installed in or near a commercial building for
reclassification purposes indefinitely after
October 1, 1990 [761.30 (a) (1) (iii) (C) (2) (ii)] . (A
retrofilled mineral oil PCB Transformer is a
mineral oil transformer that was required to be
assumed to contain between 50 and 499 ppm PCBs,
but was tested and found to contain 500 or more
ppm, and which was subsequently drained and
refilled to lower its PCB concentration.)
• Once a retrofilled transformer has been installed
in or near a commercial building for
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reclassification purposes, it must be tested 3
months after installation to ascertain the
concentration of PCBs. If the PCB concentration
is below 50 ppm, the transformer can be
reclassified as a non-PCB Transformer. If the PCB
concentration is between 50 and 500 ppm, the
transformer can be reclassified as a PCB-
Contaminated Transformer. If the PCB
concentration remains at 500 ppm or greater, the
entire process must be either repeated until the
transformer has been reclassified to a non-PCB or
PCB-Contaminated Transformer or the transformer
must be removed from service. The
reclassification process must be completed by
October 1, 1990 and adhere to the requirements of
761.30(a)(2)(v) or the transformer must be removed
from service [761.30(a) (L) (iii) (C) (2) (iii)] .
NOTE: Owners who installed PCB Transformers in or near
a commercial, building for reclassification purposes
between October 1, 1985 and September 1, 1988 were
required to notify the Regional Administrator in
writing by October 3, 1988 of such installation.
3) ELECTRICAL PROTECTION REQUIREMENTS: As of October 1,
1990, all higher secondary voltage radial PCB Transformers,
in use in or near commercial buildings, and lower secondary
voltage network PCB Transformers (below 480 volts) in or
near commercial buildings (not located in sidewalk vaults)
that have not been removed from service, must be equipped
with electrical protection to avoid transformer ruptures
caused by high current faults. As of February 25, 1991, all
lower secondary voltage radial PCB Transformers^ in use in
or near commercial buildings, must also be equipped with
electrical protection to avoid transformer ruptures caused
by high current faults [761.30(a)(1)(iv)]. The following
types of electrical protection devices are to be used:
• Current-limiting fuses or other equivalent
technology must be used to detect sustained high
current faults and provide for complete
deenergization of the transformer (within several
hundredths of a second in the case of higher
secondary voltage radidl PCB Transformers and
within tenths of a second in the case of lower
secondary voltage network PCB Transformers) before
transformer rupture occurs. The installation,
setting, and maintenance of current-limiting fuses
or other equivalent technology to avoid PCB
Transformer ruptures from sustained high current
faults must be completed in accordance with good
engineering practices [761.30(a)(1)(iv)(A)].
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• All lower secondary voltage network PCB
Transformers (below 480 volts) in or near
commercial buildings (not located in sidewalk
vaults) which have not been equipped with
electrical protection by October 1, 1990 (as
specified above) must either be removed from
service for disposal or reclassified in accordance
with 761.30(a)(2)(v) by October 1, 1993
[761.30(a)(1)(iv)(B)].
• As of February 25, 1991 all lower secondary
voltage radial PCB Transformers must be equipped
with electrical protection, such as current-
limiting fuses or other equivalent technology, to
detect sustained high current faults and provide
for the complete deenergization of the transformer
or complete deenergization of the faulted phase of
the transformer within several hundredths of a
second. The installation, setting, and
maintenance of such electrical protection must be
completed in accordance with good engineering
practices [761.30(a) (1) (iv) (E) ] .
• As of October 1, 1990, all higher secondary
voltage radial PCB Transformers (480 volts and
above, including 480/277 volt systems), in use in
or near commercial buildings, were required to be
equipped with protection to avoid transformer
ruptures caused by sustained low current faults
[761.30(3)(1)(v)].
Q13: What is the difference between a network and a radial
transformer?
A13: Network transformers are hooked up in parallel systems so
that if one transformer fails another transformer will pick
up the load. A radial transformer is hooked up in a single
line method, and if that transformer fails, the load is not
picked up by another transformer.
Q14: Why did EPA require phaseout without the option of enhanced
electrical protection of network PCB Transformers in or near
commercial buildings with high secondary voltages while
requiring electrical protection on radial transformers?
A14: EPA determined that network PCB Transformers with higher
secondary voltages are particularly likely to be involved in
serious fire-related incidents (i.e., those that involve
smoke spread into buildings). Therefore, EPA has placed
more stringent regulatory measures and controls on these
transformers.
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4) REGISTRATION REQUIREMENTS: As of December 1, 1985, all
PCB Transformers in use (including PCB Transformers in
storage for reuse) were required to be registered with fire
response personnel with primary jurisdiction (that is, the
fire department or fire brigade which would normally be
called upon for the initial response to a fire involving the
equipment) [761.30(a) (1) (vi)] . Information required to be
provided to fire response personnel includes:
• The location of the PCB Transformer(s) including:
the address(es) of the building(s) and the
physical location(s) of the PCB Transformer(s) on
the building site(s); and, for outdoor PCB
Transformers, the location of the outdoor
substation [761.30(a)(1)(vi)(A)].
• The principal constituent of the dielectric fluid
in the transformer(s) (e.g., Askarel PCBs, mineral
oil, or silicone oil) [761.30(a)(I) (vi)(B)].
• The name and telephone number of the person to
contact in the event of a fire involving the
equipment [761.30(a)(1)(vi)(C)].
Q15: Do PCB Transformers being stored for disposal have to be
registered with the Fire Department?
A15: No not under TSCA. The requirement to register transformers
with fire response personnel is specifically a "use
condition." PCB Transformers which have been removed from
service and are being stored for disposal do not require
registration. Those transformers in storage for reuse,
however, must be registered with fire response personnel.
As of December 1, 1985, PCB Transformers in use in or near
commercial buildings were required to be registered with
building owners. For PCB Transformers located in commercial
buildings, PCB Transformer owners were required to register
the transformers with the building owner of record. For PCB
Transformers located near commercial buildings, PCB
Transformer owners were required to register the
transformers with all owners of buildings located within 30
meters of the PCB Transformer(s) [761.30(a) (1) (vii)] .
Information required to be provided to building owners by
PCB Transformer owners includes but is not limited to:
• The specific location of the PCB Transformer(s)
[761.30(a)(1)(vii)(A)].
• The principal constituent of the dielectric fluid
in the transformer(s) (e.g., Askarel PCBs, mineral
oil, or silicone oil) [761.30(a) (1) (vii) (B)] .
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• The type of transformer installation (e.g., •
208/120 volt network, 280/120 volt radial, 208
volt radial, 480 volt network, 480/277 volt
network, 480 volt radial, 480/277 volt radial)
[761.30(a)(1)(vii)(C)].
As of October 1, 1990, owners of lower secondary voltage
network PCB Transformers in use in or near commercial
buildings but not located in sidewalk vaults, which have not
been equipped with electrical protection as specified under
761.30(a)(1)(iv)(A), must register in writing those
transformers with the EPA Regional Administrator in the
appropriate region [761.30 (a) (1) (iv) (C)] . The information
required to be provided in writing to the Regional
Administrator includes:
• The specific location of the PCB Transformer(s)
[761.30(a)(1)(iv)(C)(1)].
• The address(es) of the building(s) and the
physical location of the PCB Transformer(s) on the
building site(s) [761.30(a)(1)(iv)(C)(2)].
• The identification number(s) of the PCB
Transformer(s) [761.30(a)(1)(iv)(C)(3)].
This registration and disposal option is in lieu of
providing "electrical protection" as specified under
761.30 (a) (l)-(iv) (A) . Consequently, these lower secondary
voltage network PCB Transformers must be removed from
service by October 1, 1993 [761.30(a)(1)(iv)(B)].
5) COMBUSTIBLE MATERIALS: As of December 1, 1985,
combustible materials include, but are not limited to,
paints, solvents, plastics, paper, and sawn wood must not be
stored within a PCB Transformer enclosure (i.e., in a
transformer vault or in a partitioned area housing a
transformer); within 5 meters of a transformer enclosure,
or, if unenclosed (unpartitioned) , withi-n 5 meters of a PCB
Transformer [761.30 (a) (1) (viii)] .
Q16: Does the 5-meter distance requirement apply vertically as
well as laterally?
A16: EPA does not require the removal of stored combustibles
within a 5-meter vertical distance provided that there is a
continuous permanent ceiling overhead and/or., floor below.
However, if the floor, for example, is made of metal grates,
an electrical fault could still ignite combustibles below,
and consequently the 5-meter distance in this situation
would apply.
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Q17: Would items such as a wooden desk, wooden benches, and other
materials used in an office setting be considered stored
combustibles and have to be moved at least 5 meters from a
PCB Transformer?
A17: No. Since these materials are used on a day-to-day basis,
they would not be considered "stored combustibles" and
consequently are not required to be moved. Office equipment
stored as surplus would be considered stored combustibles.
Q18: If a PCB Transformer is surrounded by a chain-link fence, is
the transformer considered "enclosed" for purposes of the
stored combustibles requirement?
A18: No. A PCB Transformer surrounded by a chain-link fence is
not considered "enclosed" for the purpose of this
requirement, and therefore, combustible materials must not
be stored within 5 meters of the transformer. The reason
for this is that a chain-link fence would not provide a
barrier to prevent an electrical fault or a transformer fire
from potentially reaching nearby combustible materials. On
the other hand, a PCB Transformer surrounded by 2- to 3-hour
fire-resistant walls would be reasonably protected from
controllable or less severe fires.
Q19: Does the combustible materials requirement apply to a PCB
Transformer which has been placed into storage for disposal?
A19: No. The combustible materials requirement is specifically a
PCB Transformer "use condition." Combustible materials do
not have to be removed from close proximity to a PCB
Transformer which is being stored for disposal.
6) INSPECTIONS: A visual inspection of each PCB Transformer
(500 pptn or greater) in use or stored for reuse shall be
performed at least once every 3 months. These inspections
may take place any time during the 3 months: January-March,
April-June, July-September, and October-December as long as
there is a minimum of 30 days between inspections. The
visual inspection must include investigation for any leak or
dielectric fluid on or around the transformer. The extent
of the visual inspections will depend on the physical
constraints of each transformer installation and should not
require an electrical shutdown of the transformer being
inspected [761.30(a)(1)(ix)].
A reduced visual inspection frequency of at least once every
12 months applies to PCB Transformers that utilize either of
the following risk reduction measures. These inspections
may take place any time during the calendar year as long as
there is a minimum of 180 days between inspections
[761.30(a)(1)(xiii)]. PCB Transformers which may be
inspected annually versus quarterly include:
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• PCB Transformers which have impervious, undrained,
secondary containment capacity of at least 100
percent of the total dielectric fluid volume of
all transformers so contained
[761.30(a)(1)(xiii)(A)].
• PCB Transformers which have been tested and found
to contain less than 60,000 ppm -PCBs (after 3
months of in-service use if the transformer has
been serviced for purposes of reducing the PCB
concentration) [761.30(a)(1)(xiii)(B) ].
Records of inspection and maintenance history shall be
maintained at least 3 years after disposing of the
transformer and shall be made available for inspection, upon
request by EPA [761.30(a)(1)(xii)]. Such records shall
contain the following information for each PCB Transformer
[761.30(a)(1)(xii)(A) through (H)]:
• Its location.
• The date of each visual inspection and the date
that leak was discovered, if different from the
inspection date.
• The person performing the inspection.
• The location of any leak(s).
• An estimate of the amount of dielectric fluid
released from any leak.
• The date of any cleanup, containment, repair, or
replacement.
• A description of any cleanup, containment, or
repair performed.
• The results of any containment and daily
inspection required for uncorrected active leaks.
7) LEAKING PCB TRANSFORMERS: If a PCB Transformer is found
to have a leak which results in any quantity of PCBs running
off or about to run off the external surface of the
transformer, then the transformer must be repaired or
replaced to eliminate the source of the leak. In all cases,
any leaking material must be cleaned up and properly
disposed of according to disposal requirements of 761.60.
Cleanup of the released PCBs must be initiated as soon as
possible, but in no case later than 48 hours of its
discovery. Until appropriate action is completed, any
active leak of PCBs must be contained to prevent exposure of
humans or the environment and inspected daily to verify
1-17
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containment of the leak. Trenches, dikes, buckets, and pans
are examples of proper containment measures [761.30(a) (1) (x) ]
Cleanup should be done in accordance with the PCB Spill
Cleanup Policy. See Chapter XIV.
8) FIRE-RELATED INCIDENTS: If a PCB Transformer is involved
in a fire-related incident, the owner of the transformer
must immediately report the incident to the National
Response Center (toll-free 1-800-424-8802; in Washington,
D.C. 202-426-2675). A fire-related incident is defined as
any incident involving a PCB Transformer which involves the
generation of sufficient heat and/or pressure (by any
source) to result in the violent or non-violent rupture of a
PCB Transformer and the release of PCBs. Information must
be provided regarding the type of PCB Transformer
installation involved in the fire-related incident (e.g.,
high or low secondary voltage network transformer, high or
low secondary voltage simple radial system, expanded radial
system, primary selective system, primary loop system, or
secondary selective system or other systems) and the readily
ascertainable cause of the fire-related incident (e.g., high
current fault in the primary or secondary or low current
fault in secondary).
The owner of the PCB Transformer must also take measures as
soon as practically and safely possible to contain and
control any potential releases of PCBs and incomplete
combustion products into water [761.30(a)(1)(xi)]. These
measures include, but are not limited to:
• The blocking of all floor drains in the vicinity
of the transformer [761.30 (a) (1) (xi) (A)] .
• The containment of water runoff [761.30(a) (1) (xi)
(B)] .
• The control and treatment (prior to release) of
any water used in subsequent cleanup operations
[761.30(a)(1)(xi)(C)].
9) DISCOVERY OF A MINERAL OIL PCB TRANSFORMER: In the event
a mineral oil transformer, assumed to contain less than 500
ppm of PCBs as provided in 761.3, is tested and found to be
contaminated at 500 ppm or greater PCBs ("PCB Transformer"),
the unit is subject to all the requirements for PCB
Transformers in 40 CFR part 761 and efforts must be
initiated immediately to bring the transformer into
compliance in accordance with the following schedule
[761.30(a)(1)(xv)(A) through (J)]:
• Report fire-related incidents, effective
immediately after discovery.
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Mark/label the PCB Transformer within 7 days after
discovery.
Mark/label the vault door, machinery room door,
fence, hallway, or other means of access to the
PCB Transformer within 7 days after discovery.
Register the PCB Transformer in writing with fire
response personnel with primary jurisdiction and
with the commercial building owner, within 30 days
of discovery.
Install electrical protective equipment on a
radial PCB Transformer and a non-sidewalk vault,
lower secondary voltage network PCB Transformer in
or near a commercial building within 18 months of
discovery or by October 1, 1990, whichever is
later. NOTE: This section of the regulation was
amended in the Federal Register of November 26,
1990 (55 FR 49043) to indicate the February 25,
1991 deadline for installing electrical protection
on lower secondary voltage radial PCB Transformers
as indicated at 761.30(a)(1)(iv)(E).
Remove a non-sidewalk vault, lower secondary
voltage network PCB Transformer in or near a
commercial building, if electrical protective
equipment is not installed, within 18 months of
discovery or by October 1, 1993, whichever is
later.
Remove a lower secondary voltage network PCB
Transformer located in a sidewalk vault in or near
a commercial building, within 18 months of
discovery or by October 1, 1993, whichever is
later.
Retrofill and reclassify a high secondary voltage
radial PCB Transformer or a lower or higher
secondary voltage network PCB Transformer, located
in other than a sidewalk vault in or near a
commercial building, within 18 months or by
October 1, 1990, whichever is later (lower
secondary voltage PCB Transformers by February 25,
1991 -- see NOTE above). This is an option in
lieu of installing electrical protective equipment
on a radial or lower secondary voltage network PCB
Transformer located in other than a sidewalk vault
or of removing a higher secondary voltage network
PCB Transformer or a lower secondary voltage
network PCB Transformer, located in a sidewalk
vault, from service.
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Retrofill and reclassify a lower secondary voltage
network PCB Transformer, located in a sidewalk
vault, in or near a commercial building within 18
months or by October 1, 1993, whichever is later.
This is an option in lieu of installing electrical
protective equipment or removing the transformer
from service.
Retrofill and reclassify a higher secondary
voltage network PCB Transformer, located in a
sidewalk vault, in or near a commercial building
within 18 months or by October 1, 1990, whichever
is later. This is an option in lieu of other
requirements.
SERVICING AND RECLASSIFICATION CONDITIONS
The processing of PCB and PCB-Contaminated Transformers is
limited to servicing activities. These servicing activities
include: draining and refilling, topping off, repairing,
and retrofilling for reclassification [761.30(a)(2)].
the processing and distribution in commerce of PCBs, 50 ppm
or greater, for purposes of servicing and repairing a
customer's equipment is prohibited without an EPA exemption
[761.30(a)(2)(vii)]. However, an exemption is not required
to service your own PCB or PCB-Contaminated Transformer with
the PCB or PCB-contaminated fluid you already own, in
accordance with the regulations. Also, you can service a
customer's transformers if you use non-PCB or PCB-free
fluid; and, you are allowed to refill a customer's
transformers with the same fluid that came out of the
transformers, regardless of PCB concentration.
The processing (servicing) of non-PCB Transformers with non-
PCB fluids and/or components is allowed without restriction.
A PCB Transformer may be reclassified to a PCB-contaminated
or non-PCB Transformer by draining, refilling, and otherwise
servicing the unit. In order to be reclassified, the
transformer's dielectric fluid must contain less than 500
ppm PCB (for conversion to PCB-contaminated level) or less
than 50 ppm PCB (for conversion to non-PCB level) after a
minimum of 3 months of inservice use subsequent to the last
servicing conducted for the purposes of reducing the PCB
concentration in the transformer. Inservice means that the
transformer is used electrically under loaded conditions
that raise the temperature of the dielectric fluid to at
least 50° Centigrade. The Director of the Chemical
Management Division may grant, without further rulemaking,
approval for the use of alternative methods that simulate
the loaded conditions of inservice use [761.30(a) (2) (v)] .
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Q20: How long do I have to keep the transformer fluid at 50°C?
A20: The regulations do not give a specific amount of time for
keeping the temperature at 50°C, but the intent of the
regulation is to simulate the normal use of a transformer.
For example, if during normal use, a transformer reaches
50°C on Tuesdays and Thursdays for an hour per day, that is
how long the transformer should be at 50°C to reclassify the
transformer.
NOTE: EPA is has proposed alternative methods of
reclassification for both PCB and PCB-Contaminated
Transformers in the Federal Register of November 18, 1993
(58 FR 60970) .
The following conditions also apply to service activities:
• Removing the coil from a PCB Transformer (500 ppm
or greater) is prohibited [761.30(a) (2) (ii)] .
• PCB-Contaminated Transformers may be serviced
(including rebuilding) only with dielectric fluid
containing less than 500 ppm PCB
[761.30(a) (2) (i)] .
• PCBs, 50 ppm or greater, removed during servicing
must be either reused as dielectric fluid or
disposed of in accordance with EPA requirements
[761.30(a)(2)(ill)].
• PCBs from PCB Transformers must not be mixed with
or added to dielectric fluid from PCB-Contaminated
Transformers [761.30(a) (2) (iii)] .
• If dielectric fluid containing less than 500 ppm
PCBs is mixed with fluid containing 500 ppm or
greater PCBs, then the resulting mixture must not
be used as dielectric fluid in any electrical
equipment. The entire mixture must be considered
to be greater than 500 ppm PCBs and must be
disposed of in an incinerator that meets EPA
requirements [761.30(a)(2)(iv)].
• Any dielectric fluid containing 50 ppm or greater
PCBs used for servicing transformers must be
stored in accordance with the storage for disposal
requirements [761.30(a)(2)(vi)].
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STORAGE FOR REUSE
Transformers containing PCBs at any concentration may be
stored for reuse. While there are no time limitations on
this storage, transformers 50 ppm or greater (known or
assumed) which are stored for reuse should be in a condition
suitable for reuse. Equipment that is not suitable for
reuse will be considered improperly disposed of. Units that
are in storage for reuse are considered by EPA to be "in-
service" for purposes of the regulations. Also, as of
October 1, 1985, the storage for reuse of PCB Transformers
(500 ppm or greater) that pose an exposure risk to food or
feed is prohibited [761.30(a)(1)(i)].
Q21: How long can I keep a "burned-out" or "nonfunctional"
transformer in storage for reuse if I plan on repairing it
and using it later?
A21: EPA does not require nonfunctional transformers (regardless
of PCB concentration) to be placed into "storage for
disposal" if you intend to repair and reuse the item.
However, EPA may have grounds to enforce against lengthy
"storage for reuse" of equipment which is not reasonably
expected to be placed back into service. The owner should
be able to demonstrate good faith compliance with the intent
of the storage for disposal requirements and complete any
required servicing or repairs within a reasonable amount of
time. Any item that is damaged and cannot be repaired for
regulatory or technical reasons must be disposed of or
placed into storage for disposal.
STORAGE FOR DISPOSAL
All PCB and PCB-Contaminated Transformers must be dated when
placed into storage for disposal [761.65(c)(8)] and must be
removed from storage and disposed of within one year
[761.65(a)].
The facility used to store PCB and PCB-Contaminated
Transformers must comply with the "storage for disposal"
requirements [761.65(b)(1)]. See the chapter titled "PCB
Storage Requirements" for specific requirements.
Non-leaking PCB and PCB-Contaminated Transformers may be
stored temporarily by the generator in an area that does not
comply with the requirements for a PCB storage facility for
up to 30 days from the date of their removal from service
for disposal, provided that a notation is attached to each
transformer indicating the dates the equipment was removed
from service [761.65(c) (1) (i)], and placed into storage for
disposal [761.65(c) (8)] .
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Leaking PCB and PCB-Contaminated Transformers which are
placed in PCB Containers that comply with DOT specifications
[761.65 (c) (6)] with sufficient sorbent materials to absorb
any liquid PCBs, may also be temporarily stored by the
generator for up to 30 days provided that a notation is
attached to the container indicating the dates the
transformer was removed from service [761.65 (c) (1) (ii)], and
placed into storage for disposal [761.65(c)(8)]. Each
container or drum used to store leaking PCB Items must be
marked in accordance with EPA marking and labeling
requirements [761.40(a) (1) ] .
Nonleaking and structurally undamaged PCB-Contaminated
Transformers, that have not been drained of free-flowing
dielectric fluid, may also be stored on pallets next to a
PCB storage facility which meets the requirements for
storage for disposal. This type of storage is permitted
only when the storage facility has immediately available
unfilled storage space equal to 10 percent of the volume of
the equipment stored outside the facility. The equipment
stored outside the facility must be inspected for leaks
weekly [761.65(c)(2)], and a notation must be attached to
each unit indicating the date the equipment was removed from
service [761.65(c)(1)] and placed into storage for disposal
[761.65(c)(8)].
Commercial storers now must seek approval to operate and
demonstrate financial responsibility for closure of the
facility under the new provisions of the Notification and
Manifesting Rule which was published in the Federal Register
on December 21, 1989. See Chapters XII and XIX for further
details on commercial storage facility approvals and other
aspects of the Notification and Manifesting Rule.
DISPOSAL
PCB Transformers (500 ppm or greater) must be disposed of as
follows:
• In an incinerator that complies with 40 CFR
761.70.
• In a chemical waste landfill which complies with
761.75 provided that: the transformer is first
drained of all free-flowing liquid, filled with
solvent, allowed to stand for at least 18 hours
and then drained thoroughly. PCB liquids that are
removed shall be disposed of by incineration under
761.60(a). Solvents may include kerosene, xylene,
toluene and other solvents in which PCBs are
readily soluble. Precautionary measures should be
taken, however, that the solvent flushing
procedure is conducted in accordance with
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applicable safety and health standards as required
by Federal or State regulations
[761.60(b) (1) (i) (B)] .
• The PCB liquids that are removed, including the
flushing solvent, must be disposed of in an
incinerator that complies with 40 CFR 761.70, or
by an alternative EPA approved and permitted
disposal method in accordance with 761.60(e).
PCB-Contaminated Transformers (50-499 ppm PCBs) shall be
disposed of as follows:
• By draining all free-flowing liquid from the
transformer and disposing of the liquid in an
incinerator that complies with 40 CFR 761.70; or,
in a chemical waste landfill that complies with
761.75, if information is provided to the owner or
operator of the chemical waste landfill that shows
that the waste does not exceed 500 ppm PCBs and is
not an ignitable waste as described in
761.75(b) (8) (iii); or, in an approved high
efficiency boiler that complies with
761.65(a) (2) (iii); or, by an alternative EPA
approved and permitted disposal method that
complies with 761.60(e) [ (761.60(b) (4)] .
The disposal of the drained contaminated equipment carcass
is not regulated [761.60(b)(5)(ii)]; however, drained PCB-
Contaminated Transformer carcasses cannot be sold
(distributed in commerce) for use as parts and components in
repair or rebuilding activities. (See Distribution in
Commerce.)
Non-PCB Transformers (less than 50 ppm PCB) may be disposed
of with the following considerations:
• There are no PCB disposal requirements for non-PCB
Transformers. However, certain reuse restrictions
apply to the less than 50 ppm PCB fluid. Waste
oil with any detectable concentration of PCBs
cannot be used as a sealant, coating, or dust
control agent [761.20(d) ] ; and also, can only be
burned for energy recovery in specific combustion
facilities described in 761.20(e)(1). See the
chapter on "Disposal" for a detailed discussion of
the disposal of non-PCB waste oils.
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RECORDKEEPING
The Notification and Manifesting Rule (FR December 21, 1990)
adopts additional recordkeeping and reporting requirements
at 761.180(a) and (b) to complete the tracking system for
PCB wastes. The rule requires that the manifests themselves
be retained as records by waste handlers, and it requires
reporting to EPA in the event of irregularities in the
transport of regulated wastes. These reports depend largely
on information derived from particular manifests.
Three of_the waste tracking reports are modeled after their
RCRA counterparts. The rule requires "Exception Reports" to
be filed with EPA whenever a generator has not received
verification of delivery of PCB waste within 45 days. Also,
a "Discrepancy Report" is required of storage or disposal
facilities in those cases where the waste' actually delivered
to them does not correspond exactly with the types and
quantities described on the manifest. Third, an
"Unmanifested Waste Report" is required of disposers or
storers in those instances in which waste arrives at a
facility unaccompanied by a required manifest. All of these
reports may be thought of as "red flags" to EPA of possible
disposal violations. They provide the means for generators
and disposers to "enforce" the day-to-day workings of the
manifest system for EPA.
The rule adds one additional reporting requirement for which
there is no counterpart under RCRA. This requirement is the
"One-year Exception Report," intended to bolster EPA's
ability to enforce the requirement under TSCA regulations
that limits storage of PCBs prior to disposal to no more
than one year. Information on when items of PCB waste were
removed from service for disposal is included with the
manifests that accompany the waste from generation to
disposal. Disposers are required to certify the date of
disposal of PCB waste manifested to them, and in the event
more than one year has elapsed since the PCBs were removed
from service for disposal, a report must be filed with EPA.
Finally, the rule adds several amendments to the existing
PCB recordkeeping provisions that concern the Annual
Document requirements for the users, storers, and disposers
of PCBs. The most significant of these amendments is the
requirement that each disposer and commercial storer of PCB
waste submit by July 15 of each year an annual report, which
is a summary of the previous calendar year's PCB activity at
the facility. The report will be submitted to the
appropriate EPA Regional Administrator. See Chapter XV,
Recordkeeping and Reporting, for further details on the
recordkeeping requirements under the Notification and
Manifesting Rule.
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Testing data, inventories, servicing and reclassification
records, spill reports, and disposal records should be
maintained for all PCB and PCB-Contaminated Transformers.
Specific types and quantities of PCB's [761.180(a)] form the
basis of an Annual Document Log which must be prepared each
year and maintained for at least 3 years after the facility
ceases using or storing PCBs and PCB Items in quantities
prescribed in section 761.180(a). Annual Records (manifests
and certificates of disposal) shall be maintained for the
same period. The Annual Document for 1989 shall cover the
period from January 1, 1989 to February 5, 1990 (the
effective date of the final rule). See Chapter XV,
"Recordkeeping and Reporting" for a detailed discussion of
Annual Records.
SPILLS
Spills, leaks, and other uncontrolled discharges where the
release results in any quantity of PCBs running off or about
to run off the external surface of a PCB or PCB-Contaminated
Transformer is considered improper disposal of PCBs. The
PCB Spill Cleanup Policy provides specific cleanup measures
which, if followed explicitly, create a presumption against
enforcement for penalties or further cleanup. See the
chapter on "PCB Spill Cleanup Policy" for specific measures.
PCB spills involving 1 Ib. or more of pure PCBs (generally 1
pint of Askarel) must be reported to the National Response
Center at (800) 424-8802. Spills of 10 Ibs. or more of pure
PCBs (generally a gallon) must be reported to the
appropriate regional EPA office. Failure to notify the NRC
under CERCLA can lead to civil penalties under Section 109
or, under Section 103, criminal fines and imprisonment. Any
spill should be reported when people or animals can come
into direct and uncontrolled contact with PCBs.
Measures must immediately be taken to control the spread of
the spill. Any threats to water should be given highest
priority. Water and other complicated spills should be
cleaned up by trained personnel to levels set by the
appropriate EPA Regional Administrator. Organizations that
frequently handle PCBs should develop spill contingency
plans and conduct training for dealing with spills.
Once a spill is contained, cleanup measures can begin. EPA
requires cleanup of PCBs to different levels depending on
spill location, the potential for exposure to residual PCBs
remaining after cleanup, the concentration of PCBs initially
spilled, and the nature and size of the population
potentially at risk of exposure. While the PCB Spill
Cleanup Policy applies to the majority of situations,
exceptional circumstances may require additional cleanup at
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the direction of the EPA regional office. A detailed
description of the specific reporting, cleanup,
recordkeeping, and post-cleanup sampling requirements is
found in the chapter on "PCB Spill Cleanup Policy."
Other minor weeping from PCB or PCB-Contaminated Transformer
bushings and seams, not covered by the spill policy, is
still considered improper disposal of PCBs and compels
responsible parties to take actions to rectify the exposure
of humans and the environment to PCBs.
Q22: Do records and/or spill reports have to be kept for all PCB
or PCB-Contaminated Transformers which rupture?
A22: The PCB Spill Cleanup Policy specifies certain recordkeeping
requirements when a PCB or PCB-Contaminated Transformer
ruptures or spills. See the chapter on "PCB Spill Cleanup
Policy" for specific spill recordkeeping requirements.
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CHAPTER I
PART B
TRANSFORMERS
(RAILROAD)
Manufacturing (page 1-29)
Processing (page 1-29)
Distribution in Commerce (Sale of Railroad Transformers)
(page 1-29)
Exemptions to Manufacture, Process, and Distribute
PCBs in Commerce (page 1-31)
Marking/Labeling (page 1-31)
Use and Performance Requirements (page 1-32)
Servicing and Reclassification Conditions (page 1-32)
Storage for Reuse (page 1-33)
Storage for Disposal (page 1-33)
Disposal (page 1-33)
Spills (page 1-32)
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PART B
RAILROAD TRANSFORMERS
EPA defines railroad transformers (in the same manner as
nonrailroad transformers) in three basic categories --
"PCB," "PCB-contaminated," and "Non-PCB." Also, the
"assumption rules" discussed earlier in this chapter (see
page 1-1) apply to untested railroad transformers. The
following conditions and restrictions apply to PCBs in
transformers in railroad locomotives or railroad self-
propelled cars (railroad transformers).
MANUFACTURING
The manufacture of PCBs, regardless of concentration, for
use in railroad transformers is prohibited without an EPA
exemption [TSCA section 6(e) and 761.20(b)].
PROCESSING
The processing of PCBs, 50 pptn or greater, for use in
railroad transformers is prohibited without an EPA exemption
[TSCA section 6(e) and 761.20(c)]. However, PCBs at
concentrations less than 50 ppm may be processed for use in
railroad transformers (under specific conditions) in
accordance with the definition of "Excluded PCB Products"
[761.3]. Also, PCBs at any concentration may be processed
(i.e., prepared and/or packaged for distribution in
commerce) for purposes of disposal [TSCA section 6(e) and
761.20(c)(2)].
DISTRIBUTION IN COMMERCE (Sale of Railroad Transformers)
The distribution in commerce of PCBs, 50 ppm or greater, for
use in railroad transformers is prohibited without an EPA
exemption [761.20(c)]. However, PCBs at concentrations less
than 50 ppm may be distributed in commerce for use in
railroad transformers (under specific conditions) in
accordance with the definition of "Excluded PCB Products"
[761.3] . Also, PCBs at any concentration may be distributed
in commerce for purposes of disposal in accordance with the
requirements of 761.60 [761.20(c)(2)]. Disposal, in this
context, means the termination of the
useful life of the PCB or PCB-contaminated railroad
transformer.
The distribution in commerce (sale) of railroad transformers
which contain PCBs in concentrations of 50 ppm or greater
(known or assumed) for purposes of reuse is allowed only if:
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• the unit was originally sold for use before
July 1, 1979;
• the unit is intact and nonleaking at the time of
sale; and
• no PCBs are introduced into the unit.
Q24: Does this mean that I can sell a PCB or PCB-contaminated
railroad transformer?
A24: Yes. If the railroad transformer was originally sold for
use before July 1, 1979, and is now being sold for resale or
reuse (i.e., continued use). Also, the railroad transformer
must be intact and nonleaking. EPA recommends that the
buyer be advised that he is purchasing a PCB or PCB-
contaminated unit.
Q25: What does intact and nonleaking mean?
A25: Intact and nonleaking means that the railroad transformer
has all fluid intact and there are no PCBs on the external
surface of the equipment.
Q26: Can I sell drained PCB-contaminated railroad transformers
(known or assumed 50-499 ppm) to a scrap or salvage dealer
for metals recovery?
A26: Yes. The sale of drained 50-499 ppm carcasses for scrapping
or salvaging is generally considered distribution in
commerce for purposes of disposal and is allowed with
certain limitations. To qualify as disposal, the scrapping
practice must be one which will "...terminate the useful
life of PCBs or PCB Items" [761.3]; or, in other words, will
destroy any residual PCBs found in the drained carcasses.
Salvaging aimed at reclamation of the metals found in the
case and coil generally constitutes disposal, because any
residual PCBs are destroyed by the high temperatures
employed in the smelting process. However, where salvaging
consists of disassembling the drained equipment to obtain
parts for reuse in other equipment, the useful life of the
equipment has not been fully terminated and thus is not
considered disposal. In sum, the scrapping/salvaging of 50-
499 ppm drained equipment is unregulated to the extent that:
(1) scrapping practices do not result in leaks, spills, or
other uncontrolled discharges of PCBs, and (2) any PCB-
contaminated components are not reintroduced into commerce.
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EXEMPTIONS TO MANUFACTURE. PROCESS. AND DISTRIBUTE PCBs IN
COMMERCE
Exemptions to manufacture, process, and distribute in
commerce PCBs in railroad transformers may be granted only
by rulemaking on a case-by-case basis. The EPA
Administrator may set terms and conditions for an exemption
and may grant an exemption for not more than one year. EPA
interim procedural rules for processing and distribution in
commerce exemptions describe the required content of
processing and distribution in commerce exemptions petitions
and the procedures EPA follows in rulemaking on exemption
petitions. Those rules were published in the Federal
Register of May 31, 1979 (44 FR 31558) and are codified at
40 CFR 750.30 through 750.41.
MARKING/LABELING
All PCB railroad transformers (500 ppm or greater) must be
marked in accordance with EPA marking and labeling
requirements [761.40]. All marks/labels must comply with
EPA marking formats which specify size, color, and design
[761.45].
• All PCB railroad transformers (500 ppm or greater)
must be marked individually with the Mark ML (PCB
label) [761.40{a)(2) and (c)(l)].
• The marking of PCB-contaminated railroad
transformers (50-499 ppm) is not required
[761.40(c)(1)].
• Transport vehicles loaded with one or more PCB
Transformers (500 ppm or greater) must be marked
on each end and each side with the mark ML (PCB
label) [761.40(b)].
• All marks/labels must be placed in a position on
the exterior of the transformer and/or transport
vehicle so that the mark can be easily seen by
persons inspecting the transformer [761.40(h)].
PCB Transformer locations must also be marked/labeled in
accordance with 761.40(j).
• As of December 1, 1985, the vault door, machinery
room door, fence, hallway, or other means of
access (other than grates and manhole covers) to a
PCB Transformer must be marked with the mark ML
(PCB label) [761.40(j(1)].
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As of July I, 1986, the use of railroad transformers
containing dielectric fluids with a PCB concentration
greater than 1,000 ppm was prohibited [761.30(b)(1)(vi)].
Q27: What should be done if a railroad organization discovers
that an inservice railroad transformer contains over 1,000
ppm PCBs today?
A27: The continued use of railroad transformers containing over
1,000 ppm PCBs was prohibited in 1986. Consequently, if a
railroad transformer were discovered today as containing
more than 1,000 ppm PCBs, the owner/operator of the
transformer would be out of compliance with the regulations.
The Regional EPA Administrator should be contacted
immediately, and steps should be taken to bring the
equipment into compliance as soon as possible.
The concentration of PCBs in the dielectric fluid contained
in railroad transformers must be measured:
• Immediately upon completion of any authorized
servicing of a railroad transformer conducted for
the purpose of reducing the PCB concentration in
the dielectric fluid in the transformer
[761.30(b)(1)(vii)(A)]; and, between 12 and 24
months after each servicing
[761.30(b)(1)(vii)(B)].
• The data obtained as a result of the above
servicing shall be retained until January 1, 1991
[761.30(b)(1)(vii)(C)].
SERVICING AND RECLASSIFICATION CONDITIONS
The processing of PCB and PCB-contaminated railroad
transformers is limited to servicing activities. These
servicing activities include: draining and refilling,
topping off, repairing, and retrofilling for
reclassification [761.30(a)(2)].
• Railroad transformers may be serviced only with
dielectric fluid containing less than 1,000 ppm
PCBs [761.30(b) (2) (iii)]; except, if the coil is
removed from the casing of a railroad transformer
(e.g., the transformer is rebuilt), the railroad
transformer may not be refilled with dielectric
fluid containing a PCB concentration greater than
50 ppm [761.30(b)(2)(i)].
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• Dielectric fluid may be filtered through activated
carbon or otherwise industrially processed for the
purpose of reducing the PCB concentration in the
fluid [761.30(b)(2)(iv)].
• Any PCB dielectric fluid that is used to service
PCB railroad transformers (500 ppm or greater)
must be stored in accordance with the storage for
disposal requirements at 761.65 .[761.30(b)(1)(v)].
A PCB railroad transformer may be converted to a PCB-
Contaminated Transformer or to a non-PCB Transformer by
draining, refilling, and/or Otherwise servicing the railroad
transformer. In order to be reclassified, the railroad
transformer's dielectric fluid must contain less than 500-
ppm PCBs for conversion to PCB contaminated status, or less
than 50 ppm PCBs for conversion to non-PCB status after a
minimum of three months of inservice use subsequent to the
last servicing conducted for the purpose of reducing the PCB
concentration in the transformer [761.30(b)(2)(vii)].
STORAGE FOR REUSE
The storage for reuse conditions for PCB and PCB-
contaminated railroad transformers are identical to the
storage for reuse conditions for nonrailroad transformers as
outlined earlier in this chapter. (See page 1-22.)
STORAGE FOR DISPOSAL
The storage for disposal requirements for PCB and PCB-
contaminated railroad transformers are identical to the
storage for disposal requirements for nonrailroad
transformers as outlined earlier in this chapter. (See page
1-22.)
DISPOSAL
The disposal requirements for PCB and PCB-contaminated
railroad transformers are identical to the disposal
requirements for nonrailroad transformers as outlined
earlier in this chapter. (See page 1-23.)
SPILLS
Spills from railroad transformers are treated the same as
spills from non-railroad transformers. Please see the
earlier discussion of spills in this chapter (See page I-
26) .
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CHAPTER II
CAPACITORS
A. LARGE
Manufacturing (page 11-3}
Processing (page II-3)
Distribution in Commerce (Sale of Large PCB Capacitors)
(page II-3)
Exemptions to Manufacture, Process, and Distribute PCBs in
Commerce (page II-4)
Marking/Labeling (page II-4)
Phaseout Requirements (page II-5)
Use Conditipns (page II-6)
Servicing Conditions (page II-6)
Capacitors That Pose an Exposure Risk to Food or Feed
(page II-6)
Storage for Reuse (page II-7)
Storage for Disposal (page 11-7}
Disposal (page II-8)
Recordkeeping (page II-8)
Spills (page II-9)
-------
- CAPACITORS -
Capacitors are defined at 40 CFR 761.3 in two basic
categories--"small" and "large." A "small capacitor" is
defined as containing less than 1.36 kilograms (3 Ibs.) of
dielectric fluid. A "large capacitor" is defined as
containing 1.36 kilograms (3 Ibs.) or more of dielectric
fluid. The following assumptions may be used if the actual
weight of the dielectric fluid is unknown.
• A capacitor whose total volume is less than 1,639 cubic
centimeters (100 cubic inches) may be considered to
contain less than 1.36 kilograms (3 Ibs.) of dielectric
fluid.
• A capacitor whose total volume is more than 3,278 cubic
centimeters (200 cubic inches) must be considered to
contain more than 1.36 kilograms (3 Ibs.) of dielectric
fluid.
• A capacitor whose total volume is between 1,639 and
3,278 cubic centimeters may be considered to contain
less than 1.36 kilograms (3 Ibs.) of dielectric fluid
if the total weight of the capacitor is less than 4.08
kilograms (9 Ibs.).
Ql: Our rural utility has discovered numerous small capacitors
in phase converters (commonly referred to as "add-a-phases")
which are utilized in various applications, specifically on
farm irrigation systems. In most cases, these add-a-phase
type units contain several small, independent capacitors
(less than 3 Ibs. each) banded together within a single
housing compartment. Does EPA classify capacitors such as
these as small, individual capacitors, or must the combined
volume of the small capacitors be totaled and treated as one
large capacitor?
Al: Capacitors are classified according to the weight of fluid
in each individual unit, not by the total weight of a group.
II-l
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PART A
LARGE CAPACITORS
Large PCB Capacitors are used extensively by electric
utilities and other various industries. Large capacitors
are commonly used to improve the voltage and power factor of
electric power systems. Virtually all capacitors
manufactured prior to 1978 were filled with PCB dielectric
fluids generically known as "Askarels." (See the
"Introduction" chapter for a list of "Common Trade Names.")
These "Askarel" dielectric fluids generally range from 75-
100 percent PCB concentration. After July 1, 1979, the
manufacture of capacitors using these PCB dielectric fluids
(Askarels) was prohibited.
Large PCB Capacitors are classified based upon voltage
ratings [761.3] . A large capacitor that is rated for
operation at 2,000 volts (A.C. or B.C.) or above is termed a
"large, high-voltage capacitor," while a large capacitor
that is rated for operation below 2,000 volts is termed a
"large, low-voltage capacitor." Most TSCA requirements for
large PCB Capacitors are identical for both with the
exception of certain marking/labeling requirements which
vary depending upon "high" or "low" voltage. Also, the use
of PCB-contaminated Capacitors has not been phased out.
After October 1, 1988, the use of large PCB Capacitors is
prohibited unless the capacitor is used within a restricted
access area [761.30(1)]. Large PCB Capacitors which are
located in certain "restricted-access" areas may be used for
the remainder of their useful life. There are basically two
types of "restricted-access" areas which are acceptable for
the continued use of large PCB Capacitors beyond October 1,
1988: (1) restricted-access electrical substations, and
(2) contained and restricted-access indoor installations.
A "restricted-access electrical substation" is an outdoor,
fenced, or walled-in facility that restricts public access
and is used in the transmission or distribution of electric
power. Release of PCBs from capacitors in these substations
beyond the confines of the substations are extremely
limited. Outdoor, fenced or walled-in suburban locations
that perform R&D activities on large capacitors but do not
transmit or distribute electric power are still considered
to be restricted access areas.
A "contained and restricted-access indoor installation"
restricts public access and has an adequate roof, walls, and
floor to contain any release of PCBs within the indoor
location. Release of PCBs in these facilities also presents
very limited exposure potential.
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The majority of large PCB Capacitors which are not in a
restricted-access location are primarily found on utility
poles throughout electric service areas. The exposure risks
associated with these capacitors vary due to their
widespread use. These capacitor installations are used in
residential neighborhoods, industrial areas, rural areas,
public areas (such as shopping centers, schools, etc.), and
near waterways. Because of their location, these PCB
Capacitors have a greater potential for exposing humans,
animals, and the environment during their use than do other
large PCB Capacitors; therefore, their use was prohibited as
of October 1, 1988 [761.30(1)].
MANUFACTURING
The manufacture of PCBs, regardless of concentration, for
use in large capacitors is prohibited without an EPA
exemption [761.20(b)].
PROCESSING
The processing of PCBs, 50 ppm or greater, for use in large
capacitors is prohibited without an EPA exemption [761.20(c)
and (4)]. However, PCBs at any concentration may be
processed (i.e., prepared and/or packaged for distribution
in commerce) for purposes of disposal [761.20 (c) (2)] .
DISTRIBUTION IN COMMERCE (Sale of Large PCB Capacitors)
The distribution in commerce of PCBs, 50 ppm or greater, for
use in large capacitors is prohibited without an EPA
exemption [761.20 (c)] . PCBs at any concentration may be
distributed in commerce for purposes of disposal
[761.20(c)(2)]. Disposal, in this context, means the
termination of the useful life of the PCB or PCB-
Contaminated Capacitors.
The distribution in commerce (sale) of large capacitors
which contain PCBs in concentrations of 50 ppm or greater
for purposes of reuse is allowed provided:
• the capacitor was originally sold for use before
July 1, 1979;
• the capacitor is intact and nonleaking at the time
of sale; and
• no PCBs are introduced into the capacitor.
II-3
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Q2: Does this mean that I can sell a PCB Capacitor?
A2: Yes, if the capacitor was originally sold for use before
July 1, 1979, and is now being sold for continued use.
Also, the capacitor must be intact and nonleaking. EPA
recommends that the buyer be advised that he is purchasing a
PCB Capacitor. The capacitor must be marked in accordance
with 761.40.
Q3: What does intact and nonleaking mean?
A3: Intact and nonleaking means that the capacitor is
structurally sound with all fluid intact and there are no
PCBs on the external surface of the capacitor.
EXEMPTIONS TO MANUFACTURE. PROCESS. AND DISTRIBUTE PCBs IN
COMMERCE
Exemptions to manufacture, process, and distribute in
commerce PCB Capacitors or PCB dielectric fluids for use in
PCB Capacitors may be granted only by rulemaking on a case-
by-case basis. The EPA Administrator may set terms and
conditions for an exemption and may grant an exemption for
not more than one year. EPA interim procedural rules for
processing and distribution in commerce exemptions describe
the required content of processing and distribution in
commerce exemption petitions and the procedures EPA follows
in rulemaking on exemption petitions. Those rules were
published in the Federal Register of May 31, 1979 (44 FR
31558) and are codified at 40 CFR 750.30 through 750.41.
MARKING/LABELING
All large PCB Capacitors must be marked in accordance with
EPA marking and labeling requirements [761.40]. All
marks/labels must comply with EPA marking formats which
specify size, color, and design [761.45].
• All PCB large, high-voltage capacitors which are
in service (including stored for reuse) must be
marked individually with the mark ML (PCB label) .
• All PCB large, high-voltage capacitors and
equipment containing a large high-voltage
capacitor must be marked individually with the
mark ML (PCB label) at the time of removal from
use if not already marked [761.40(a)(3) and (4)].
II-4
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• PCB large, low-voltage capacitors are not required
to be marked while in service, but must be marked
at the time of removal from use [761.40(a)(5)].
• All marks/labels must be placed in a position on
the exterior of the capacitor so that the marks
can be easily seen by persons inspecting the
capacitor(s) [761.40(h)].
PHASEOUT REQUIREMENTS
• After October 1, 1988, the use and storage for
reuse of PCB large, high- and low-voltage
capacitors which pose an exposure risk to food or
feed is prohibited [761.30(1)].
• After October 1, 1988, the use of all PCB large,
high- and low-voltage capacitors is prohibited
unless the capacitor is used within a restricted
access electrical substation or in a contained and
restricted-access indoor installation. A
contained and restricted-access indoor
installation must have adequate roof, walls, and
floor to contain any release of PCBs within the
indoor location [761.30(1)]. Examples are
manufacturing facilities and commercial building
vaults.
Q4: Can large PCB Capacitors be used for the remainder of their
useful life provided they are located in a restricted access
electrical substation?
A4: Yes. However, if the location of the PCB Capacitors within
the substation still poses an exposure risk to food or feed,
the continued use of these units was prohibited after
October 1, 1988.
Q5: Can large PCB Capacitors be used for the remainder of their
useful life if they are located in an electrical power
plant? *
A5: Only if the power plant is a restricted access building and
has adequate roof, walls, and floors which would contain any
release of PCBs within the power plant.
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USE CONDITIONS
Large PCB Capacitors may be used for the remainder of their
useful lives only in accordance with the phaseout
requirements of 761.30(1). Non-PCB Capacitors are
unregulated for use.
• Inspections; No recorded maintenance inspections
are required for large PCB Capacitors. However,
ruptures, leaks, and other uncontrolled discharges
from PCB Capacitors are considered improper
disposal of PCBs, and should be cleaned up in
accordance with the PCB Spill Cleanup Policy.
SERVICING CONDITIONS
Since there is no specific authorization for servicing lage
PCB Capacitors their servicing is prohibited without an EPA
exemption.
CAPACITORS THAT POSE AN EXPOSURE RISK TO FOOD OR FEED
The use and storage for reuse of large PCB Capacitors that
pose an exposure risk to food or feed became prohibited
after October 1, 1988 [761.30(1)(1)].
Q6: Should a person consider catastrophic failure, such as
ruptures, explosions, or fire when trying to determine
whether a large PCB Capacitor poses an exposure risk to food
or feed?
A6: One must consider the location of a specific PCB Capacitor
in relation to food or feed products, and all other
available information. If there is a reasonable possibility
of contact between PCBs and food or feed as a result of a
discharge, the capacitor must be considered a risk. In
evaluating the exposure risk, it is useful to consider a
hypothetical situation in which PCBs are discharged in any
way from the capacitor, such as through a rupture or a leak.
The question to be asked is whether contact between food or
feed and PCBs is reasonably possible. PCB Capacitors that
are located adjacent to or above food or feed products pose
an exposure risk, unless there is secondary containment or J
another physical structure that prevents PCB discharges from
contaminating the food or feed. The standard to be applied
is a reasonable possibility of contamination of food or feed
by PCBs.
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STORAGE FOR REUSE
Large capacitors containing PCBs in any concentration may be
stored for reuse provided the storage does not pose an
exposure risk to food or feed. There are no time
limitations on this storage; however, the large PCB
Capacitors which are being stored for reuse must be in a
condition suitable for reuse, and the owner of the
capacitors should be able to demonstrate a reasonable need
to store spare capacitors. Large PCB Capacitors stored for
reuse must be stored in a restricted access electrical
substation or other restricted access indoor installation.
Capacitors stored for reuse are considered by EPA to be "in
service" for purposes of the regulations. These capacitors
must be handled as in use capacitors and all requirements
including marking, recordkeeping, and disposal remain the
same.
STORAGE FOR DISPOSAL
All large PCB Capacitors must be dated when placed into
storage for disposal and must be removed from storage and
disposed of within one year [761.65(a)].
Q7: Does each large PCB Capacitor in storage for disposal have
to be dated, or would a storage log or list indicating these
dates be sufficient?
A7: Each PCB Article, including individual PCB Capacitors, must
be dated on the article when placed into storage for
disposal [761.65(c)(8)]. Consequently, the mere listing of
dates on a storage log or list is not sufficient.
The facility used to store large PCB Capacitors for disposal
must comply with the "storage for disposal" requirements
[761.65(b)(1)]. See Chapter XII on "PCB Storage
Requirements" for specific requirements.
Nonleaking large PCB Capacitors may be stored temporarily by
the generator in an area that does not comply with the
requirements for a PCB storage facility for up to 30 days
from the date of their removal from service for disposal,
provided that a notation is attached to each capacitor
indicating the date the capacitor was removed from service
[761.65(c)(1)(i)] and placed into storage for disposal
[761.65(c) (8)] .
Leaking PCB Capacitors which are placed in PCB Containers
that comply with DOT specification [761.65(c)(6)] with
sufficient sorbent materials to absorb any liquid PCBs, may
also be temporarily stored by the generator for up to 30
II-7
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days provided that a notation is attached to the container
indicating the date the capacitor was removed from service
[761.65 (c) (1) (ii)] and placed into storage for disposal
[761.65 (c) (8)] . Each container or drum used to store
leaking PCB Capacitors must be marked in accordance with EPA
marking and labeling requirements [761.40(a)(1)].
Nonleaking and structurally undamaged PCB large, high-
voltage capacitors may also be stored for more than 30 days
on pallets next to a PCB storage facility which meets the
requirements for storage for disposal. This type of storage
is permitted only when the storage facility has immediately
available unfilled storage space equal to 10 percent of the
volume of capacitors and equipment stored outside the
facility. The capacitors stored outside the facility must
be inspected for leaks weekly [761.65(c) (2)], and a notation
must be attached to each capacitor indicating the date the
capacitor was removed from service [761.65(c)(1)] and placed
into storage for disposal [761.65(c)(8)]. If a weekly
visual inspection reveals a capacitor is leaking, having the
required available space within the storage area allows
immediate containment of the leak by moving the capacitor
into the storage area.
DISPOSAL
Large PCB Capacitors must be disposed of as follows:
• In an incinerator that complies with 40 CFR
761.70.
• By an alternative EPA approved and permitted
method in accordance with 761.60(e).
RECORDKEEPING
Owners or operators of facilities which use or store 50 or
more large PCB Capacitors shall develop and maintain records
on the disposition of the PCB Capacitors [761.180 (a)] .
These records shall consist of (1) the Annual Records and
(2) the Annual Document Log which must be prepared each year
by the facility and must be maintained for at least 3 years
after the facility ceases using or storing PCBs and PCB
Items in the prescibed quantities. See Chapter XV,
"Recordkeeping and Reporting" for a detailed discussion of
Annual Document Logs and Annual Records.
Q8: In my records, must I convert the weight of each PCB
Capacitor to kilograms?
II-8
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A8: Yes, the weight of PCB Capacitors is required to be
converted to kilograms using the total weight of the PCB
Capacitor and its contents.
Q9: Do I have to keep written inspections for PCB Capacitors?
A9: Except for capacitors temporarilly stored outside a storage
facility, no recorded maintenance inspections are required
for PCB Capacitors. However, ruptures, leaks, and other
uncontrolled discharges from PCB Capacitors are considered
improper disposal of PCBs.
SPILLS
Spills, leaks, and other uncontrolled discharges where the
release results in any quantity of PCBs running off or about
to run off the external surface of a large PCB Capacitor is
considered improper disposal of PCBs. The PCB Spill Cleanup
Policy provides specific cleanup measures which, if followed
explicitly, create a presumption against enforcement for
penalties or further cleanup under TSCA. See Chapter XIV on
"PCB Spill Cleanup Policy" for specific measures.
PCB Spills involving 1 Ib. or more of PCBs (generally 1 pint
of Askarel) must be reported to the National Response Center
(NRC) at (800) 424-8802. Spills involving 10 Ibs. or more
of PCBs (generally 1 gallon of Askarel) must also be
reported to the appropriate regional EPA office. Failure to
notify the NRC under CERCLA can lead to civil penalties
under Section 109 or, under Section 103, criminal fines and
imprisonment. Any spill should be reported when people or
animals can come into direct and uncontrolled contact with
PCBs.
Measures must immediately be taken to control the spread of
the spill. Any threats to water should be given highest
priority. Water and other complicated spills should be
cleaned up by trained personnel to levels set by the
appropriate EPA Regional Administrator. Organizations who
frequently handle PCBs should develop spill contingency
plans and conduct training for dealing with spills.
Once a spill is contained, cleanup measures can begin. EPA
requires cleanup of PCBs to different levels depending on
spill location, the potential for exposure to residual PCBs
remaining after cleanup, the concentration of PCBs initially
spilled, and the nature and size of the population
potentially at risk of exposure. While the PCB spill
cleanup policy applies to the majority of situations,
exceptional circumstances may require additional cleanup at
the direction of the EPA regional office. A detailed
description of the specific reporting, cleanup,
II-9
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recordkeeping, and post-cleanup sampling requirements is
found in Chapter XIV on "PCB Spill Cleanup Policy."
Other minor weeping from PCB Capacitor bushings and seams
not covered by the spill policy is still considered improper
disposal of PCBs and the provisions of the PCB Spill Cleanup
Policy should be followed.
Q10: Do records and/or spill reports have to be kept for all PCB
Capacitors which rupture?
A10: The PCB Cleanup Policy specifies certain recordkeeping when
a PCB Capacitor ruptures or spills. See the chapter on "PCB
Spill Cleanup Policy" for specific spill recordkeeping.
11-10
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CAPACITORS
B. SMALL
Manufacturing (page 11-12)
Processing (page 11-12)
Distribution in Commerce (Sale of Small PCB Capacitors)
(page 11-12)
Marking/Labeling (page 11-13)
Use Conditions (page 11-13)
Storage for Reuse (page 11-13)
Storage for Disposal (page 11-13)
Disposal (page 11-14)
Spills (page 11-14)
11-11
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PART B
SMALL CAPACITORS
Small capacitors are those which contain less than 3 Ibs. of
dielectric fluids. They commonly contain between 0.1 and
0.6 pound of PCBs and are used in fluorescent light
ballasts, household appliances, and industrial equipment.
In most applications, the equipment containing the small
capacitor in its circuitry cannot function without it.
Since these capacitors contain small quantities of
dielectric fluid and significant amounts of absorbent
material such as paper, and because many of these capacitors
are encapsulated, large amounts of PCBs are not released
from these capacitors during their use in appliances or
other equipment containing small capacitors. Therefore,
exposure risks to humans, food, feed, water, or the
environment from the use of these capacitors are generally
low. EPA has determined that the use of small capacitors
containing PCBs is not unreasonable because of their low
risk compared with the benefits from the use of millions of
pieces of electronic equipment and consumer products;
billions of dollars in replacement costs; and the lack of
practical cost-effective risk reduction measures.
MANUFACTURING
The manufacture of PCBs, regardless of concentration, for
use in small capacitors is prohibited [761.20(b)].
PROCESSING
The processing of PCBs, 50 ppm or greater, for use in small
capacitors is prohibited without an EPA exemption
[761.20 (c)] . PCBs in any concentration may be processed
(i.e., prepared and/or packaged for distribution in
commerce) for purposes of disposal in accordance with the
requirements of 761.60 [761.20(c)(2) and (4)].
DISTRIBUTION IN COMMERCE (Sale of Small PCS Capacitors)
The distribution in commerce of PCBs, 50 ppm or greater, for
use in small capacitors is prohibited without an EPA
exemption [761.20 (c)] . PCBs at any concentration may be
distributed in commerce for purposes of disposal in
accordance with the requirements of 761.60 [761.20(c) (2) and
(4)]. Disposal means the termination of the useful life of
the PCB or PCB-Contaminated Capacitors.
11-12
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The distribution in commerce (sale) of a small PCB Capacitor
for reuse or resale is allowed provided:
• the small capacitor was originally sold for use
before July 1, 1979;
• the small capacitor is intact and nonleaking at
the time of sale; and
• no PCBs are introduced into the small capacitor.
MARKING/LABELING
Small PCB Capacitors are not required to be marked or
labeled while in service or when removed from service for
disposal.
However, as of January 1, 1979, all PCB Equipment containing
a small PCB Capacitor was to be marked at the time of
manufacture with the statement: "This equipment contains
PCB Capacitor(s)." The mark was to be the same size as the
mark ML [761.40(d)].
Each small capacitor used in alternating circuits and each
fluorescent bulb manufactured between July 1, 1978 and July
1, 1998 that does not contain PCBs must be marked by the
manufacturer."No PCBs" [761.40(g)].
USE CONDITIONS
EPA has not placed any restrictions on the use of small PCB
Capacitors.
STORAGE FOR REUSE
There are no restrictions or limitations on the storage for
reuse of small PCB Capacitors provided that the capacitors
are in a condition suitable for reuse.
STORAGE FOR DISPOSAL
There are no time restrictions or storage requirements on
the storage for disposal of small PCB Capacitors provided
that they are intact and nonleaking [761.60(b)(6)].
However, a PCB Container (e.g., drum) which contains leaking
small PCB Capacitors must be marked, dated, and placed into
proper storage in accordance with the regulatory
requirements for a "PCB Container," and must be removed from
11-13
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storage and disposed of within one year [761.65(a)]. Also,
any small PCB Capacitor owned by any person, who
manufactures, or at any time manufactured, PCB Capacitors or
PCB Equipment and acquired the PCB Capacitor in the course
of such manufacturing, must be stored in accordance with
761.65(b).
DISPOSAL
Small PCB Capacitors and Equipment containing small PCB
Capacitors may be disposed of as municipal solid waste
[761.60(b) (2) (ii)], except that any small PCB Capacitor
owned by any person who manufactures or at any time
manufactured PCB Capacitors or PCB Equipment and acquired
the PCB Capacitors in the course of such manufacturing must
be disposed of as follows [761.60(b)(2)(iv)]:
• In an incinerator that complies with 40 CFR
761.70.
• By an alternative EPA approved and permitted
method.
EPA recommends that where several small PCB Capacitors are
gathered together in drums or containers, that the disposal
method be determined by the combined amount of PCBs in the
several capacitors. That is, if 3 Ibs. or more of PCBs are
contained in the several small capacitors, the Agency
recommends that the several small capacitors be disposed of
in accordance with the requirements for large capacitors.
Also, EPA encourages users of large amounts of small PCB
Capacitors to institute voluntary collection programs to
dispose of the small capacitors in PCB Incinerators.
[Readers are advised to contact their PCB Regonal
Coordinator for the policy on the disposal of large numbers
of small capacitors.]
SPILLS
Spills, leaks, and other uncontrolled discharges where the
release results in any quantity of PCBs running off or about
to run off the external surface of a small PCB Capacitor is
considered improper disposal of PCBs. The PCB Spill Cleanup
Policy provides specific cleanup measures which, if followed
explicitly, create a presumption against enforcement for
penalties or further cleanup. See the chapter on "PCB Spill
Cleanup Policy" for specific measures.
11-14
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Other minor weeping from PCB Capacitor bushings and seams
not covered by the spill policy is still considered improper
disposal of PCBs and it is recommended that the provisions
of the Spill Cleanup Policy be followed.
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CHAPTER III
HEAT TRANSFER AND
HYDRAULIC SYSTEMS
Manufacturing (page III-l)
Processing (page III-l)
Distribution in Commerce (Sale of Heat Transfer & Hydraulic
Systems) (page III-2)
Exemptions to Manufacture, Process, and Distribute PCBs in
Commerce (page III-2)
Marking/Labeling (page III-2)
Use and Servicing Conditions (page III-3)
Storage for Reuse (page III-4)
Storage for Disposal (page III-4)
Disposal (page III-4)
Recordkeeping (page III-5)
Spills (page III-5)
-------
- HEAT TRANSFER AND HYDRAULIC SYSTEMS -
PCBs were manufactured for use in heat transfer (Therminol-
66) and hydraulic (Pydraul) systems that were utilized in a
variety of industries until 1972. Heat transfer systems,
containing PCB fluids, were used in the inorganic chemical,
organic chemical, plastics and synthetics, and petroleum
refining industries. The aluminum, copper, iron, and steel
forming industries used hydraulic systems with commercial
Aroclor PCB fluids. High PCB levels apparently remained in
some systems until at least 1979. In addition, some unknown
quantity of unused PCB fluids was probably kept by
facilities after production ceased in 1972 and was used for
topping-off hydraulic and heat transfer systems.
Under section 6(e)(2) of TSCA, EPA may authorize the use of
PCBs if the Agency finds that the use will not present an
unreasonable risk to human health or the environment. EPA
has authorized the use of PCBs in heat transfer and
hydraulic systems at concentrations less than 50 ppm (under
specific conditions) for the remainder of their useful lives
[761.30(d) and (e)].
Numerous substitutes for PCBs have been used in heat
transfer and hydraulic systems to lower the PCB
concentration levels to less than 50 ppm. Included among
the chemical compounds used in non-PCB substitutes for
hydraulic fluid are phosphate esters, water/glycol
solutions, and water/oil emulsions. In addition, various
non-PCB heat transfer fluids are available. These include
modified esters, synthetic hydrocarbons, polyaromatic
compounds, partially hydrogenated and mixed terphenyls, and
blends of diphenyls.
MANUFACTURING
The manufacture of PCBs, regardless of concentration, for
use in heat transfer and hydraulic systems is prohibited
without an EPA exemption [761.20(b)].
PROCESSING
The processing of PCBs, 50 ppm or greater, for use in heat
transfer and hydraulic systems is prohibited without an EPA
exemption [761.20(c)]. PCBs at concentrations less than 50
ppm may be processed for use in heat transfer and hydraulic
systems (under specific conditions) in accordance with the
definition of "Excluded PCB Products" [761.3]. Also, PCBs
at any concentration may be processed (i.e.,
III-l
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prepared or packaged for distribution in commerce) for
purposes of disposal [761.20(c) (2) ].
DISTRIBUTION IN COMMERCE (Sale of Heat Transfer & Hydraulic
Systems)
The distribution in commerce (sale) of a heat transfer or
hydraulic system for reuse or resale which is contaminated
with PCBs (50 ppm or greater) is prohibited without an EPA
exemption [761.20(c)]. However, PCBs at any concentration
may be distributed in commerce for purposes of disposal
[761.20(c)(2)]. Disposal means the termination of the
useful life of the heat transfer or hydraulic system
[761.60(a) and (b)(3)].
EXEMPTIONS TO MANUFACTURE. PROCESS. AMD DISTRIBUTE PCBs IN
COMMERCE
Exemptions to manufacture, process, and distribute in
commerce PCBs in heat transfer and hydraulic systems or PCB
fluids for use in heat transfer and hydraulic systems may be
granted only by rulemaking on a case-by-case basis. The EPA
Administrator may set terms and conditions for an exemption
and may grant an exemption for not more than one year. EPA
interim procedural rules for processing and distribution in
commerce exemptions describe the required content of
processing and distribution in commerce exemptions petitions
and the procedures EPA follows in rulemaking on exemption
petitions. Those rules were published in the Federal
Register of May 31, 1979 (44 FR 31558) and are codified at
40 CFR 750.30 through 750.41.
All heat transfer and hydraulic systems with PCB
concentrations of 50 ppm or greater must be marked in
accordance with EPA marking and labeling requirements
[761.40] . All marks/labels must comply with EPA marking
formats which specify size, color, and design [761.45]. All
marks/labels must be placed in a position on the exterior of
the system so that the mark/label can be easily read by
persons inspecting or servicing the system [761.40(h)]. The
use of a heat transfer or hydraulic system with PCB
concentrations of 50 ppm or greater became unlawful after
July 1, 1984.
III-2
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USE AND SERVICING CONDITIONS
In 1979, EPA authorized the continued use of PCBs in
concentrations of 50 ppm or greater in heat transfer and
hydraulic systems in conjunction with a required retrofill
program. These use authorizations expired on July 1, 1984.
EPA assumed that the conditions of those use authorizations,
which required retrofilling all contaminated systems with
non-PCB fluids, would reduce the PCB concentration levels in
all of those systems to below 50 ppm by July 1, 1984.
When the 50 ppm regulatory cutoff was overturned in 1984 (as
a consequence of EOF v. EPA), the status of reducing PCB
concentrations in heat transfer and hydraulic systems to
less than 50 ppm was unclear. The July 10, 1984 ruling
authorized the continued use of heat transfer and hydraulic
systems with PCB concentrations less than 50 ppm (under
specific conditions) for the remainder of their useful
lives. However, the use of heat transfer and hydraulic
systems with PCB concentrations of 50 ppm or greater became
unlawful after July 1, 1984.
As of July 1, 1984, intentionally manufactured PCBs at
concentrations less than 50 ppm may be used in heat transfer
and hydraulic systems for the remainder of their useful
lives if the following requirements are met:
• Each owner of a heat transfer or hydraulic system
that ever contained 50 ppm or greater PCBs was
required to test his/her system for its PCB
concentration by no later than November 1, 1979,
and retest the system at least annually thereafter
[761.30(d) and (e) ] .
• Within 6 months of a test indicating the system's
fluid contains 50 ppm or greater PCBs, the system
must be drained of PCBs and refilled with non-PCB
fluid containing less than 50 ppm PCB [761.30(d)
and (e)].
• All subsequent required annual retests must be
performed at least 3 months after the most recent
fluid refilling. Then, when a test shows that the
PCB concentration in the system is less than 50
ppm, further testing is no longer required
[761.30(d) and (e)].
• After November 1, 1979, no heat transfer system
that was used in the manufacture or processing of
any food, drug, cosmetic or device, as defined in
Section 201 of the Federal Food, Drug, and *
III-3
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Cosmetic Act, could contain transfer fluid with 50
ppm or greater PCBs [761.30(d)(3)].
• Servicing, including topping-off, heat transfer
and hydraulic systems with fluids containing PCS
concentrations 50 ppm or greater is prohibited
[761.30(d) and (e)].
• All testing data must be retained for 5 years
•after the heat transfer or hydraulic system
reaches less than 50 ppm PCBs [761.30(d)&(e)].
Ql: Do VitonR elastomer gloves still have to be provided by
system owners and worn by system maintenance personnel?
Al: EPA has concluded that the VitonR glove requirement is not
necessary to protect against any unreasonable risks
presented by the continued use of authorized (less than 50
ppm) heat transfer and hydraulic systems. Consequently, EPA
amended the July 10, 1984 rule in the Federal Register of
June 27, 1988, by deleting the VitonR glove requirements
from the use authorizations. The use of impermeable gloves
to prevent dermal contact with PCB containing fluids may be
warranted, but the choice of such protection will be
dependent upon such factors as duration of exposure,
concentration of PCBs, and the permeability of the glove
material.
STORAGE FOR REUSE
The continued use and storage for reuse of heat transfer and
hydraulic systems containing 50 ppm or greater PCBs is
prohibited without an EPA exemption [761.20(a)].
EPA has not placed any restrictions on the storage for reuse
of non-PCB (less than 50 ppm) heat transfer and hydraulic
systems.
STORAGE FOR DISPOSAL
EPA has not placed any restrictions on the storage for
disposal of non-PCB (less than 50 ppm) heat transfer and
hydraulie systems.
DISPOSAL
EPA has not placed any restrictions on the disposal of non-
PCB (less than 50 ppm) heat transfer and hydraulic systems.
However, non-PCB fluids (2-49 ppm) generated from the
III-4
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draining of a non-PCB heat transfer or hydraulic system can
only be burned for energy recovery in accordance with EPA
restrictions on burning used oils as outlined under
761.20(e)(3). See the chapter on "Excluded PCB Products"
for a detailed discussion on burning non-PCB used oils.
RECORDKEEPING
Each owner of a heat transfer or hydraulic system that ever
contained PCBs at concentrations of 50 ppm or greater must
maintain all servicing and retrofill records as well as all
PCB testing data for 5 years after the PCB concentration in
the system was reduced to less than 50 ppm [761.30(d)(5) and
(e) (5)] .
Records should be maintained pursuant to 761.180 for all PCB
liquids (50 ppm or greater) which are drained from heat
transfer and hydraulic systems for disposal. In addition,
all owners of heat transfer and hydraulic systems who at one
time have stored at least 45 kilograms (99.4 pounds) of PCB
liquids in PCB Containers must develop and maintain Annual
Document Logs and Annual Records for each calendar year
[761.180(a)]. See Chapter XV, "Recordkeeping and Reporting",
for a detailed discussion of Annual Document Logs and Annual
Records.
SPILLS
Spills, leaks, and other uncontrolled discharges where the
release results in any quantity of PCBs ay concentrations of
50 ppm or greater running off or about to run off the
external surface of a heat transfer or hydraulic system is
considered improper disposal of PCBs. The PCB Spill Cleanup
Policy provides specific cleanup measures which, if followed
explicitly, create a presumption against enforcement of
penalties of further cleanup. See the chapter on "PCB Spill
Cleanup Policy" for specific measures.
Other minor weeping from heat transfer and hydraulic systems
with PCB concentrations 50 ppm or greater is still
considered improper disposal of PCBs and it is recommended
that the provisions of the Spill Cleanup Policy be followed.
III-5
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CHAPTER IV
NATURAL GAS PIPELINES
Manufacturing (page IV-1)
Processing (page IV-1)
Distribution in Commerce (page IV-1)
Use Conditions (page IV-2)
Marking/Labeling (page IV-2)
Storage for Disposal (page IV-2)
Disposal (page IV-3)
Air Compressors (page IV-4)
Reuse of Pipe at Less than 50 ppm PCBs (page IV-4)
-------
- NATURAL GAS PIPELINES -
PCB contamination in natural gas pipeline air compressors,
natural gas compressors, and natural gas pipeline liquids is
believed to have occurred through several sources. The
major sources of contamination are thought to be:
lubricating oils (Turbinol) used in the natural gas air
compressors; "fogging" of the pipe lines with an oil vapor
to minimize the entrainment of dust and other particles in
the pipeline system and migration of PCBs from contaminated
lines into other systems. By the 1960s, fogging of
pipelines was virtually nonexistent due to improved dry
filters and the replacement of cast iron pipe with welded
steel pipes. PCBs have not been used as lubricating oils in
compressors since the 1970s. Note: EPA continues to
develop guidance for the practical use and disposal of PCB
contaminated pipelines. The Federal Register should be
reviewed for any new information regading pipelines and
related facilities.
MANUFACTURING
The manufacture of PCBs, regardless of concentration, for
use in natural gas pipelines is prohibited without an EPA
exemption [761.20(b)].
PROCESSING
The processing of PCBs, 50 ppm or greater, for use in
natural gas pipelines is prohibited without an EPA exemption
[761.20 (c)]. However, PCBs at concentrations less than 50
ppm may be processed for use in natural gas pipelines (under
limited specific conditions) in accordance with the
definition of "Excluded PCB Products" [761.3]. Also, PCBs
at any concentration may be processed (i.e., prepared and/or
packaged for distribution in commerce) for purposes of
disposal in accordance with the requirements of 761.60
[761.20(c) (2)] .
DISTRIBUTION IN COMMERCE
The distribution in commerce of PCBs, 50 ppm or greater, for
use in natural gas pipelines is prohibited without an EPA
exemption [761.20 (c)]. However, pipes and other reusable
materials from natural gas pipelines historically with PCB
concentrations less than 50 ppm may be distributed in
commerce for reuse (under specific conditions) in accordance
with the definition of "Excluded PCB Products" [761.3].
IV-1
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However, EPA reommends that any such pipe should not be used
in connection with water supply sources, drainage ditches,
or in other circumstances where food or feed could become
contaminated. While such applications may not violate TSCA,
they may result in potential civil liability for damages for
the supplier or violations of other Federal or State
regulations. PCBs at any concentration may be distributed
in commerce for purposes of disposal in accordance with the
requirements of 761.60 [761.20(c) (2) ] .
USE CONDITIONS
EPA has determined that the use of PCBs in natural gas
pipeline compressors (compressors used for the transmission
of gas) and in the liquid found in natural gas pipelines at
concentrations of less than 50 ppm (not as a result of
dilution) does not present an unreasonable risk to human
health or the environment. Therefore, EPA has authorized
the continued use of PCBs at concentrations less than 50 ppm
in natural gas pipeline compressors and liquids indefinitely
[761.30(i)], provided that the compressors and the pipelines
are marked/labeled in accordance with EPA marking
requirements [761.45(a)].
MARKING/LABELING
Natural gas pipeline compressors and pipelines which are
contaminated with PCBs, regardless of concentration, must be
marked/labeled in compliance with EPA marking requirements
[761.30(i)] . All marks/labels must comply with EPA marking
formats which specify size, color, and design [761.45]. All
marks/labels must be placed in a position on the compressor
so that the mark can be easily read by persons inspecting or
servicing the compressor [761.40(h)].
STORAGE FOR DISPOSAL
Liquids and/or solids (e.g., rags, dirt, debris, etc.)
contaminated with PCBs (50 ppm or greater) must be placed
into proper containers for storage for disposal. All PCB
waste (50 ppm or greater) generated from natural gas
pipelines (such as used pipe, liquids contaminated with PCBs
and solids/debris contaminated with PCBs) must be stored in
accordance with EPA storage requirements under 761.65.
The above PCB Articles (used pipe) and PCB Containers
(liquids and/or solids) 50 ppm or greater must be dated when
placed into storage for disposal [761.65(c)(8)] and must be
removed from storage and disposed of within one year
[761.65(a)].
IV-2
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The facility used to store PCB waste (50 ppm or greater)
generated from natural gas pipelines must comply with the
storage for disposal requirements under 761.65(b)(1). See
the chapter on "PCB Storage Requirements" for specific
requirements.
Nonleaking PCB Articles may be stored temporarily by the
generator in an area that does not comply with the
requirements for a PCB storage facility for up to 30 days
from the date of their removal from service for disposal,
provided that a notation is attached to each article
indicating the dates the article was removed from service
[761.65(c) (1) (i)], and placed into storage for disposal
[761.65(c) (8)] .
DISPOSAL
All PCB waste (50 ppm or greater) including used pipe,
condensate, and other liquids and solids contaminated with
PCBs at levels 50 ppm or greater, must be disposed of in
accordance with EPA disposal requirements under 761.60.
All condensate removed from the pipe is liquid PCBs and must
be disposed of according to its concentration. At
concentrations less than 50 ppm, liquid PCBs are not
regulated for disposal under TSCA unless such PCBs are
diluted to circumvent disposal regulations [761.1(b).
Disposal of condensate containing less than 50 ppm PCB
(undiluted) is regulated under RCRA. Liquid PCBs in
concentrations between 50 and 500 ppm must be incinerated,
disposed of in a TSCA chemical waste landfill, a high
efficiency boiler, or by an alternative disposal method
[761.60(a)(1), (4) and (e) ].
Pipeline is regarded as a "PCB Article" as defined under
761.3. It must be disposed of according to its
concentration of PCBs under 761.60(b)(5). Accordingly,
removed pipe with PCB concentrations greater than 500 ppm
must be disposed of in a TSCA incinerator, a TSCA chemical
waste landfill, or by an alternative disposal method
[761.60(e)]. Pipeline with concentrations greater than 500
ppm may not be abandoned. Any pipe with a PCB concentration
between 50 and 500 ppm is not regulated for disposal after
all free flowing liquid has been removed. This means that
the pipe can be either abandoned in place, disposed of in a
municipal waste landfill, or smelted for recycling.
IV-3
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AIR COMPRESSORS
PCBs were used in lubricating oils that were added to air
compressors in the 1970s and early 1980s. These air
compressors were used to start natural gas compressors and
consisted of separate piping and receiver tanks as part of
the system. The air compressor system is regarded by EPA
for regulatory purposes as distinct from the natural gas
compressor itself.
EPA views the PCB contamination in air compressor system
piping and receiving tanks as PCB contamination that results
because of a spill from or in proximity to a PCB Item.
Accordingly, if the spill is cleaned up pursuant to EPA
regional standards, the use of the pipes and tanks would be
authorized under 761.20 (c) (5). Otherwise the contamination
constitutes an unauthorized use.
REUSE OF PIPE AT LESS THAN 50 PPM PCBs
The reuse of natural gas pipe at less than 50 ppm PCBs is
conditioned on the assumption that the three caveats in the
definition of"Excluded PCB Products" (section 761.3) are
met. These are that the products or source of the products
containing less than 50 ppm PCBs were (1) legally
manufactured, processed, distributed in commerce, or used
before October 1, 1984, (2) legally manufactured, processed,
distributed in commerce, or used pursuant to authority
granted by EPA regulation, by exemption petition, by
settlement agreement, or pursuant to other Agency-approved
programs, and (3) not the result of dilution, or leaks or
spills of PCBs at concentrations over 50 ppm.
QA: Once it is determined that the natural gas pipe I own is
less than 50 ppm PCBs, and not as a result of dilution, may
I sell this pipe for another use?
Al: Yes, if it has been determined that the pipe was
historically contaminated with less than 50 ppm PCBs or
reduced to less than 50 ppm PCBs through an authorized
process. If the pipeline system has an interconnection with
another pipeline system that has been contaminated at 50 ppm
or greater, the pipeline is presumed to have PCB
contamination as a result of dilution and may not be reused.
If this is the case, the pipeline company has two options:
(1) decontaminate the pipeline pursuant to a consent decree
or (2) obtain an approval for an alternate disposal
technology permit. If it is determined that the pipe may be
sold for another use under the TSCA regulations, you are not
relieved of any additional requirements under other Federal
or State statutes. For example, if the pipe were to be used
IV-4
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as conduits for drinking water they would have to be cleaned
to a level of non-detect according to the provisions of the
Safe Drinking Water Act.
IV-5
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CHAPTER V
ELECTROMAGNETS
SWITCHES AND
VOLTAGE REGULATORS
Manufacturing (page V-l)
Processing (page V-l)
Distribution in Commerce (Sale of Electromagnets, Switches, and
Voltage Regulators) (page V-2)
Exemptions to Manufacture, Process, and Distribute PCBs in
Commerce (page V-3)
Marking/Labeling (page V-4)
Phaseout Requirements (page V-4)
Use Conditions (page V-4)
Servicing and Reclassification Conditions (page V-4)
Storage for Reuse (page V-8)
Storage for Disposal (page V-8)
Disposal (page V-9)
Recordkeeping (page V-10)
Spills (page V-ll)
-------
- ELECTROMAGNETS. SWITCHES, AND VOLTAGE REGULATORS -
Electromagnets are primarily used over conveyer belts to
remove iron from nonmagnetic commodities. Electromagnets
designed to contain PCBs are used in areas such as coal
mines, coal preparation plants, and coal-fired generating
stations.
Voltage regulators and switches (including sectionalizers
and motor starters) are used by electric utilities and
industry to control, transmit, and distribute electric power
efficiently. Almost all of this electrical equipment is
mineral oil-filled and not designed to contain PCB
dielectric fluid. However, many voltage regulators,
switches, and also electromagnets have become contaminated
with PCBs through historic maintenance and servicing
activities. In addition, voltage regulators are
particularly susceptible to PCB contamination as they often
contain a small PCB starter capacitor which, if it leaks or
ruptures, is likely to contaminate the regulator's mineral
oil dielectric fluid.
Electromagnets, switches, and voltage regulators which
contain mineral oil dielectric fluid are not required to be
tested for PCBs. It is very important to note, however,
that oil-filled electromagnets, switches, and voltage
regulators, whose PCB concentration is unknown, must be
assumed to be PCB-Contaminated Electrical Equipment (50-499
ppm) and must be treated as such. This "assumption rule"
effectively applies to all regulatory requirements relating
to the equipment including: use and servicing, leaks and
spills, sale for reuse, storage for disposal, and disposal.
MANUFACTURING
The manufacture of PCBs, regardless of concentration, for
use in electromagnets, switches, and voltage regulators is
prohibited without an EPA exemption [761.20(b)].
PROCESSING
The processing of PCBs, 50 ppm or greater, for use in
electromagnets, switches, or voltage regulators is
prohibited without an EPA exemption [761.20 (c)] . However,
PCBs at concentrations less than 50 ppm may be processed for
use in electromagnets, switches, and voltage regulators
(under specific conditions) in accordance with the
definition of "Excluded PCB Products" [761.3]. Also, PCBs
at any concentration may be processed (i.e., prepared and/or
V-l
-------
packaged for distribution in commerce) for purposes of
disposal [761.20(c)(2)].
DISTRIBUTION IN COMMERCE (Sale of Electromagnets. Switches.
and Voltage Regulators)
The distribution in commerce of PCBs, 50 ppm or greater, for
use in electromagnets, switches, and voltage regulators is
prohibited without an EPA exemption [761.20 (c)]. However,
PCBs at concentrations less than 50 ppm may be distributed
in commerce for use in electromagnets, switches, and voltage
regulators (under specific conditions) in accordance with
the definition of "Excluded PCB Products" [761.3]. Also,
PCBs at any concentration may be distributed in commerce for
purposes of disposal [761.20(c) (2)]. Disposal means the
termination of the useful life of the PCB or PCB-
contaminated electromagnet, switch, or voltage regulator.
The distribution in commerce (sale) of electromagnets,
switches, and voltage regulators which contain PCBs in
concentrations of 50 ppm or greater (known or assumed) for
purposes of reuse or resale is allowed provided:
• the unit was originally sold for use before
July 1, 1979;
• the unit is intact and nonleaking at the time of
sale; and
• no PCBs are introduced into the unit.
Ql: Does this mean that I can sell a PCB or PCB-contaminated
voltage regulator, switch, or electromagnet?
Al: Yes. If the equipment was originally sold for use before
July 1, 1979, and is now being sold for reuse or resale
(i.e., continued use). Also, the unit must be intact and
nonleaking. EPA recommends that the buyer be advised that
he is purchasing a PCB or PCB-contaminated unit.
Q2: What does intact and nonleaking mean?
A2: Intact and nonleaking means that the equipment is
structurally sound with all fluid intact and there are no
PCBs on the external surface of the equipment.
Q3: Can I sell drained PCB-contaminated voltage regulators
and/or switch carcasses (known or assumed 50-499 ppm) to a
rebuilder for reuse as parts in repair and remanufacturing
activities?
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A3: No. Selling drained (50-499 ppm) carcasses for reuse is an
unauthorized distribution in commerce of PCBs and is
prohibited without an EPA exemption. On the other hand,
non-PCB carcasses (less than 50 ppm) can be sold for reuse
(under specific conditions) in accordance with the
definition of "Excluded PCB Products" [761.3] .
Q4: Can I sell drained PCB-contaminated voltage regulators
and/or switch carcasses (known or assumed -50-499 ppm) to a
scrap or salvage dealer for metals recovery?
A4: Yes. The sale of drained (50-499 ppm) carcasses for
scrapping or salvaging is generally considered distribution
in commerce for purposes of disposal and is allowed with
certain limitations. To qualify as disposal, the scrapping
practice must be one which will "...terminate the useful
life of PCBs or PCB Items" [761.3]; or, in other words, will
destroy any residual PCBs found in the drained carcasses.
Salvaging aimed at reclamation of the metals found in the
case and coil generally constitutes disposal, because any
residual PCBs are destroyed by the high temperatures
employed in the smelting process. However, where salvaging
consists of disassembling the drained equipment to obtain
parts for reuse in other equipment, the useful life of the
equipment has not been fully terminated and thus is not
considered disposal. In sum, the scrapping/salvaging of 50-
499 ppm drained equipment is unregulated to the extent that:
(1) scrapping practices do not result in leaks, spills, or
other uncontrolled discharges of PCBs, and (2) any PCB-
contaminated components are not reintroduced into commerce.
EXEMPTIONS TO MANUFACTURE. PROCESS. AND DISTRIBUTE PCBs IN
COMMERCE
Exemptions to manufacture, process, and distribute in
commerce PCBs in electromagnets, switches, and voltage
regulators may be granted only by rulemaking on a case-by-
case basis. The EPA Administrator may set terms and
conditions for an exemption and may grant an exemption for
not more than one year. EPA interim procedural rules for
processing and distribution in commerce exemptions describe
the required content of processing and distribution in
commerce exemptions petitions and the procedures EPA follows
in rulemaking on exemption petitions. Those rules were
published in the Federal Register of May 31, 1979 (44 FR
31558) and are codified at 40 CFR 750.30 through 750.41.
V-3
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MARKING/LABELING
Marking/labeling of electromagnets, switches, and voltage
regulators, regardless of PCB concentration, is not
required.
PHASEOUT REQUIREMENTS
After October 1, 1985, the use and storage for reuse of any
PCB electromagnet (500 ppm or greater) which poses an
exposure risk to food or feed is prohibited [761.30(h)(1)].
It is the owner's responsibility to determine whether the
electromagnet poses an exposure risk to food or feed.
USE CONDITIONS
PCB and PCB-contaminated electromagnets, switches, and
voltage regulators may be used for the remainder of their
useful lives. No recorded maintenance inspections are
required for PCB or PCB-contaminated electromagnets,
switches, or voltage regulators.
SERVICING AND RECLASSIFICATION CONDITIONS
The processing of PCB and PCB-contaminated electromagnets,
switches, and voltage regulators is limited to servicing
activities. These servicing activities include: draining
and refilling, topping off, repairing, and retrofilling for
reclassification [761.30(h) (2)]. Note: In the Federal
Register of Novemeber 18, 1993 (58 FR 60970) EPA proposed
amendments to the reclassification provisions for this type
of equipment.
The processing and distribution in commerce of PCBs, 50 ppm
or greater, for purposes of servicing and repairing a
customer's equipment is prohibited without an EPA exemption
[761.30(h) (2) (vii)] . However, an exemption is not required
to service your own PCB or PCB-contaminated electromagnet,
switch, or voltage regulator with the PCB or PCB-
contaminated fluid you already own, in accordance with the
regulations. Also, you can service a customer's unit if you
use non-PCB or PCB-free fluid; and, you are allowed to
refill a customer's unit with the same fluid that came out
of the unit, regardless of PCB concentration.
The processing (servicing) for non-PCB electromagnets,
switches, and voltage regulators with non-PCB fluids and/or
components is allowed without restriction.
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A PCB electromagnet, switch, or voltage regulator may be
reclassified to a PCB-contaminated or non-PCB unit by
draining, refilling, and otherwise servicing the unit. In
order to reclassify, the unit's dielectric fluid must
contain less than 500 ppm PCB (for conversion to PCB-
contaminated level) or less than 50 ppm PCB (for conversion
to non-PCB level) after a minimum of 3 months of in-service
use subsequent to the last servicing conducted for the
purposes of reducing the PCB concentration in the unit. In-
service means that the unit is used electrically under
loaded conditions [761.30(h)(2)(v)].
The following conditions also apply to service activities:
• Removing the coil from PCB electromagnets,
switches, or voltage regulators (500 ppm or
greater) is prohibited [761.30(h)(2)(i)].
• PCB-contaminated electromagnets, switches, and
voltage regulators may be serviced (including
rebuilding) only with dielectric fluid containing
less than 500 ppm PCB [761.30(h) (2) (ii)] .
• PCBs, 50 ppm or greater, removed during servicing
must be either reused as dielectric fluid or
disposed of in accordance with EPA requirements
[761.30(h) (2) (iii)] .
• PCBs from PCB electromagnets, switches, and
voltage regulators must not be mixed with or added
to dielectric fluid from PCB-contaminated
electromagnets, switches, and voltage regulators
[761.30(h)(2)(iii)].
• If dielectric fluid containing less than 500 ppm
PCBs is mixed with fluid containing 500 ppm or
greater PCBs, then the resulting mixture must not
be used as dielectric fluid in any electrical
equipment. The entire mixture must be considered
to be greater than 500 ppm PCBs and must be
disposed of in an incinerator that meets EPA
requirements [761.30(h)(2)(iv)].
• Any dielectric fluid containing 50 ppm or greater
PCBs used for servicing electromagnets, switches,
or voltage regulators must be stored in accordance
with the storage for disposal requirements [761.30
(h) (2) (vi)] .
Q5: Is an electromagnet, switch, or voltage regulator required
to reach 50° Centigrade during the 90-day in-service period
for proper reclassification?
V-5
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A5: No. Unlike transformers, there is no 50° Centigrade
requirement for reclassification of these types of equipment
[761.30(h)(2)(v)].
Q6: Do electromagnets, switches, and voltage regulators have to
be tested to determine their PCB concentration? If not, how
can I determine the equipment's classification?
A6: The regulations do not require that these types of equipment
be tested to determine the PCB concentration in their fluid.
However, in the absence of a test, certain assumptions
should be made about the equipment. For example, if the
nameplate indicates that the equipment contains PCB
dielectric fluid, or, if there is any reason to believe that
the equipment at one time contained PCB dielectric fluid,
or, if there is no nameplate on the equipment, then the
equipment must be assumed to be PCB (500 ppm or greater).
Electromagnets, switches, and voltage regulators which
contain mineral oil dielectric fluid and whose PCB
concentration is unknown, must, be assumed to be PCB-
Contaminated Electrical Equipment (50-499 ppm) and must be
treated as such. These "assumption rules" effectively apply
to all regulatory requirements relating to the equipment
including: use and servicing, leaks and spills, sale for
reuse, storage for disposal, and disposal.
Q7: Can screening tests, such as Clor-n-Oil™, be used to
determine the PCB concentration of an electromagnet, switch,
or voltage regulator? If so, can "Certified Non-PCB" labels
be used to classify electromagnets, switches, or voltage
regulators based upon a screen test?
A7: Currently, the regulations do not require that any
particular testing method be utilized when determining the
PCB concentration in electromagnets, switches, or voltage
regulators. However, owners of these types of equipment
should prudently scrutinize PCB testing options, as there
are significant differences in the integrity and accuracy of
various testing methods. It should be noted that, in most
situations, EPA will utilize laboratory gas-chromatography
(GC) testing to determine PCB concentrations during facility
inspections. EPA recommends that owners of electrical
equipment choose testing methods, and practice sampling
procedures, which are analytically accurate, reproducible,
assure quality control, and are certifiable. EPA does not
recognize the results of field screening test kits.
The use of non-PCB labels is unregulated by EPA. That is to
say, there are no prohibitions or requirements to place non-
PCB labels on electromagnets, switches, or voltage
regulators. However, if non-PCB labels are used to indicate
the classification of equipment, then owners should be able
V-6
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to provide documentation such as test results or
manufacturer's letters along with historic service records
which will substantiate the non-PCB classification. A
criminal action could be persued for someone intentionally
using non-PCB labels on known or assumed PCB Items.
Q8: Can I batch test oil samples from several electromagnets,
switches, and/or voltage regulators and classify each unit
based upon one test result?
A8: The only place in the regulations where "batch testing" is
specifically allowed is under testing procedures for
disposal of PCBs [761.60(g) ] . However, batch testing to
classify equipment for continued use of PCBs is also
allowable provided that dilution does not take place. That
is, mineral oil that is assumed or known to contain 50 ppm
or greater PCBs must not be mixed with mineral oil that is
known or assumed to contain less than 50 ppm PCBs to reduce
the concentration of PCBs in the batch. It should also be
noted that while batch testing is allowed, it does not
relieve the owner from any regulatory requirements if an
individual unit unknowingly contains a higher concentration
of PCBs than was detected in the batch test.
Q9: Many mineral oil-filled voltage regulators and switches have
no information on their nameplate indicating that they do,
in fact, contain mineral oil dielectric fluid. Without this
nameplate information, am I required to assume that these
units are "PCB" classification (500 ppm or greater)?
A9: The regulations allow "oil-filled", electrical equipment
whose PCB concentration is unknown to be assumed less than
500 ppm (PCB-contaminated, 50-499 ppm). EPA has received
numerous comments from the electric utility industry and
others indicating that significant numbers of mineral oil-
filled voltage regulators and switches have no nameplate
information about their dielectric fluid. In the absence of
this information, one could interpret the regulations to
require that these units be assumed "PCB" instead of "PCB-
contaminated." However, almost all voltage regulators and
switches are, in fact, mineral oil-filled and not designed
to use PCB dielectric fluid. Consequently, it is reasonable
to assume that voltage regulators and switches are "oil-
filled" unless: (1) the nameplate indicates that the
equipment contains PCB dielectric fluid, or (2) if there is
any reason to believe that the equipment at one time
contained PCB dielectric fluid.
V-7
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STORAGE FOR REUSE
Voltage regulators and switches containing PCBs at any
concentration may be stored for reuse. There are no time
limitations on this storage; however, voltage regulators
and/or switches (50 ppm or greater) which are stored for
reuse must be in a condition suitable for reuse. These
units are considered by EPA to be in-service for purposes of
the regulations.
Electromagnets containing PCBs at any concentration may also
be stored for reuse indefinitely provided that they are in a
condition suitable for reuse; except that, the storage for
reuse of a PCB electromagnet which poses an exposure risk to
food or feed is prohibited after October 1, 1985.
Q10: How long can I keep a "burned-out" or "nonfunctional"
electromagnet, switch, or voltage regulator in storage for
reuse if I plan on repairing it and using it later?
A10: EPA does not require nonfunctional electromagnets, switches,
or voltage regulators (regardless of PCB concentration) to
be placed into "storage for disposal" if you intend to
repair and reuse the item. However, EPA may have grounds to
enforce against lengthy "storage for reuse" of equipment
which is not reasonably expected to be placed back into
service. In other words, while there are no explicit
requirements for, or restrictions on, the storage for reuse
of equipment which can be repaired, the owner should be able
to demonstrate good faith compliance with the intent of the
storage for disposal requirements and complete any required
servicing or repairs within the same one year limitation
associated with PCB disposal.
STORAGE FOR DISPOSAL
All PCB and PCB-contaminated electromagnets, switches, and
voltage regulators must be dated when placed into storage
for disposal [761.65(c)(8)] and must be removed from storage
and disposed of within one year [761.65(a)].
The facility used to store PCB and PCB-contaminated
electromagnets, switches, and/or voltage regulators must
comply with the "storage for disposal" requirements [761.65
(b)(1)]. See the chapter on "PCB Storage Requirements" for
specific requirements.
Nonleaking PCB and PCB-contaminated electromagnets,
switches, and voltage regulators may be stored temporarily
by a generator in an area that does not comply with the
requirements for a PCB storage facility for up to 30 days
V-8
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from the date of their removal from service for disposal
provided that a notation is attached to each unit indicating
the dates the equipment was removed from service
[761.65(c) (1)], and placed into storage for disposal
[761.65(c)(8)].
Leaking PCB and PCB-contaminated electromagnets, switches,
and voltage regulators which are placed in appropriate PCB
Containers [761.65 (c) (6)] with sufficient sorbent materials
to absorb any liquid PCBs, may also be temporarily stored
for up to 30 days provided that a notation is attached to
the container indicating the dates the equipment was removed
from service [761.65 (c) (1) (ii)], and placed into storage for
disposal [761.65(c)(8)]. Each container or drum used to
store leaking PCB Items must be marked in accordance with
EPA marking and labeling requirements [761.40 (a) (1)] .
Nonleaking and structurally undamaged PCB-contaminated
electromagnets, switches, and voltage regulators that have
not been drained of free-flowing dielectric fluid may also
be stored temporarily on pallets next to a PCB storage
facility which meets the requirements for storage for
disposal. This type of storage is permitted only when the
storage facility has immediately available unfilled storage
space equal to 10 percent of the volume of the equipment
stored outside the facility. The equipment stored outside
the facility must be inspected for leaks weekly
[761.65(c) (2)], and a notation must be attached to each unit
indicating the dates the equipment was removed from service
[761.65 (c) (1)] and placed into storage for disposal [761.65
(c) (8)] .
DISPOSAL
PCB electromagnets, switches, and voltage regulators must be
disposed of as follows:
• In an incinerator that complies with 40 CFR
761.70.
• In a chemical waste landfill provided that all
free-flowing liquid PCBs have been thoroughly
drained from the equipment. The PCB liquids that
are removed (including any flushing solvent) must
be disposed of in an incinerator that complies
with 40 CFR 761.70, or by an alternative EPA
approved and permitted method in accordance with
761.60 (e) .
PCB-contaminated electromagnets, switches, and voltage
regulators must be disposed of as follows:
V-9
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• By draining all free-flowing liquid from the
equipment and disposing of the liquid in an
incinerator that complies with 40 CFR 761.70, in a
chemical waste landfill that complies with 761.75,
in an approved high efficiency boiler that
complies with 761.60(a) (2) (iii), or by an
alternative EPA approved and permitted method that
complies with 761.60(e). The disposal of the
drained equipment carcass is not regulated [761.60
(b) (5) (ii)] . (See Distribution in Commerce.)
Non-PCB electromagnets, switches, and voltage regulators
(less than 50 ppm PCB) may be disposed of with the following
considerations:
• There are no PCB disposal requirements for non-PCB
electromagnets, switches, and voltage regulators.
However, certain reuse restrictions apply to the
less than 50 ppm PCB fluid. Waste oil with any
detectable concentration of PCBs cannot be used as
a sealant, coating, or dust control agent
[761.20(d)]; and also, can only be burned for
energy recovery in specific combustion facilities
described in 761.20(e)(1). See the Chapter XIII
on "PCB Disposal Requirements" for a detailed
discussion of the disposal of non-PCB waste oils.
Qll: Do PCB electromagnets, switches, and voltage regulators have
to be filled with a solvent for 18 hours and redrained
before transporting the carcass to a chemical waste
landfill?
All: No. Unlike PCB Transformers, there is no requirement to
fill and flush PCB electromagnets, switches, or voltage
regulators with solvent prior to disposal of the drained
carcass in a chemical waste landfill. However, owners of
PCB Equipment should take appropriate steps to insure that
all free-flowing liquid PCBs have been extracted from the
carcass.
RECORDKEEPING
Testing data, inventories, servicing and reclassification
records, spill reports, and disposal records should be
maintained for all PCB and PCB-contaminated electromagnets,
switches, and voltage regulators. Under specific quantity
guidelines, [761.180(a)] records are required to be kept to
form the basis of an Annual Document Log and Annual Record
which must be prepared each year and maintained for at least
3 years after the facility ceases using or storing PCBs and
PCB Items. Disposers and commercial storers of all PCB and
V-10
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PCB-contaminated electromagnets, switches, and voltage
regulators are required to keep records pursuant to
761.180(b). See Chapter XV, "Recordkeeping and Reporting"
for a detailed discussion of other recordkeeping
requirements.
SPILLS
Spills, leaks, and other uncontrolled discharges where the
release results in any quantity of PCBs running off or about
to run off the external surface of a PCB or PCB-contaminated
electromagnet, switch, or voltage regulator is considered
improper disposal of PCBs. The PCB Spill Cleanup Policy
provides specific cleanup measures which, if followed
explicitly, create a presumption against enforcement for
penalties or further cleanup. See the chapter on "PCB Spill
Cleanup Policy" for specific measures.
PCB spills involving 1 Ib. or more of PCBs (generally 1 pint
of Askarel) must be reported to the National Response Center
(NRC) at (800) 424-8802. Spills involving 10 Ibs. or more
of PCBs (generally 1 gallon of Askarel) must be reported to
the appropriate Regional EPA office. Failure to notify the
NRC under CERCLA can lead to penalties under Section 109 or,
under Section 103, criminal fines and imprisonment. Any
spill should be reported when people or animals can come
into direct and uncontrolled contact with PCBs.
Measures must immediately be taken to control the spread of
the spill. Any threats to water should be given highest
priority. Water and other complicated spills should be
cleaned up by trained personnel to levels set by the
appropriate EPA Regional Administrator. Organizations that
frequently handle PCBs should develop spill contingency
plans and conduct training for dealing with spills.
Once a spill is contained, cleanup measures can begin. EPA
requires cleanup of PCBs to different levels depending on
spill location, the potential for exposure to residual PCBs
remaining after cleanup, the concentration of PCBs initially
spilled, and the nature and size of the population
potentially at risk of exposure. While the PCB Spill
Cleanup Policy applies to the majority of situations,
exceptional circumstances may require additional cleanup at
the discretion of the EPA regional office. A detailed
description of the specific reporting, cleanup,
recordkeeping, and post-cleanup sampling requirements is
found in the chapter on "PCB Spill Cleanup Policy."
Other minor weeping from PCB or PCB-contaminated equipment
capacitor bushings and seams, not covered by the spill
V-ll
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policy, is still considered improper disposal of PCBs and
compels responsible parties to take actions to rectify the
exposure of humans and the environment to PCBs.
Q12: Do records and/or spill reports have to be kept for all PCB
or PCB-contaminated electromagnets, switches, or voltage
regulators which rupture?
A12: The PCB Spill Cleanup Policy specifies certain recordkeeping
when a PCB or PCB-contaminated electromagnet, switch, or
voltage regulator ruptures or spills. See the chapter on
"PCB Spill Cleanup Policy" for specific spill recordkeeping.
V-12
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CHAPTER VI
CIRCUIT BREAKERS
RECLOSERS AND CABLE
Manufacturing (page VI-1)
Processing (page VI-1)
Distribution in Commerce (Sale of Circuit Breakers, Reclosers,
and Cable) (page VI-2)
Exemptions to Manufacture, Process, and Distribute PCBs in
Commerce (page VI-3)
Marking/Labeling (page VI-3)
Use Conditions (page VI-4)
Servicing and Reclassification Conditions (page VI-4)
Storage for Reuse (page VI-7)
Storage for Disposal (page VI-7)
Disposal (page VI^8)
Recordkeeping (page VI-9)
Spills (page VI-10)
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- CIRCUIT BREAKERS. RECLOSERS. AND CABLE -
Circuit breakers, reclosers, and cable are used primarily by
electric utilities in the transmission and distribution of
eiectric power to protect other equipment in the electric
power system from damage caused by electrical faults.
Circuit breakers, reclosers, and cable are types of oil-
filled electrical equipment generally not designed to
contain PCBs. However, available data indicate that a small
percentage of this electrical equipment does in fact contain
PCBs resulting from past servicing and manufacturing
practices.
One very important difference between circuit breakers,
reclosers, and cable is that they are not required to be
"assumed" PCB-Contaminated Electrical Equipment as are other
untested, oil-filled units such as transformers and voltage
regulators whose PCB concentration is unknown. That is to
say, circuit breakers, reclosers, and cable have
specifically been excluded from the "Assumption Rule"
[761.3]. It is important to note, however, that if circuit
breakers, reclosers, or cable are 50 ppm or greater PCBs,
then all regulatory requirements relating to the equipment
including leaks and spills, storage for disposal, and
disposal apply.
MANUFACTURING
The manufacture of PCBs, regardless of concentration, for
use in circuit breakers, reclosers, and cable is prohibited
without an EPA exemption [761.20(b)].
PROCESSING
The processing of PCBs, 50 ppm or greater, for use in
circuit breakers, reclosers, or cable is prohibited without
an EPA exemption [761.20(c) ] . However, PCBs at
concentrations less than 50 ppm may be processed for use in
circuit breakers, reclosers, and cable (under specific
conditions) in accordance with the definition of "Excluded
PCB Products" [761.3]. Also, PCBs at any concentration may
be processed (i.e., prepared and/or packaged for
distribution in commerce) for purposes of disposal
[761.20(c)(2)].
VI-1
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DISTRIBUTION IN COMMERCE (Sale of Circuit Breakers.
Reclosers, and Cable)
The distribution in commerce of PCBs, 50 ppm or greater, for
use in circuit breakers, reclosers, and cable is prohibited
without an EPA exemption [761.20(c) ] . However, PCBs at
concentrations less than 50 ppm may be distributed in
commerce for use in circuit breakers, reclosers, and cable
(under specific conditions) in accordance -with the
definition of "Excluded PCB Products" [761.3]. Also, PCBs
at any concentration may be distributed in commerce for
purpose of disposal [761.20(c)(2)]. Disposal, means the
termination of the useful life of the PCB or PCB-
contaminated circuit breaker, recloser, or cable.
The distribution in commerce (sale) of circuit breakers,
reclosers, and cable which already contain PCBs in
concentrations of 50 ppm or greater for purposes of reuse is
allowed provided:
• the unit was originally sold for use before
July 1, 1979;
• the unit is intact and nonleaking at the time of
sale; and
• no PCBs are introduced into the unit.
Ql: Does this mean I can sell a PCB or PCB-contaminated circuit
breaker, recloser, or cable?
Al: Yes. If the equipment was originally sold for use before
July 1, 1979, and is now being sold for reuse (i.e.,
continued use). Also, the unit must be intact and
nonleaking. EPA recommends that the buyer be advised that
he is purchasing a PCB or PCB-contaminated unit.
Q2: What does intact and nonleaking mean?
A2: Intact and nonleaking means that the equipment is
structurally sound with all fluid intact and there are no
PCBs on the surface of the equipment.
Q3: Can I sell drained PCB-contaminated circuit breakers and/or
recloser carcasses to a rebuilder for reuse as parts in
repair and remanufacturing activities?
A3: No. Selling drained 50-499 ppm carcasses for reuse as parts
is an unauthorized distribution in commerce of PCBs and is
prohibited without an EPA exemption. On the other hand,
non-PCB carcasses (less than 50 ppm) can be sold for reuse
VI-2
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(under specific conditions) in accordance with the
definition of "Excluded PCB Products" [761.3].
Q4: Can I sell drained PCB-contaminated circuit breakers and/or
recloser carcasses to a scrap or salvage dealer for metals
recovery?
A4: Yes. The sale of drained 50-499 ppm carcasses for scrapping
or salvaging is generally considered distribution in
commerce for purposes of disposal and is allowed with
certain limitations. To qualify as disposal, the scrapping
practice must be one which will "...terminate the useful
life of PCBs or PCB Items" [761.3]; or, in other words, will
destroy any residual PCBs found in the drained carcasses.
Salvaging aimed at reclamation of the metals found in the
case and coil generally constitutes disposal, because any
residual PCBs are destroyed by the high temperatures
employed in the smelting process. However, where salvaging
consists of disassembling the drained equipment to obtain
parts for reuse in other equipment, the useful life of the
equipment has not been fully terminated and thus is not
considered disposal. In sum, the scrapping/salvaging of 50-
499 ppm drained equipment is unregulated to the extent that:
(1) scrapping practices do not result in leaks, spills, or
other uncontrolled discharges of PCBs, and (2) any PCB-
contaminated components are not reintroduced into commerce.
EXEMPTIONS TO MANUFACTURE. PROCESS. AND DISTRIBUTE PCBs IN
COMMERCE
Exemptions to manufacture^ process, and distribute in
commerce PCBs in circuit breakers, reclosers, and cable may
be granted only by rulemaking on a case-by-case basis. The
EPA Administrator may set terms and conditions for an
exemption and may grant an exemption for not more than one
year. EPA interim procedural rules for processing and
distribution in commerce exemptions describe the required
content of processing and distribution in commerce
exemptions petitions and the procedures EPA follows in
rulemaking on exemption petitions. Those rules were
published in the Federal Register of May 31, 1979 (44 FR
31558) and are codified at 40 CFR 750.30 through 750.41.
MARKING/LABELING
Marking/labeling of circuit breakers, reclosers, and cable,
regardless of PCB concentration, is not required.
VI-3
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USE CONDITIONS
PCB and PCB-contaminated circuit breakers, reclosers, and
cable may be used for the remainder of their useful lives.
No recorded maintenance inspections are required for PCB or
PCB-contaminated circuit breakers, reclosers, or cable.
However, ruptures, leaks, and other uncontrolled discharges
from PCB or PCB-contaminated circuit breakers, reclosers,
and cable are considered improper disposal of PCBs.
SERVICING AND RECLASSIFICATION CONDITIONS
Processing of PCB and PCB-contaminated circuit breakers,
reclosers, and cable is limited to servicing activities.
These servicing activities include: draining and refilling,
topping off, repairing, and retrofilling for
reclassification [761.30(m)(1)]. Circuit breakers,
reclosers, and cable may be serviced (including rebuilding)
only with dielectric fluid containing less than 50 ppm PCB.
A PCB circuit breaker or recloser may be reclassified to a
PCB-contaminated or non-PCB unit by draining, refilling, and
otherwise servicing the unit. In order to reclassify, the
unit's dielectric fluid must contain less than 500 ppm PCB
(for conversion to PCB-contaminated level) or less than 50
ppm PCB (for conversion to non-PCB level) after a minimum of
3 months of -in-service use subsequent to the last servicing
conducted for the purposes of reducing the PCB concentration
in the unit. In-service means that the unit is used
electrically under loaded conditions [761.30(m)(1)].
t
The following conditions also apply to service activities:
• Removing the coil from PCB circuit breakers or
reclosers (500 ppm or greater) is prohibited
[761.30(m)(1)].
• PCBs from PCB circuit breakers, reclosers, and
cable must not be mixed with or added to
dielectric fluid from PCB-contaminated circuit
breakers, reclosers, and cable [761.30(m)(1)].
• If dielectric fluid containing less than 500 ppm
PCBs is mixed with fluid containing 500 ppm or
greater PCBs, then the resulting mixture must not
be used as dielectric fluid in any electrical
equipment. The entire mixture must be considered
to be greater than 500 ppm PCBs and must be
disposed of in an incinerator that meets
EPA requirements [761.30(m) (1)], or by an
alternative EPA approved and permitted method.
VI-4
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• Mineral oil from circuit breakers, reclosers, and
cable must not be mixed with mineral oil from
other electrical equipment, such as transformers
and voltage regulators, whose PCB concentration is
unknown. If dielectric fluid from untested, oil-
filled circuit breakers, reclosers, or cable is
collected in a common container with dielectric
fluid from other oil-filled electrical equipment,
the entire contents of the container must be
treated as PCBs at a concentration of at least 50
ppm, unless all of the fluid from the other oil-
filled electrical equipment has been tested and
shown to contain less than 50 ppm PCBs
[761.60(g)(1)(i)].
Q5: Our facility periodically drains oil-filled circuit
breakers, reclosers, and cable, brought in for servicing,
into drums and/or bulk tanks. From time to time, an
untested transformer or voltage regulator is also brought in
for servicing and the oil from these units is drained into
the same drums and/or storage tanks. These drums/tanks are
always batch tested for PCBs and the contents are then
reused in servicing oil-filled circuit breakers, reclosers,
and cable, or disposed of based upon the PCB test result.
Is there anything wrong with this type of mixing and batch
testing?
A5: Yes. What you have in this scenario is unauthorized
"dilution" of PCBs. The regulations do allow mixing and
batch testing under certain conditions. However, the mixing
of untested oil from circuit breakers, reclosure, and cable
with untested transformer and regulator oil for batch
testing is prohibited. If these dielectric fluids are
collected in a common container, then the entire mixture
must be treated as 50 ppm or greater PCBs even if a batch
test resulted in less than 50 ppm. Consequently, the
mixture could not be reused in servicing oil-filled circuit
breakers, reclosers, and cable, and the entire mixture must
be stored for disposal and disposed of as.containing PCBs at
a concentration of 50 ppm or greater.
Q6: Is a circuit breaker or recloser required to reach 50°
Centigrade during the 90-day in-service period for proper
reclassification?
A6: No. Unlike transformers, there is no 50° Centigrade
requirement for reclassification of these types of equipment
[761.30(m)(1)].
VI-5
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Q7: Can screening tests, such as Clor-n-Oil™, be used to
determine the PCB concentration of circuit breakers,
reclosers, or cable? If so, can "certified non-PCB" labels
be used to classify these units based upon a screen test?
A7: Currently, the regulations do not require that any
particular testing method be utilized when determining the
PCB concentration in circuit breakers, reclosers, or cable.
However, owners of these types of equipment should prudently
scrutinize PCB testing options, as there are significant
differences in the integrity and accuracy of various testing
methods. It should be noted that, in most situations, EPA
will utilize laboratory gas-chromatography (GC) testing to
determine PCB concentrations during facility inspections.
EPA recommends that owners of electrical equipment choose
testing methods, and practice sampling procedures, which are
analytically accurate, reproducible, assure quality control,
and are certifiable. EPA does not recognize results of
field screening test kits for classifying PCB equipment.
The use of non-PCB labels is unregulated by EPA. That is to
say, there are no prohibitions or requirements to place non-
PCB labels on circuit breakers, reclosers, or cable.
However, if non-PCB labels are used to indicate the
classification of equipment, then owners should be able to
provide documentation such as test results or manufacturer's
letters along with historic service records which will
substantiate the non-PCB classification. Criminal action
could be pursued for someone intentionally using non-PCB
labels on PCB or PCB-contaminated items.
Q8: Can I batch test oil samples from several circuit breakers
or reclosers and classify each unit based upon one test
result?
A8: The only place in the regulations where "batch testing" is
specifically allowed is under testing procedures for
disposal of PCBs [761.60(g)]. However, batch testing to
classify equipment for continued use of PCBs is also
allowable provided that dilution does not take place. That
is, mineral oil that is assumed or known to contain 50 ppm
or greater PCBs must not be mixed with mineral oil that is
known or assumed to contain less than 50 ppm PCBs to reduce
the concentration of PCBs in the batch. It should also be
noted that while batch testing is allowed, it does not
relieve the owner from any regulatory requirements if an
individual unit is discovered to contain a higher
concentration of PCBs than was detected in the batch test.
VI-6
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STORAGE FOR REUSE
Circuit breakers, reclosers, and cable containing PCBs at
any concentration may be stored for reuse. There are no
time limitations on this storage; however, circuit breakers,
reclosers, and cable (50 ppm or greater) which are stored
for reuse must be in condition suitable for reuse. These
units are considered by EPA to be in-service for purposes of
the regulations.
*•
Q9: How long can I keep a "burned-out" or "nonfunctional" PCB or
PCB-contaminated circuit breaker or recloser in storage for
reuse if I plan on repairing it and using it later?
A9: It is not required that nonfunctional equipment be placed
into "storage for disposal" if there is a possibility of
repair. However, EPA may have grounds to enforce against
lengthy "storage for reuse" of equipment which is not
reasonably expected to be placed back into service. In
other words, while there are no explicit requirements for,
or restrictions on, the storage for reuse of equipment which
can and may be repaired, the owner should be able to
demonstrate good faith compliance with the intent of the
storage for disposal requirements and complete any required
servicing and/or repairs within a reasonable timeframe.
STORAGE FOR DISPOSAL
All PCBs and PCB-contaminated circuit breakers, reclosers,
and cable must be dated when placed into storage for
disposal [761.65(c)(8)] and must be removed from storage and
disposed of within one year [761.65(a)].
The facility used to store PCB and PCB-contaminated circuit
breakers, reclosers, and/or cable must comply with the
"storage for disposal" requirements [761.65(b)(1)]. See the
chapter on "PCB Storage Facilities" for specific
requirements.
Nonleaking PCB and PCB-contaminated circuit breakers,
reclosers, and cable may be stored temporarily by a
generator in an area that does not comply with the
requirements for a PCB storage facility for up to 30 days
from the date of their removal from service for disposal
provided that a notation is attached to each unit indicating
the dates the equipment was removed from service
[761.65 (c) (1) (i)], and placed into storage for disposal
[761.65(c) (8)] .
Leaking PCB and PCB-contaminated circuit breakers,
reclosers, and cable which are placed in appropriate PCB
VI-7
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Containers [761.65(c)(6)] with sufficient sorbent materials
to absorb any liquid PCBs, may also be temporarily stored by
a generator for up to 30 days provided that a notation is
attached to the container indicating the dates the equipment
was removed from service [761.65(c)(1)], and placed into
storage for disposal [761.65(c)(8)]. Each container or drum
used to store leaking PCB Items must be marked in accordance
with EPA marking and labeling requirements [761.40(a)(1)].
Nonleaking and structurally undamaged PCB-contaminated
circuit breakers, reclosers, and cable that have not been
drained of free-flowing dielectric fluid may be stored
temporarily on pallets next to a PCB storage facility which
meets the requirements for storage for disposal. This type
of storage is permitted only when the storage facility has
immediately available unfilled storage space equal to 10
percent of the volume of the equipment stored outside the
facility. The equipment stored outside the facility must be
inspected for leaks weekly [761.65(c)(2)], and a notation
must be attached to each unit indicating the dates the
equipment was removed from service [761.65(c) (1)] and placed
into storage for disposal [761.65 (c)(8)]. If a weekly
visual inspection reveals a piece of equipment is leaking,
having the required available space within the storage area
allows immediate containment of the leak by moving the
equipment into the storage area.
DISPOSAL
PCB circuit breakers, reclosers, and cable must be disposed
of as follows:
• In an incinerator that complies with 40 CFR
761.70.
• In a chemical waste landfill provided that all
free-flowing liquid PCBs have been thoroughly
drained from the equipment. The PCB liquids that
are removed (including any flushing solvent) must
be disposed of in an incinerator that complies
with 40 CFR 761.70, or by an alternative EPA
approved and permitted method in accordance with
761.60(e).
PCB-contaminated circuit breakers, reclosers, and cable must
be disposed of as follows:
• By draining all free-flowing liquid from the
equipment and disposing of the liquid in an
incinerator that complies with 40 CFR 761.70, in a
chemical waste landfill that complies with 761.75,
in an approved high efficiency boiler that
complies with 761.60(a) (2) (iii), or by an
VI-8
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alternative EPA approved and permitted method that
complies with 761.60(e). The disposal of the
drained equipment carcass is not regulated [761.60
(b) (5) (ii)] ; however, the sale or trade of the
drained carcass for reuse as parts or in
rebuilding is regulated. (See Distribution in
Commerce.)
Non-PCB circuit breakers, reclosers, and cable (less than 50
ppm PCB) may be disposed of with the following
considerations:
• There are no PCB disposal requirements for non-PCB
circuit breakers, reclosers, and cable. However,
certain reuse restrictions apply to the less than
50 ppm PCB fluid. Waste oil with any detectable
concentration of PCBs cannot be used as a sealant,
coating, or dust control agent [761.20(d)]; and
also, can only be burned for energy recovery in
specific combustion facilities described in
761.20 (e) (1) . See the chapter on "PCB Disposal
Requirements" for a detailed discussion of the
disposal of non-PCB waste oils.
Q10: Do PCB circuit breakers, reclosers, and cable have to be
filled with a solvent for 18 hours and redrained before
transporting the carcass to a chemical waste landfill?
A10: No. Unlike PCB Transformers, there is no requirement to
fill and flush PCB circuit breakers, reclosers, and cable
with solvent prior to disposal of the drained carcass in a
chemical waste landfill. However, owners of PCB Equipment
should take appropriate steps to insure that all free-
flowing liquid PCBs have been extracted from the carcass.
RECORDKEEPING
Testing data, inventories, servicing and reclassification
records, spill reports, and disposal records should be
maintained for all PCB and PCB-contaminated circuit
breakers, reclosers, and cable. Under specific quantity
guidelines, [761.180(a)] records are required to be kept to
form the basis of an Annual Document Log and Annual Record
which must be prepared each year and maintained for at least
3 years after the facility ceases using or storing PCBs and
PCB Items. See Chapter XV, "Recordkeeping and Reporting"
for a detailed discussion of other recordkeeping
requirements.
VI-9
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SPILLS
Spills, leaks, and other uncontrolled discharges where the
release results in any quantity of PCBs running off or about
to run off the external surface of a PCB or PCB-contaminated
circuit breaker, recloser, or cable is considered improper
disposal of PCBs. The PCB Spill Cleanup Policy provides
specific cleanup measures which, if followed explicitly,
create a presumption against enforcement for penalties or
further cleanup. See the chapter on "PCB Spill Cleanup
Policy" for specific measures.
PCB spills involving 1 Ib. or more of PCBs (generally 1 pint
of Askarel) must be reported to the National Response Center
(NRC) at (800)424-8802. Spills involving 10 Ibs. or more of
PCBs must be reported to the appropriate regional EPA
office. Failure to notify the NRC under CERCLA can lead to
civil penalties under Section 109 or, under Section 103,
criminal fines and imprisonment. Any spill should be
reported when people or animals can come into direct and
uncontrolled contact with PCBs.
Measures must immediately be taken to control the spread of
the spill. Any threats to water should be given highest
priority. Water and other complicated spills should be
cleaned up by trained personnel to levels set by the
appropriate EPA Regional Administrator. Organizations that
frequently handle PCBs should develop spill contingency
plans and conduct training for dealing with spills.
Once a spill is contained, cleanup measures can begin. EPA
requires cleanup of PCBs to different levels depending on
spill location, the potential for exposure to residual PCBs
remaining after cleanup, the concentration of PCBs initially
spilled, and the nature and size of the population
potentially at risk of exposure. While the PCB Spill
Cleanup Policy applies to the majority of situations,
exceptional circumstances may require additional cleanup at
the discretion of the EPA regional office. A detailed
description of the specific reporting, cleanup,
recordkeeping, and postcleanup sampling requirements is
found in the chapter on "PCB Spill Cleanup Policy."
Other minor weeping from PCB or PCB-contaminated equipment
bushings and seams not covered by the spill policy is still
considered improper disposal of PCBs and compels responsible
parties to take actions to rectify the exposure of humans
and the environment to PCBs.
Qll: Do records and/or spill reports have to be kept for all PCB
or PCB-contaminated circuit breakers, reclosers, or cable
which rupture and/or spill?
VI-10
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All: The PCB Spill Cleanup Policy specifies specific
recordkeeping when a PCB or PCB-contaminated circuit
breaker, recloser, or cable ruptures or spills. See the
chapter on "PCB Spill Cleanup Policy" for specific spill
recordkeeping.
VI-ll
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CHAPTER VII
RESEARCH AND DEVELOPMENT
Manufacturing (page VII-1)
Processing (page VII-1)
Distribution in Commerce (page VII-1)
Exporting (page VII-1)
Exemptions to Manufacture, Process, Distribute in
Commerce, and Export PCBs (page VII-2)
Use Conditions (page VII-2)
Marking/Labeling (page VII-3)
Storage for Disposal (page VII-4)
Disposal (page VII-4)
Recordkeeping and Reporting Requirements (page VII-5)
Spills (page VII-5)
-------
-RESEARCH AND DEVELOPMENT-
PCBs are used in toxicological and environmental testing.
They are also used in analytical chemistry as "reference
standards" for the analysis of unknown compounds that may
contain PCBs.
EPA determined that there are no substitutes for PCBs for
the continuation of important health, environmental, and
analytical research and that substitutes for PCBs in these
applications will not be developed in the future.
Therefore, there is a unique need for exemptions to
manufacture, process, distribute in commerce, and export
PCBs in small quantities for research and development.
MANUFACTURING
The manufacture of PCBs for the purpose of research and
development is prohibited without an EPA exemption
[761.20(b)]. (Note: EPA has granted exemptions to
manufacture PCBs in small quantities for research and
development.)
PROCESSING
The processing of PCBs for the purpose of research and
development is prohibited without an EPA exemption
[761.20 (c)3 • (Note: EPA has granted exemptions to process
PCBs in small quantities for research and development.)
DISTRIBUTION IN COMMERCE
The distribution in commerce of PCBs for the purpose of
research and development is prohibited without an EPA
exemption [761.20 (c)] . (Note: EPA has granted exemptions
to distribute in commerce PCBs in small quantities for
research and development.)
EXPORTING
The export of PCBs for the purpose of research and
development is prohibited without an EPA exemption
[761.20(b)&(c)]. (Note: EPA has granted exemptions to
export PCBs in small quantities for research and
development.)
VII-1
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EXEMPTIONS TO MANUFACTURE. PROCESS. DISTRIBUTE IN COMMERCE.
AND EXPORT PCBs
Section 6(e)(3)(B) of TSCA provides that any person may
petition the Administrator for an exemption from the
prohibition against the manufacture, processing, and
distribution in commerce of PCBs. The Administrator may by
rule grant an exemption if the Administrator finds that " (i)
an unreasonable risk to health or the environment would not
result, and (ii) good faith efforts have been made to
develop a chemical substance which does not present an
unreasonable risk of injury to health or the environment and
which may be substituted for such polychlorinated biphenyl."
The Administrator may set terms and conditions for an
exemption and may grant an exemption for not more than one
year.
EPA's Interim Procedural Rules for Processing and
Distribution in Commerce Exemptions describe the required
content of processing and distribution in commerce exemption
petitions and the procedures EPA follows in rulemaking on
exemption petitions. Those rules were published in the
Federal Register of May 31, 1979 (44 FR 31514) and are
codified at 40 CFR 750.30 through 750.41.
The class exemption on processing and distribution in
commerce includes all persons or business entities which
process and distribute in commerce PCBs in accordance with
the definition of "small quantities for research and
development" [761.30 (j)] . EPA also places the following
terms and conditions on the class 'exemption:
• All processors and distributors must maintain
records of their PCB activities for a period of 5
years.
• Any person or company that expects to process or
distribute in commerce 100 grams (.22 Ib.) or more
PCBs for research and development in 1 year must
report to EPA and identify the sites of PCB
activities and the quantity of PCBs to be
processed and distributed in commerce.
USE CONDITIONS
PCBs may be used in small quantities for the purpose of
research and development indefinitely provided the use is in
accordance with the following definition:
• "Small Quantities for Research and Development"
means any quantity of PCBs (1) that is originally
VII-2
-------
packaged in one or more hermetically sealed
containers of a volume of no more than five (5.0)
milliliters, and (2) that is used only for
purposes of scientific experimentation or
analysis, or chemical research on, or analysis of
PCBs, but not for research or analysis for the
development of a PCB product.
As published in the Federal Register on March 30, 1983 (48
FR 13184), research and development on disposal methods
using PCBs constitutes disposal and is regulated using the
disposal section of the PCB regulations (40 CFR 761.60).
Failure to obtain prior approval from EPA to conduct
disposal research and development is a violation of the PCB
disposal regulations.
Ql: I have just received a package of PCBs for research and
development purposes. How should I store the hermetically
sealed containers until use?
Al: There are no storage requirements for hermetically sealed
packages of PCBs that will be used for research and
development. As long as the hermetically sealed containers
have not been opened, they may be stored for future use
indefinitely. However, once the seal has been broken on a
container, the small quantity of PCBs must be used for their
intended purpose in a timely fashion. Any residual PCB
wastes, including contaminated containers and lab
instruments, must be stored for disposal in accordance with
EPA requirements.
Q2: Is there a limit on the number of hermetically sealed 5
milliliter containers that can be used?
A2: No, one may use as many as necessary to conduct the research
and development activity.
MARKING/LABELING
All hermetically sealed containers containing small
quantities of PCBs for research and development must be
marked/labeled in accordance with EPA marking requirements
for PCB Containers [761.40(a) (1)] .
In addition, if sealed containers are stored in a package,
then the package must be marked/labeled in accordance with
EPA marking requirements for PCB Article Containers
[761.40(a)(9)].
VII-3
-------
STORAGE FOR DISPOSAL
Any PCB waste generated from the use of small quantities of
PCBs for research and development (i.e., contaminated
containers and lab instruments) must be stored for disposal
in a facility which complies with EPA storage for disposal
requirements [761.65(b) (1)] .
However, PCB waste from research and development can also be
stored temporarily by the generator for up to 30 days in an
area that does not comply with the requirements for a PCB
storage facility provided that the following conditions are
met:
• PCB waste must be placed in an appropriate PCB
Container/drum [761.65(c)(6)] with sufficient
sorbent materials to absorb any liquid PCBs.
• The PCB Container/drum must be marked/labeled in
accordance with EPA marking requirements
[761.40(a)(1)].
• A notation must be attached to the PCB
Container/drum indicating the date the first PCB
waste was placed into the container/drum for
disposal [761.65(c) (1)] .
• Within 30 days, all PCB waste within the
container/drum must either be transferred to a
storage facility which meets the requirements for
storage for disposal [761.65(b)(1)], or to an EPA
approved and permitted PCB disposal facility.
Q3: From time to time, our lab wishes to return PCB analytical
standards to our supplier because of overshipment and/or the
delivery of incorrect standards. Can these standards be
returned and used by another company or must unused
standards be disposed of as PCB waste?
A3: The class exemption to process and distribute in commerce
small quantities of PCBs for research and development would
also apply in this situation and allow the return of
standards to suppliers for processing and use by another
company. The standards must be packaged in hermetically
sealed containers of a volume of no more than 5 milliliters.
DISPOSAL
PCB wastes (50 ppm or greater) generated from research and
development activities such as used PCB standards,
contaminated containers, and contaminated lab instruments
VII-4
-------
must be disposed of in accordance with EPA disposal
requirements under 761.60. Debris from a spill may be
disposed of in a 761.60 incinerator or a 761.75 chemical
waste landfill [761.60(a)(4)].
RECORDKEEPING AND REPORTING REQUIREMENTS
The class exemption to process and distribute in commerce
small quantities of PCBs for research and development
includes the following recordkeeping/reporting requirements:
• All processors and distributors must maintain
records of their PCB activities for a period of 5
years.
• Any person or. company that expects to process or
distribute in commerce 100 grams (.22 Ib.) or more
PCBs for research and development in 1 year must
report to EPA and identify the sites of PCB
activities and the quantity of PCBs to be
processed and distributed in commerce.
SPILLS
Spills, leaks, and other uncontrolled discharges resulting
in the release of any quantity of PCBs (50 ppm or greater)
is considered improper disposal of PCBs. The PCB Spill
Cleanup Policy provides specific cleanup measures which, if
followed explicitly, create a presumption against
enforcement for penalties or further cleanup. See the
chapter on "PCB Spill Cleanup Policy" for specific measures.
VIl-5
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CHAPTER VIII
MICROSCOPIC
MOUNTING MEDIUM
IMMERSION OILS
OPTICAL LIQUIDS
Manufacturing, Processing, and Distribution in Commerce
(page VIII-2)
Use Conditions (page VIII-2)
Disposal (page VIII-2)
Spills (page VIII-2)
-------
-MICROSCOPIC MOUNTING MEDIUM. IMMERSION OILS. OPTICAL LIQUIDS-
PCBs are reported to be an ideal mounting medium for light
microscopy primarily because of their stability, refractive
index, viscosity, and thermoplastic properties. In the
past, the principal users have been mineralogists and
chemical microscopists employed in chemical laboratories
such as: police crime-laboratories, museum conservation
laboratories, industrial laboratories, where contaminant
particles in drugs, food, and plastics are identified, and
in laboratories studying environmental contaminants. PCBs *
are used in art and historic conservation as a mounting
medium to preserve specimens permanently and in the
preservation of small environmental, forensic, and
industrial contaminant particles.
Although mounting media exist with refractive indices and
viscosities similar to PCBs, these media reportedly discolor
in time. At this time, there are no adequate substitutes
for PCBs in the preparation of permanent slides.
PCBs are useful as microscope immersion oils in medical
research. Small amounts of PCB immersion oils are useful in
cancer studies in which fluorescence microscopy is used.
The technique used in immersion microscopy involves placing
a drop of immersion oil on the coverslip of the slide and
lowering the objective lens of the microscope until it just
touches the oil.
PCB immersion oil has the lowest fluorescence of any
currently available formulation, and this property is
particularly important in fluorescence microscopy where the
immersion oil must not fluoresce and therefore will not
compete with the fluorescence of the specimen under
analysis. There appears to be no other suitable alternate
material with the desirable low auto-fluorescence, low
dispersion, and high refractive index of PCBs.
Scientists in the fields of space, communications, and
defense-related research use .02 cc to 4 liters of PCBs in
certain specialized optical applications including use in
fiber optic connectors. These PCBs are contained in optical
equipment where they exist in a permanent or semi-permanent
state.
It is believed there are no adequate substitutes for PCBs as
optical liquids in space, communications, defense-related
research projects, and other specialized optical uses, such
as the use of PCBs in tunable light receivers. There are
relatively few compounds with as high a refractive index as
PCBs and none that also has the long-term stability.
VIIl-l
-------
An example of an optical use of PCBs, where their use is
essential, is the use of PCBs with tunable light receivers
for the analysis of light from a solar telescope. PCBs are
necessary in these light receivers because of their
stability and ability to transmit light better in the blue
and green regions of the spectrum, where starlight is
transmitted, than other potential substitute fluids.
MANUFACTURING. PROCESSING. AND DISTRIBUTION IN COMMERCE
The manufacture, processing, and distribution in commerce of
PCBs for use as a mounting medium, immersion oil in
fluorescence microscopy, and optical liquid are permitted
only for persons who are granted an exemption under TSCA
section 6(e)(3)(B).
USE CONDITIONS
PCBs may be used as a permanent microscopic mounting medium,
an immersion oil in fluorescence microscopy, and an optical
liquid in a manner other than a totally enclosed manner
indefinitely [761.30(k), (n), (o)].
DISPOSAL
All PCB waste resulting from the use of PCBs in
concentrations 50 ppm or greater as a mounting medium,
immersion oil, and/or optical liquid must be disposed of in
accordance with EPA disposal requirements [761.60].
SPILLS
Spills, leaks, and other uncontrolled discharges resulting
in the release of any quantity of PCBs (50 ppm or greater)
is considered improper disposal of PCBs. The PCB Spill
Cleanup Policy provides specific cleanup measures which, if
followed explicitly, create a presumption against
enforcement for penalties or further cleanup. See the
chapter on "PCB Spill Cleanup Policy" for specific measures
VIII-2
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CHAPTER IX
CARBONLESS COPY PAPER
Overview (page IX-1)
Manufacturing (page IX-l)
Processing (page IX-1)
Distribution in Commerce (page IX-1)
-------
-CARBONLESS COPY PAPER-
OVERVIEW
Prior to 1971, some carbonless copy paper was made with ink
containing PCBs. There does not appear to be a way to
distinguish PCB carbonless copy paper from non-PCB
carbonless copy paper except by dates or o'ther indications
on unused inventories. A large portion of the PCB copy
paper that has not been destroyed is probably in files. An
enormous undertaking would be required of both business and
government to purge existing files of PCB carbonless copy
paper. As the amount of PCB on each sheet of paper is
extremely small, EPA has concluded that the continued use of
carbonless copy paper does not present an "unreasonable
risk" and has authorized the continued use of existing PCB
copy paper.
MANUFACTURING
The manufacture of PCBs for use in carbonless copy paper is
prohibited without an EPA exemption [761.20(b)].
PROCESSING
The processing of PCBs for use in carbonless copy paper is
prohibited without an EPA exemption [761.20(c)].
DISTRIBUTION IN COMMERCE
The distribution in commerce of PCBs for use in carbonless
copy paper is prohibited without an EPA exemption
[761.20(c)].
IX-1
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CHAPTER X
EXCLUDED PCB PRODUCTS
Used Oil (page X-2)
Investment Casting Waxes (page X-6)
Electrical Equipment Components (page X-6)
-------
-EXCLUDED PCB PRODUCTS-
In the Federal Register of July 10, 1984 (49 FR 28172), EPA
published the "Uncontrolled PCBs" rule. This final rule was
a result of the "EDF v. EPA" lawsuit in which the
Environmental Defense Fund (EDF) challenged EPA's general 50
parts per million (ppm) regulatory cutoff for PCBs. This
challenge was successful and on October 30, 1980, the U.S.
District Court of Appeals found that there was not
substantial evidence to support EPA's original decision to
exclude generally from regulation all materials containing
PCBs at concentrations less than 50 ppm. Consequently, EPA
undertook the regulation of very low concentration PCBs
(less than 50 ppm).
The 1984 "Uncontrolled PCBs" rule among other things,
regulated manufacturing processes generating low
concentration PCBs in other than "closed" and "controlled
waste" processes. On the date the rule became effective,
the Court lifted its stay in the EDF lawsuit, which had the
effect of banning any activity involving any quantifiable
level of PCBs unless that activity was specifically
excluded, exempted, or authorized by regulation. The
practical effect of the Court's action was to make illegal
many activities which were neither anticipated nor evaluated
during the rule's development and which presented no
unreasonable risk to health or the environment.
Consequently, on June 27, 1988 (53 FR 24206), EPA published
in the Federal Register a set of amendments to the 1984 PCB
"Uncontrolled Rule." These amendments have excluded the
majority of low-level PCB activities (less than 50 ppm) from
regulation. In other words, many low-level PCB activities
which became prohibited with the "Uncontrolled PCBs" rule
have returned to unregulated status.
The amendments to the 1984 rule include a generic exclusion
for products containing less than 50 ppm PCBs using the new
term "Excluded PCB Products" (761.3). Generally, the
processing, distribution in commerce, and use of "Excluded
PCB Products" is now unregulated. "Excluded PCB Products"
are defined as PCBs which appear at concentrations less than
50 ppm in products including, but not limited to,
inadvertently generated PCBs (see 761.l(f)), PCB
contaminated products (e.g., investment casting waxes), PCB
contaminated recycled fluids and equipment, and used oils,
provided that:
• The products were legally manufactured, processed,
distributed in commerce, or used before October 1,
1984.
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• The products were legally manufactured, processed,
distributed in commerce, or used pursuant to
authority granted by EPA by regulation, by
exemption, by settlement agreement, or pursuant to
other agency-approved programs.
• The resulting PCB concentration (< 50 ppm) is not
a result of any dilution.
NOTE: This rule does not affect land application practices
involving sewage sludge or other nonhazardous solid wastes
which contain PCBs at concentrations less than 50 ppm.
These activities are regulated under other EPA programs.
EPA adopted the generic exclusion for "Excluded PCB
Products" based upon the Agency's determination that the
use, processing, and distribution in commerce of these
products with less than 50 ppm PCB contamination will not
generally present an unreasonable risk to health or the
environment. However, EPA is aware that some product uses
and processing, particularly the burning and recycling of
used oil, may present unique exposure and risk considera-
tions.
USED OIL - History
Under the PCB "Uncontrolled Rule," there was considerable
confusion regarding the status of used oil containing less
than 50 ppm PCBs. In the earlier 1979 "PCB Ban Rule", used
non-PCB oil (less than 50 ppm) was unregulated except for
its reuse as a dust suppressant, sealant, or coating which
was prohibited at any detectable PCB level. However, with
the overturning of the general 50 ppm regulatory cutoff by
the EDF v. EPA decision, activities (use, processing, or
distribution in commerce) involving less than 50 ppm PCBs
became prohibited on October 1, 1984, unless specifically
authorized, exempted, or excluded by regulation. Prior to
publication of the PCB "Uncontrolled Rule" amendments, EPA
had specifically authorized only three reuses of oil
products with less than 50 ppm PCBs:
• The reuse of dielectric fluids (as dielectrics).
• The reuse of hydraulic and heat transfer fluids
(as hydraulic and heat transfer fluids).
• The reuse of waste oil as a feedstock by
manufacturers of asphalt roofing materials under
the conditions set out in the definition of
"Recycled PCBs" processes.
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Therefore, other activities involving the use, processing,
or distribution in commerce of used oil with any
quantifiable PCB concentration (2 ppm or greater) became
prohibited.
USED OIL - Current
The processing, distribution in commerce, 'and use of low-
level used oils (2-49 ppm) is generally excluded from
regulation under the definition of "Excluded PCB Products."
This exclusion does not, however, affect the existing
prohibitions on the use of waste oil containing any
detectable level of PCBs as a dust suppressant, sealant, or
coating. It is important to note that low-level used oil
activities consisting solely of "disposal" are not
prohibited. This "unregulated disposal" status does not
mean that EPA has authorized the indiscriminate dumping or
burning of used oil containing less than 50 ppm PCBs. It
should be stressed that the PCB regulations define
"Disposal" in terms of acts which "complete or terminate the
useful life of PCBs." In this context, the Agency considers
that used oil activities such as recycling for use and/or
burning in a manner that does not destroy or "terminate the
useful life of PCBs" in fact constitutes reuse or processing
of PCBs and consequently became prohibited under the PCB
"Uncontrolled Rule." Used oil (2-49 ppm) could be burned
for energy recovery, but only in combustion units which
accomplish PCB destruction. Burning PCBs, even at low-level
concentrations, in combustion units which do not accomplish
PCB destruction may volatilize the PCBs and potentially
create an additional point source of toxic products such as
polychlorinated dibenzofurans (PCDFs). The burning of used
oil (2-49 ppm) is allowed only if the following marketing,
burning, testing, and recordkeeping requirements are met:
1) MARKETING: Owners and operators of facilities which
process and/or distribute in commerce for energy recovery
used oil containing any detectable level of PCBs are
referred to as "Marketers" of used oil fuels. Used oil
containing any detectable level of PCBs may be marketed only
to:
• qualified incinerators defined in 40 CFR 761.3,
• other marketers identified in 40 CFR 279, or
• burners identified under 40 CFR 761.20(e) (1) (iii) .
2) BURNING: Owners and operators of facilities which burn
used oil containing any detectable level of PCBs are
referred to as "Burners" of used oil fuels. Used oil
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containing any detectable level of PCBs may be burned for
energy recovery only in:
• an incinerator approved under the provisions of
761.70, or
• a high efficiency boiler which complies with the
criteria of 761.60(a)(2)(iii)(A), and for which
the operator (burner) has given written notice to
the EPA Regional Administrator in accordance with
the requirements under 761.60(a) (2) (iii) (B) , or
• an incinerator approved under Section 3005(c) of
RCRA, or
• burners identified in 40 CFR 279.61(a)(1) and (2).
In addition, before a burner accepts from a marketer the
first shipment of used oil fuel containing detectable PCBs
(2-49 ppm), he must provide the marketer a one-time written
and signed notice certifying that:
• he has complied with any notification requirements
applicable to "Qualified Incinerators" (761.3) or
to "Burners" regulated under 40 CFR Part 279; and
• he will burn the used oil only in a combustion
facility identified in 761.20(e)(1).
3) TESTING: Used oil to be burned for energy recovery is
presumed to contain detectable levels of PCBs unless the
marketer obtains analysis (testing) or other information
documenting that the used oil fuel does not contain
detectable levels of PCBs.
• The person who first claims that a used oil fuel
does not contain detectable PCBs is subject to the
requirement to obtain analysis or other
information to support this claim.
• Testing to determine the PCB concentration in used
oil may be conducted on individual samples, or in
accordance with the batch testing procedures
described in 761.60(g)(2).
• Other information documenting that used oil fuel
does not contain detectable levels of PCBs may
consist of either personal, special knowledge of
the source and composition of the used oil, or a
certification from the person generating the used
oil claiming that the oil contains no detectable
PCBs (i.e., <2 ppm).
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4) RECORDKEEPING: The following recordkeeping
requirements apply to the testing, marketing, and burning of
used oil fuels.
• The marketer who first claims that used oil fuel
contains no detectable PCBs must include copies of
the analysis or other information documenting his
claim among the records required to be kept under
40 CFR 279.72 and 279.74.
• Burners must include a copy of each
761.20 (e) (3) (ii) certification notice that he
sends to a marketer among the records required to
be kept under 40 CFR 279.65 and 279.66.
• A marketer must include a copy of each
certification notice relating to transactions
involving PCB-containing used oil among the
records required to be kept under 40 CFR 279.74
and 279.75.
Ql: My facility regularly accumulates used oil containing low-
level PCBs. What options do I have for getting rid of these
waste oils?
Al: Some of the options available for waste oils containing low-
level PCB contamination (less than 50 ppm) include but are
not limited to:
1) Disposal in a "Qualified Incinerator" (761.3).
2) Disposal by an alternative EPA approved and permitted
method such as "chemical detoxification."
3) Servicing and/or reuse in electrical equipment as a
dielectric fluid (if originally a dielectric fluid).
4) Servicing and/or reuse in heat transfer and hydraulic
systems (if originally heat transfer and hydraulic
fluid).
Q2: From time to time our facility sells and/or gives away waste
oils we've accumulated to other parties. It is unknown
whether these waste oils contain any PCBs or exactly what
these waste oils are used for. Our facility isn't
responsible for how these waste oils are used or
burned...are we?
A2: First, the waste oils your facility is selling/giving away
must be presumed to contain detectable levels of PCBs unless
the oil is tested or otherwise certified not to contain
detectable PCBs. Also, if the waste oils being sold or
given to other parties are being used in prohibited
activities, your facility is possibly involved in improper
distribution in commerce (marketing) of PCBs. The marketing
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of low-level PCB waste oils is a regulated activity and
imposes specific recordkeeping and certification
requirements of the marketer.
Q3: Can a facility burn its own non-PCB (2-49 ppm) waste oils?
A3: Yes, provided the facility uses a high efficiency boiler or
other combustion system that complies with the definition of
"Qualified Incinerators" (761.3). If it is unclear whether
a boiler or incinerator meets the requirements, the facility
should contact their Regional EPA Office and provide
information on their system which EPA will evaluate on a
case-by-case basis.
INVESTMENT CASTING WAXES
EPA examined the facts surrounding past uses of PCBs as a
wax extender, as well as the circumstances of residual low
levels of PCB contamination in the stocks of reclaimed
waxes. EPA determined that the further use, processing, and
distribution in commerce of these waxes will not present an
unreasonable risk to health or the environment. In the 1988
amendments to the PCB "Uncontrolled Rule," investment
casting waxes were included among the class of "Excluded PCB
Products." Activities involving these waxes are now
generally excluded from TSCA regulation provided they
contain less than 50 ppm PCBs [761.3].
ELECTRICAL EQUIPMENT COMPONENTS
The "Electrical Equipment Rule" (August 25, 1982 47 FR
37342) authorized indefinitely the use of many types of
"Non-PCB" (less than 50 ppm) electrical equipment. These
authorizations include: transformers, voltage regulators,
capacitors, electromagnets, switches, circuit breakers,
reclosers, and cable. For each of these categories, the
"Electrical Equipment Rule" authorized use at the less than
50 ppm level without any corresponding use conditions
restricting that use. In other words, as long as no fluids
50 ppm or greater PCBs are introduced into such equipment,
there are no restrictions on the servicing of this
equipment, including its rebuilding. Also, intact "Non-PCB"
electrical equipment is free from any requirement to obtain
exemptions from the processing and distribution in commerce
bans under TSCA. Thus, this equipment is essentially free
from TSCA regulation.
Since the promulgation in 1979 of the PCB ban rule, drained,
obsolete transformers (formerly containing less than 50 ppm
PCBs) may be disposed of as salvage. Although described as
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a form of unregulated disposal, a qualification on
permissible salvage operations is that they must bring about
the termination of the useful life of PCBs and PCB Items.
So, salvaging which accomplishes metals recovery through the
smelting of transformer components qualifies as "disposal"
under TSCA if the PCBs are eliminated by the smelting
process.
EPA has determined that recycling activities involving
equipment components with PCB concentrations less than 50
ppm do not present any significantly greater risks than
other activities connected with the unrestricted use and
servicing of "Non-PCB" electrical equipment.
Based upon this evaluation, EPA included "Non-PCB" equipment
components (when generated by authorized rebuilding or
salvaging) within the exclusion for "Excluded PCB Products."
These components may now be freely incorporated into other
electrical equipment, or distributed in commerce for the
purpose of reuse in electrical equipment provided the
components comply with the definition of "Excluded PCB
Products."
To summarize:
• Electrical equipment with PCB contamination less
than 50 ppm may be dismantled (processed) and the
components reused in repair and rebuilding
activities provided the components comply with the
definition of "Excluded PCB Products" (761.3).
• Electrical equipment with PCB contamination less
than 50 ppm may also be sold (distributed in
commerce) to be dismantled (processed) for reuse
in repair and rebuilding activities provided the
components comply with the definition of "Excluded
PCB Products" (761.3).
• Drained electrical equipment with PCB
contamination less than 500 ppm may be scrapped or
salvaged for metals recovery as a method of
unregulated disposal provided that: (1) these
practices do not result in spills or uncontrolled
discharges of PCBs, and (2) these practices must
bring about the termination of the useful life of
PCBs or PCB Items.
Drained electrical equipment with PCB
contamination 50-499 ppm (known or assumed) may
not be dismantled (processed) for the purpose of
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reusing the equipment components to repair or
rebuild other electrical equipment.
Drained electrical equipment with PCB
contamination 50-499 ppm (known or assumed) may
not be sold or traded (distributed in commerce)
for the purpose of reusing the equipment
components to repair or rebuild other electrical
equipment.
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CHAPTER XI
RECYCLED PCBS
AND EXCLUDED
MANUFACTURING PROCESSES
Recycled PCBs (page XI-1)
Excluded Manufacturing Processes (page XI-2)
-------
-RECYCLED PCBs AND EXCLUDED MANUFACTURING PROCESSES-
The 1984 PCB "Uncontrolled Rule" allowed the manufacture,
processing, distribution in commerce, and use of certain
PCBs (less than 50 ppm) under the definitions of "Recycled
PCBs" and "Excluded Manufacturing Processes."
RECYCLED PCBs
EPA has concluded that excluding low-level PCB materials
involved in certain recycling processes would not present an
unreasonable risk to health or the environment. EPA
included within the definition of "recycled PCBs" two
industries: 1) paper and pulp manufacturers, and 2)
manufacturers of asphalt roofing materials. Processes which
recycle PCBs in paper products and asphalt roofing materials
must meet the following requirements:
• There are no detectable concentrations of PCBs in
asphalt roofing material products leaving the
processing site.
• The concentration of PCBs in paper products
leaving any manufacturing site processing paper
products, or in paper products imported into the
United States, have an annual average of less than
25 ppm, and not exceeding a 50 ppm maximum at any
given time.
• The release of PCBs at the point at which
emissions are vented to ambient air must be less
than 10 ppm.
• The amount of Aroclor PCBs added to water
discharged from an asphalt roofing processing site
must at all times be less than 3 micrograms per
liter (/ig/L) for total Aroclors (roughly 3 parts
per billion). Water discharges from the
processing of paper products must at all times be
less than 3 micrograms per liter (^ig/L) for total
Aroclors (roughly 3 ppb), or comply with the
equivalent mass-based limitation.
Ql: Does the 3 parts per billion (ppb) discharge limit for pulp
and paper mills apply only to direct discharges?
Al: Yes, the discharge limit for pulp and paper mills applies
only to direct discharges. It does not apply to paper mills
that discharge into publicly owned treatment works (POTWs).
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Disposal of any other process wastes at
concentrations of 50 ppm or greater must be in
accordance with 761.60.
EXCLUDED MANUFACTURING PROCESSES
The 1984 PCB "Uncontrolled Rule" also amended the PCB
regulations by replacing the definitions of "Closed
Manufacturing Process" and "Controlled Waste Manufacturing
Process" with a generic exclusion now defined as "Excluded
Manufacturing Processes." This established limits for PCB
releases in products, air emissions, water effluents, and
wastes. In sum, EPA has prescribed a generic exclusion to
manufacture, process, distribute in commerce, and use
inadvertently generated PCBs in accordance with the
definition of "Excluded Manufacturing Process" provided
that:
• PCBs in products leaving the manufacturing site
are limited to an annual average of less than 25
ppm, and not exceeding a 50 ppm maximum at any
given time.
• Where the product is detergent bars, PCB
concentrations in the product are limited to less
than 5 ppm.
• PCBs added to water discharges from the
manufacturing site are limited to less than 100
micrograms per resolvable gas chromatographic peak
per liter of water discharged.
• Releases of PCBs in air emissions are limited to
less than 10 ppm at the point where emissions are
vented.
• Disposal of any other process wastes at
concentrations of 50 ppm or greater must be in
accordance with 761.60.
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CHAPTER XII
PCB STORAGE REQUIREMENTS
PCB Storage For Disposal Facilities (page XII-3)
Storage Options (page XII-5)
Marking/Labeling (page XII-6)
Handling Equipment (page XII-6)
Inspections (page XII-7)
Storage Containers (page XII-7)
Storage Management (page XII-9)
-------
-PCB STORAGE REQUIREMENTS-
Storage of PCBs became regulated in 1979 with the
promulgation of the "PCB Ban Rule." Since those earliest
PCB regulations, the storage requirements for PCBs have
remained virtually unchanged but for a very few amendments
found in the 1982 "Electrical Equipment Rule." However, the
improper storage of PCBs remains one of the most frequent
areas of non-compliance based upon EPA inspection reports
from regional EPA offices.
Complying with the storage requirements for PCBs involves:
• Establishing a proper storage facility for PCBs.
• Utilizing proper containers for PCB storage.
• Managing PCB storage in accordance with marking,
recordkeeping, and inspection requirements.
• Understanding which PCBs and PCB Items require
storage and the various storage options which are
available.
• Removal from storage and disposal of PCBs and PCB
Items within the 1-year disposal time limitation.
PCB storage requirements apply to those PCBs and PCB Items
with PCB concentrations of 50 ppm or greater (or PCBs less
than 50 ppm as a result of dilution from 50 ppm or greater
material) including those PCBs and PCB Items which EPA
requires to be assumed to be 50 ppm or greater. Generally,
PCB storage requirements apply to PCBs and PCB Items which
have been removed from service and designated for disposal.
However, PCB storage requirements also apply to any PCB
liquids (50 ppm or greater) in PCB Containers which are
being stored for authorized servicing of electrical
equipment. PCB and PCB-Contaminated Electrical Equipment
being stored for reuse (stock) is considered by the Agency
to be "in-service" and does not require storage in a PCB
storage facility.
The new Notification and Manifesting Rule adopts an approval
process for commercial PCB waste storers. The term
"commercial storer" is defined broadly to mean any facility
that stores PCB wastes generated by others, or that brokers
waste generated during electrical equipment servicing.
The rule allowed commercial storers a 180-day period of
interim approval (from February 5, 1990 to August 2, 1990),
within which they must have applied for approvals from their
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EPA Regional Administrators (or from the Director, CMD/OPPT
for approval of commercial storage areas at disposal
facilities approved by Headquarters).
The issuance of a final storage approval will follow a
review of the environmental compliance history of the
company and its principals and key employees. The Regional
Administrator must be satisfied that the applicant is
qualified to engage in the commercial storage business.
Also, applicants will be required to submit acceptable
closure plans and demonstrate their financial responsibility
for closure. The requirement to demonstrate one's financial
responsibility can generally be satisfied by one or more of
the financial assurance mechanisms described in current RCRA
regulations for hazardous waste facilities. Finally,
applicants will be required to certify their compliance with
the TSCA storage facility standards, and to estimate the
maximum quantities of PCB waste that will be handled at the
facility.
Ql: Is electrical equipment being stored for "repair" considered
"in use" or "removed from service" by EPA?
Al: In the opening paragraph to the "Storage and Disposal"
subpart of the PCB regulations (761.60), it is indicated
that the regulations do not require "...removal of PCBs and
PCB Items from service earlier than would normally be the
case." It is very important to understand that the term
"removed from service," when used in the regulations,
specifically means that PCBs and PCB Items have been
designated for disposal to terminate or end the useful life
which they were originally designed for. In fact, it is the
policy of the agency that once a PCB Item has been "removed
from service" for disposal, it cannot be placed back "in
service" for continued use including repairing the item for
further use.
There has been considerable misunderstanding of the term
"removed from service" by those in the regulated community,
especially electric utilities that for years have considered
electrical equipment being "changed out" and brought in from
their system to be repaired, serviced, or placed back into
stock for reuse as being "removed from service." This is
not what EPA means when the regulations refer to PCB Items
being "removed from service." To the contrary, EPA
considers electrical equipment being stored for repair
and/or reuse to be just as "in use" as those on-line units
being actively used within the electric system.
On the other hand, questions have been raised about the
continued legality of storing nonfunctional electrical
equipment indefinitely for repair when the owner or user of
XII-2
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the equipment has no intention of actually repairing the
equipment or does not complete repairs within a reasonable
amount of time. Such indefinite storage of equipment which
may ultimately be disposed of thwarts the intent of the 1-
year restriction on storage for disposal. EPA promulgated
the storage for disposal requirements in the 1978 "Marking
and Disposal" Rule due to the concern that long-term storage
could lead to deterioration of PCB Containers and PCB
Articles and result in the release of PCBs'. Consequently,
the agency may enforce against lengthy "storage for reuse"
of equipment which is not reasonably expected to be placed
back into service.
PCB STORAGE FOR DISPOSAL FACILITIES
Establishing a PCB storage facility which meets the criteria
listed under 761.65(b) does not necessarily require
tremendous expense, space, or technical engineering. In
fact, many facilities which store small quantities of PCBs
and PCB Items are able to set up a designated PCB storage
area involving minimal space and expense but which complies
with all regulatory requirements. On the other hand, some
facilities have need of larger, more elaborate PCB storage
facilities to meet the greater volume of PCBs and PCB Items
being processed and stored for disposal. In either case,
owners or operators of facilities used for the storage of
PCBs and PCB Items shall comply with the following
requirements:
• The facility shall have adequate roof and walls to
prevent rainwater from reaching the stored PCBs
and PCB Items [761.65(b)(1)(i)].
• The facility shall have an adequate floor which
has continuous curbing with a minimum 6-inch high
curb. The floor and curbing must provide a
containment volume equal to at least two times the
internal volume of the largest PCB Article or PCB
Container stored therein or 25 percent of the
total internal volume of all PCB Articles or PCB
Containers stored therein, whichever is greater
[761.65(b) (l) (ii)] .
• The facility shall have no drain valves, floor
drains, expansion joints, sewer lines, or other
openings that would permit liquids to flow from
the curbed area [761.65(b)(1)(iii)].
• The facility shall have floors and curbing
constructed of continuous smooth and impervious
materials, such as portland cement concrete or
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steel, to prevent or minimize penetration of PCBs
[761.65(b)(1)(iv)].
• The facility shall not be located at a site that
is below the 100-year flood water elevation
[761.65(b) (1) (v)] .
Q2: Can PCBs be stored for disposal without having to set up a
"PCB storage facility"?
A2: The regulations include optional storage methods for PCBs
such as "30-day temporary storage" by a generator and
"pallet storage." (See Storage Options.) However, in all
cases where PCBs 50 ppm or greater (known or assumed) are
stored for disposal for more than 30 days, a PCB storage
facility is necessary. Liquid PCBs 500 ppm or above may not
be stored temporarily.
Q3: Does a facility have to construct a special building
specifically for PCB storage or can a portion of an existing
building be used to properly store PCBs?
A3: EPA does not require the construction of a separate building
for proper storage of PCBs and PCB Items. It is allowable
to use an existing structure to act as a PCB storage
facility provided all of the criteria of 761.65(b) are met.
Also, the use of an entire building (whether new or
existing) solely for the storage of PCBs is not specifically
required. A designated area within the building reserved for
PCB storage is permissible; however, in those instances
where only a portion of a building is being used as a
PCB storage facility, that area should be clearly marked
and segregated from other activities within the structure.
Q4: Do owners and users of PCBs have to pour expensive concrete
floors and curbing to meet the criteria for a PCB storage
facility, or are other less expensive options available?
A4: The PCB regulations specifically mention "adequate floors"
and "continuous curbing" in the requirements for PCB storage
facilities. However, EPA has generally allowed flexibility
in this area such as the use of a stock tank or metal box to
meet the "berming" criteria requirement for a proper PCB
storage facility. These optional "berms" must be
constructed of smooth impervious materials and must meet the
minimum 6-inch height and volume requirements under
761.65(b)(1)(ii). Also, a stock tank or metal box must not
have any drains, seams, or other openings that would permit
liquids to flow from the containment area.
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STORAGE OPTIONS
As mentioned earlier, the regulations outline two options
for storing PCBs in areas other than a "PCB storage
facility." These two storage options are often referred to
as "30-day temporary storage" and "pallet storage."
"Thirty-day temporary storage" [761.65(c)(1)] allows the
generator to store certain PCB Items in an area that does
not comply with the requirements for a PCB storage facility
for up to 30 days from the date of their removal from
service for disposal provided that a notation is attached to
the PCB Item or PCB Container indicating the date the item
was removed from service for disposal. PCB Items which can
be stored under this 30-day temporary storage option
include:
• Nonleaking PCB Articles and PCB Equipment
[761.65(c)(1)(i)].
• Leaking PCB Articles and PCB Equipment if the PCB
Items are placed in a nonleaking PCB Container
that contains sufficient sorbent materials to
absorb any liquid PCBs remaining in the PCB Items
[761.65(c) (1) (ii)] .
• PCB Containers containing nonliquid PCBs such as
contaminated soil, rags, and debris [761.65(c)(1)
(iii)J.
• PCB Containers containing liquid PCBs at a
concentration between 50 and 500 ppm, provided a
Spill Prevention, Control, and Countermeasure Plan
has been prepared for the temporary storage area
in accordance with 40 CFR 112. In addition, each
container must bear a notation that indicates that
the liquids in the drum do not exceed 500 ppm PCB
[761.65(c)(1)(iv)].
Another storage option outlined in the PCB regulations is
often referred to as "pallet storage." Pallet storage
allows certain PCB Items to be stored temporarily on pallets
next to a PCB storage facility that meets the requirements
of 761.65(b)(1). However, pallet storage is permitted only
when the PCB storage facility has immediately available
unfilled storage space equal to 10 percent of the volume of
the PCB Items being stored on pallets next to the facility
[761.65 (c) (2)] . PCB Items which can be stored under this
"pallet storage" option include:
• Nonleaking and structurally undamaged PCB large,
high-voltage capacitors, and
XII-5
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• PCB-Contaminated Electrical Equipment (known or
assumed 50-500 ppm) that have not been drained of
free-flowing dielectric fluid [761.65 (c) (2)] .
These PCB Items must be checked weekly when stored outside
the facility and leaking PCB Items must be placed inside the
storage area.
Q5: Is the 30-day temporary storage option available for
commercial storage and disposal facilities?
A5: No. Temporary storage applies only to generators of PCB
waste items since they are the only ones who have access to
the PCB Items immediately after their removal from service
for disposal.
Q6: Does temporary storage provide generators of PCB waste with
an additional 30 days to the 1-year storage and disposal
time limitation?
A6: No. Thirty-day temporary storage is included in the total
1-year storage and disposal time limitation.
Q7: Is pallet storage allowed for a facility that doesn't have a
PCB storage facility?
A7: No. Pallet storage is only allowed when located next to a
PCB storage facility that meets the requirements of
761.65(b)(1).
Q8: Does pallet storage have to be indoors?(
A8: No, provided that the PCB Capacitors and/or PCB-Contaminated
Electrical Equipment being stored for disposal are on
pallets located adjacent to the building which houses the
PCB storage facility.
MARKING/LABELING
All PCB storage areas including the "PCB storage facility"
as well as "30-day temporary storage" and "pallet storage"
areas must be marked/labeled in accordance with the EPA
marking requirement at 761.40(a)(10).
HANDLING EQUIPMENT
Any movable equipment that is used for handling PCBs and PCB
Items in the PCB storage facility, and that comes in direct
contact with PCBs, shall not be removed from the storage
facility area unless it has been decontaminated by swabbing
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the surfaces that have contacted PCBs with a solvent that
meets the criteria of 761.79(a). The solvent may be reused
for decontamination until it contains 50 ppm PCBs. The
solvent and any nonliquid PCBs that result from the
decontamination must then be disposed of in accordance with
761.60(a) and 761.60(a)(4) respectively.
INSPECTIONS
All PCB Articles and PCB Containers in the PCB storage
facility must be inspected for leaks at least once every 30
days. Any leaking PCB Articles and PCB Containers and their
contents shall be transferred immediately to properly marked
nonleaking containers. Any spilled or leaked materials
shall be immediately cleaned up, using sorbents and/or other
adequate means, and the PCB-Contaminated materials and
residues shall be disposed of in accordance with PCB
disposal requirements [761.65(c) (5) ] .
Any PCB Capacitors and PCB-Contaminated Electrical Equipment
stored adjacent to the PCB storage facility on pallets must
be inspected for leaks weekly [761.65 (c) (2)] .
STORAGE CONTAINERS
Containers used for the storage of PCBs (known or assumed 50
ppm or greater) shall comply with the shipping container
specifications of the Department of Transportation (DOT).
Containers approved under TSCA at 761.65(c)(6) for the
storage of liquid PCBs include:
• DOT-5 steel drum without removable head
• DOT-SB steel drum without removable head
• DOT-6D overpack with DOT-2S or DOT-2SL molded
polyethylene containers
• DOT-17E single trip steel drum without removable
head
Containers approved for the storage of nonliquid PCBs
include:
• DOT-5 steel drum without removable head
• DOT-5B steel drum without removable head
• DOT-17C single trip steel drum with removable head
XII-7
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As an alternate, containers larger than those specified in
DOT specifications 5, 5B, or 17C may be used for nonliquid
PCBs if the containers are designed and constructed in a
manner that will provide as much protection against leaking
and exposure to the environment as the DOT specification
containers, and are of the same relative strength and
durability as the DOT specification containers
[761.65(c)(6)].
Storage containers for liquid PCBs can be larger than the
containers listed above (i.e., bulk storage tanks) provided
that:
• The containers are designed, constructed, and
operated in compliance with Occupational Safety
and Health Standards [29 CFR 1910.106] for
flammable and combustible liquids
[761.65(c)(7)(i)].
• Before using these containers/bulk tanks for
storing PCBs, the design of the containers must be
reviewed to determine the effect on the structural
safety of the containers that will result from
placing liquids with the specific gravity of PCBs
into the containers [761.65 (c) (7) (i)] .
• Owners or operators of any facility using these
containers/bulk tanks shall prepare and implement
a Spill Prevention Control and Countermeasure
(SPCC) Plan [761.65(c)(7)(ii)].
Q9: Can I use a storage container for PCB waste other than those
specifically referenced in 761.65 (c) (6)?
A9: Yes. The PCB regulations, as currently written, essentially
require the use of the "Cadillac" of 55-gallon drums for PCB
containment, shipment, and storage. The design
specifications and engineering criteria used in the
manufacture of these drums are, in DOT'S opinion, not really
necessary, given the physical and chemical properties of
PCBs. Therefore, EPA will defer to the expertise of DOT as
far as testing drums is concerned, and would allow the use
of an alternate drum if it has been demonstrated to DOT'S
satisfaction that the alternate container will protect
against leaking and exposure to the environment of PCBs.
Q10: The regulations define a PCB Transformer as containing 500
ppm or greater PCBs. However, there is no specific PCB
level mentioned under the definition of a "PCB Container."
Has EPA established a regulatory PCB level for PCB
Containers in relation to marking/labeling, storage, and
recordkeeping?
XII-8
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A10: Yes. The term "PCB Container" as found under the marking,
storage, disposal, and recordkeeping sections of the TSCA
regulations, specifically applies to drums, bulk tanks, and
other containers (defined under 761.3) containing PCBs in
concentrations of 50 ppm or greater. This 50 ppm regulatory
level applies to "PCB Article Containers" as well.
Prior to disposal, an undrained PCB Container with PCB
concentrations at 50 ppm or greater shall be stored in a PCB
storage facility. Unless decontaminated, a PCB Container
containing PCBs in concentrations of 50 ppm or greater shall
be disposed of in accordance with 761.60 (c) . For a PCB
Container to be decontaminated, it must be flushed three
times with a solvent containing less than 50 ppm PCBs. The
solubility of PCBs in the solvent must be 5 percent or more
by weight. Each rinse shall use a volume of normal diluent
equal to approximately 10 percent of the PCB Container
capacity. The solvent may be reused for decontamination
until it contains 50 ppm PCB [761.79(a)]. The solvent shall
then be disposed of as liquid PCBs in accordance with
761.60(a). Nonliquid PCBs resulting from decontamination
procedures shall also be disposed of in accordance with
761.60(a)(4).
STORAGE MANAGEMENT
PCB storage management goes beyond simply setting up a PCB
storage area and using proper DOT drums. To effectively
store PCBs and PCB Items in accordance with federal PCB
regulations, a facility must also develop and maintain
appropriate storage practices and storage records.
PCB storage must be managed so that PCB Articles and PCB
Containers can be located by the date they entered storage.
To accomplish this, all PCB Articles and PCB Containers must
be dated on the article or container when they are placed in
the "PCB Storage Facility" [761.65 (c) (8)] . Attaching dates
to PCB Articles and PCB Containers applies to "30-day
temporary storage" and "pallet storage" as well.
Owners or operators of facilities which store PCBs and PCB
Items must establish and maintain records on the storage and
disposition of PCBs in accordance with 761.180(b). (See
chapter XV, on "Recordkeeping and Reporting," for a detailed
discussion of PCB storage records.) For PCB Containers,
these records should include: container contents, PCB
concentration (ppm), the container's total volume, unique
identification number, date placed in transport for
disposal, and date disposed of, if known. These records
will form the basis of a required "Annual Records" to be
prepared by the facility, and therefore the information
XII-9
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should be carefully logged and maintained for future need.
If a facility is utilizing "bulk" storage of PCBs in
containers/bulk tanks larger than 55-gallon DOT drums, the
facility must also maintain records for each batch of PCBs
added to the containers. These records must include the
quantity of the batch and the date the batch was added to
the container. The records shall also include the date,
quantity, and disposition of any batch of PCBs removed from
the container [761.65(c) (8) ] .
Finally, PCB storage must be managed so that PCB Articles
and PCB Containers stored for disposal are removed from
storage and disposed of within 1 year from the date the
articles were removed from service for disposal or the first
batch of PCBs was placed in the container for storage for
disposal.
Qll: The regulations indicate that PCBs must be disposed of
within 1 year. How long can PCBs be stored for disposal
prior to shipment to the final disposal site?
All: The PCB regulations require the disposal of PCBs within the
1-year disposal deadline. EPA has adopted a written policy
(TSCA Compliance Program Policy No. 6-PCB-6) which provides
that a generator delivering PCB waste to a disposal facility
later than 90 days before the end of 1-year disposal
deadline will be held liable if the disposal facility cannot
dispose of the waste in time. If the generator delivers the
waste with 90 days or more remaining in the 1-year deadline,
the disposer is responsible for disposing of the material
before the deadline. The disposer will share in any
liability if he does not dispose of PCB waste within 90 days
from the date it is received at the disposal facility. In
sum, the generator has 9 months of the 1-year disposal
timeframe to store PCBs and transport those PCBs to the
final disposition site.
Q12: As a generator of PCB waste, our facility regularly
contracts a disposal "broker" to pick up and transport our
PCB waste to a PCB disposal site. Normally, these "brokers"
will transport our PCB waste to their facility for storage
and consolidation with PCB waste from other generators. How
long can our PCB waste be stored by a broker?
A12: A disposal "broker" is merely an extension of the generator
in terms of the 1-year disposal deadline. That is, the
generator remains liable if the disposal "broker" fails to
deliver the PCB waste to the disposal site in time for the
waste to be disposed of within the 1-year deadline. In sum,
EPA places the responsibility for delivering PCB waste to a
disposal facility at least 90 days before the 1-year
deadline on the generator of the waste and does not allow
XII-10
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additional time for PCB waste to be processed and/or stored
by disposal brokers or commercial storage facilities.
XII-11
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CHAPTER XIII
PCB DISPOSAL REQUIREMENTS
PCB Liquids with Concentrations of 500 ppm or Greater
(page XIII-1)
Mineral Oil Dielectric Fluid and Other Liquids (50-499 ppm PCB)
(page XIII-1)
Nonliquid PCBs (50 ppm or Greater) (page XIII-2)
PCB Transformers (500 ppm or Greater PCB) (page XIII-2)
PCB Capacitors (page XIII-2)
Large, High- or Low-Voltage PCB Capacitors (page XIII-3)
Small PCB Capacitors (page XIII-3)
PCB-Contaminated Electrical Equipment (50-499 ppm PCB)
(page XIII-3)
PCB Containers (page XIII-3)
PCB Hydraulic Machines (page XIII-4)
Other PCB Articles (page XIII-4)
Dredged Materials and Municipal Sewage Treatment Sludge
(page XIII-4)
Spills (page XIII-5)
Alternative Disposal Methods (page XIII-5)
-------
- PCB DISPOSAL REQUIREMENTS -
Disposal of PCBs became regulated in 1978 with the
promulgation of the "PCB Marking and Disposal" Rule. In
this final Rule, EPA prescribed various disposal
requirements for PCBs and PCB Items, and also established
the 500 parts per million (ppm) regulatory cutoff for the
disposal of PCBs. In the "PCB Ban Rule" published in the
Federal Register on May 31, 1979 (44 FR 31514), the
regulatory cutoff for PCBs was changed from 500 to 50 ppm.
In that same Federal Register. EPA published its "anti-
dilution" provision [40 CFR 761.1(b)] which effect the
disposal of PCBs. The provision states: "No provision
specifying a PCB concentration may be avoided as a result of
any dilution, unless otherwise specifically provided".
Thus, in general, materials are required to be disposed of
according to their original concentration.
PCB LIQUIDS WITH CONCENTRATIONS OF 500 PPM OR GREATER
All PCB liquids and industrial sludges with PCB
concentrations of 500 ppm or greater must be disposed of in
a TSCA incinerator that complies with 761.70 [761.60(a)(1)]
or by an alternate method permitted under 761.60(e).
MINERAL OIL DIELECTRIC FLUID AND OTHER LIQUIDS (50-499 ppm
PCB) - 761.60(a)(2) and (3)
Mineral oil dielectric fluid from PCB-contaminated
electrical equipment containing a PCB concentration of 50-
499 ppm (known or assumed) and liquids other than mineral
oil dielectric fluid containing a PCB concentration of 50-
499 ppm, must be disposed of in one of the following:
• In a TSCA incinerator that complies with 761.70.
• In a chemical waste landfill that complies with
761.75 if information is provided to the owner or
operator of the chemical waste landfill that shows
that the mineral oil dielectric fluid does not
exceed 500 ppm PCB and is not an ignitable waste
as described in 761.75(b) (8) (iii) . (NOTE: After
July 8, 1987 land disposal of liquid hazardous
wastes containing 50 ppm or greater PCB is
prohibited under the Land Disposal Reduction
Program of RCRA, unless an exemption is granted.)
• In a high efficiency boiler that complies with
761.60(a) (2) (iii) (A) .
XIII-1
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By an alternative EPA approved method that
complies with 761.60(e), such as chemical
detoxification, biological treatment, and physical
separation.
NONLIOUID PCBs (50 ppm OR GREATER) - 761.60(a)(4)
Nonliquid PCBs at concentrations of 50 ppm or greater in the
form of contaminated soil, rags, or other debris must be
disposed of in one of the following:
• In an incinerator that complies with 761.70.
• In a chemical waste landfill that complies with
761.75. (NOTE: Except as provided in
761.75(b) (8) (ii), liquid PCBs shall not be
processed into nonliquid forms to circumvent the
high temperature incineration requirements of
761.60(a).
By an alternate method permitted under 761.60 (e) .
PCS TRANSFORMERS (500 ppm OR GREATER PCB) - 761.60(b) (1)
PCB Transformers with PCB concentrations 500 ppm or greater
must be disposed of in accordance with either of the
following:
• In an incinerator that complies with 761.70.
• In a chemical waste landfill that complies with
761.75 provided that the transformer is first
drained of all free-flowing liquid, filled with
solvent, allowed to stand for at least 18 hours,
and then drained thoroughly. PCB liquids and
solvents that are removed shall be incinerated in
accordance with 761.60(a). Solvents may include
kerosene, xylene, toluene, and other solvents in
which PCBs are readily soluble (5% or more).
. By an alternate method permitted under 761.60(e).
PCB CAPACITORS - 761.60(b)(2)
The disposal of any capacitor shall comply with the
following requirements unless it is known from label or
nameplate information, manufacturer's literature, or
chemical analysis (test results) that the capacitor does not
contain PCBs.
XIII-2
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LARGE. HIGH- OR LOW-VOLTAGE PCS CAPACITORS -
761.60(b) (2) (iii)
Any large, high- or low-voltage capacitor which contains 500
ppm or greater PCBs must be disposed of in an incinerator
that complies with 761.70 or through an alternate method
permitted under 761. 60 (e).
SMALL PCS CAPACITORS - 761.60(b)(2)(ii)
Intact, nonleaking PCB small capacitors may be disposed of
as municipal solid waste except that manufacturers who at
any time manufactured PCB small capacitors or equipment
containing a PCB small capacitor must dispose of PCB small
capacitors in an incinerator that complies with 761.70.
Small capacitors that are not intact or are leaking must be
incinerated. EPA recommends that disposers of large
quantities of small PCB capacitors dispose of them in a
TSCA-approved incinerator. Readers are advised to check
with their Regional PCB Coordinator to determine the
specific regional policy on disposal of small capacitors.
PCB-CONTAMINATED ELECTRICAL EQUIPMENT (50-499 DPm PCB) -
761.60(b)(4)
PCB-contaminated electrical equipment, except capacitors,
with PCB contamination 50-499 ppm shall be disposed of by
draining all free-flowing liquid from the electrical
equipment and disposing of the liquid in accordance with
761.60(a)(2) or (3). The disposal of the drained carcass is
not regulated.
Capacitors that contain 50-499 ppm PCBs must be disposed of
in an incinerator that complies with 761.70 or in a chemical
waste landfill that complies with 761.75.
PCB CONTAINERS - 761.60(c)
Unless decontaminated in accordance with 761.79, PCB
Containers with PCB concentrations of 500 ppm or greater
must be disposed of in one of the following:
• In an incinerator that complies with 761.70.
• In a chemical waste landfill that complies with
761.75 provided that if there are PCBs in a liquid
state, the PCB Container shall first be drained
and the PCB liquid disposed of in accordance with
761.60(a)(2) or (3).
XIII-3
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PCB Containers that used to contain PCB concentrations less
than 500 ppm may be disposed of as municipal solid wastes,
provided that the container is drained of any liquid PCBs
and any liquid PCBs in concentrations 50 ppm or greater are
disposed of in accordance with 761.60(a)(2) or (3). The
container must also be emptied of any PCB solids 50 ppm or
greater, and the solids disposed of in accordance with
761.60(a)(4).
PCB HYDRAULIC MACHINES - 761.60(b)(3)
PCB hydraulic machines containing PCBs at concentrations of
50 ppm or greater such as die casting machines may be
disposed of as municipal solid waste or salvage provided
that the machines are drained of all free-flowing liquid and
the liquid is disposed of in accordance with 761.60(a) (2) or
(3). If the PCB liquid contains 1000 ppm or greater, then
the hydraulic machine must be flushed prior to disposal with
a solvent containing less than 50 ppm PCB and the solvent
disposed of in accordance with 761.60(a).
OTHER PCB ARTICLES - 761.60(b)(5)
Other PCB Articles with PCB concentrations at 500 ppm or
greater must be disposed of in one of the following:
• In an incinerator that complies with 761.70.
• In a chemical waste landfill that complies with
761.75, provided that all free-flowing liquid PCBs
have been thoroughly drained from any articles
before the articles are placed in the chemical
waste landfill and that the drained liquids are
disposed of in an incinerator that complies with
761.70.
Other PCB Articles with PCB concentrations at 50-499 ppm
must be disposed of by draining all free-flowing liquid from
the article and disposing of the liquid in accordance with
761.60(a)(2) or (3). The disposal of the drained article is
not regulated.
DREDGED MATERIALS AND MUNICIPAL SEWAGE TREATMENT SLUDGE
All dredged materials and municipal sewage treatment sludge
with PCB concentrations of 50 ppm or greater must be
disposed of in an approved incinerator or j.n an approved
chemical waste landfill, or by an approved alternative
method.
XIII-4
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SPILLS
Spills are included within the definition of "Disposal" at
761.3. Spills of PCBs at 50 ppm or greater are illegal
disposal. PCBs that result from the cleanup of spills must
be stored for disposal and disposed of according to the
applicable regulations [761.60(d)(1) and (2)].
ALTERNATIVE DISPOSAL METHODS - 761.60(e)
Any person who is required to incinerate any PCBs and PCB
Items as discussed in this chapter, and who can demonstrate
that an alternative method of destroying PCBs and PCB Items
exists and that this alternative method can achieve a level
of performance equivalent to 761.70 incinerators or high
efficiency boilers as provided in 761.60(a)(2) and (3), may
submit a written request to either the Regional
Administrator or the Director of the Chemical Management
Division (CMD) for an exemption from the incineration
requirements of 761.70 or 761.60. Requests for approval of
alternate methods that will be operated in more than one
region must be submitted to the Director of CMD except for
research and development involving less than 500 pounds of
PCB material. Requests for approval of alternate methods
that will be operated in only one region must be submitted
to the appropriate Regional Administrator. The applicant
must show that his method of destroying PCBs will not
present an unreasonable risk of injury to health or the
environment. On the basis of such information and any
available information, the Regional Administrator or the
Director of CMD may, in his discretion, approve the use of
the alternate method if he finds that the alternate disposal
method provides PCB destruction equivalent to disposal in a
761.70 incinerator or a 761.60 high efficiency boiler and
will not present an unreasonable risk of injury to health or
the environment. Any approval must be stated in writing and
may contain such conditions and provisions as the Regional
Administrator or the Director of CMD deems appropriate. The
person to whom such waiver is issued must comply with all
limitations contained in such determination.
Guidance documents for submitting alternate disposal method
applications are available from the Operations Branch (7404)
at EPA Headquarters in Washington, D.C.
XIII-5
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CHAPTER XIV
PCB SPILL CLEANUP POLICY
Scope of the Policy (page XIV-3)
Key Definitions (page XIV-5)
PCB Spill Reporting Requirements (page XIV-8)
Determination of Spill Boundaries (page XIV-9)
Cleanup, Recordkeeping, and Testing Requirements (page XIV-9)
Small, Low-Concentration Spills (page XIV-9)
Large, Low-Concentration Spills and High-Concentration Spills
(page XIV-12)
Excluded Spills (page XIV-16)
-------
- PCS SPILL CLEANUP POLICY -
EPA promulgated regulations on the disposal of PCBs in the
Federal Register on February 17, 1978 and May 31, 1979.
These early PCB regulations broadly defined the term
"disposal" to include accidental as well as intentional
releases of PCBs into the environment. Under these
regulations, EPA considers intentional, as well as
unintentional, spills, leaks, and other uncontrolled
discharges of PCBs at concentrations of 50 parts per million
or greater to be "improper disposal" of PCBs. When PCBs are
improperly disposed of as a result of a spill of a material
containing 50 ppm or greater PCBs, EPA has the authority to
compel persons to take actions to rectify damage and/or
cleanup contamination resulting from the spill.
For many years now, EPA standards for the cleanup of spilled
PCBs have been established at the EPA Regional Office level.
Each region established PCB spill cleanup standards in the
form of general guidelines and then applied the general
guidelines on a case-by-case basis for specific spill
situations. Owners of spilled PCBs were required to meet
these standards or face potential penalties for improper
disposal of PCBs.
In establishing PCB spill cleanup standards on a regional
basis, EPA has experienced inconsistency in the general
guidelines and their application to spills from region to
region. For certain spill situations, EPA Regional Offices
have required cleanup only to 50 ppm PCBs. In other spill
situations, regions have required cleanup to preexisting
background levels, or to the limit of detection of PCBs.
Most recently, EPA Regional Offices have applied the "lowest
practicable level" guidelines set up in the January 27,
1984, decision on "General Electric v. U.S.E.P.A." However,
the agency has experienced several areas of difficulty in
applying the "lowest practicable level" approach to all PCB
spills. First, the guideline is subject to, and has
resulted in, disparate interpretations. Second, the term
"lowest practicable level" cannot be easily applied by the
regulated community without guidance from EPA, potentially
resulting in delays in cleanup and prolonged exposures to
humans and more widespread environmental contamination.
Finally, the owner of PCBs may disagree with the EPA
Regional Office's interpretation of the "lowest practicable
level" standard. This may occur when the EPA Regional
Office interpretation would require more stringent and
costly measures than the owner believes are warranted.
XIV-1
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When addressing the subject of PCB spills, EPA has
emphasized two very important ingredients. First, the
timely cleanup of PCB spills. And second, establishing
prudent, yet practicable, numerical criteria standards for
PCB spills cleanup. Since 1982, EPA has had in place
requirements for timely cleanup of certain PCB spills 50 ppm
or greater. In the final PCB Electrical Equipment Rule
published August 25, 1982, EPA required the initiation of
spill cleanup from a PCB Transformer (500 ppm or greater)
within 48 hours of spill discovery. However, the issue of
timely cleanup of PCB spills from sources other than PCB
Transformers (i.e., PCB Capacitors, PCB-Contaminated
Electrical Equipment, etc.) was not addressed; and, the PCB
Electrical Equipment Rule did not establish final cleanup
standards for PCB spills.
Even though EPA did not finalize a PCB spill cleanup policy
in 1982, the Agency has continued to evaluate available
information on the risks posed by spilled PCBs and the costs
associated with cleanup to various levels. EPA recognized
that setting a nationwide PCB spill cleanup policy was a
desirable goal and in the winter of 1984 produced a draft
TSCA Compliance Monitoring Program Policy covering PCB spill
cleanup. Although the 1984 draft was never officially
released, members of the press and the public acquired and
reviewed the draft policy. The Environmental Defense Fund
(EDF), National Resources Defense Council (NRDC), Edison
Electric Institute (EEI), Chemical Manufacturers Association
(CMA), and National Electrical Manufacturers Association
(NEMA), among others, were principal reviewers of the 1984
draft policy. On May 17, 1985, EDF, NRDC, EEI, CMA, and
NEMA submitted to EPA an alternative PCB spill cleanup
policy for consideration by the Agency. EPA viewed this
alternative cleanup policy (referred to as the "Consensus
Agreement") as a framework for completing its nationwide PCB
spill cleanup policy and evaluated the Consensus Agreement
as a source of information in developing the Agency's own
policy. The Agency and the Consensus Group shared two
general principles about the appropriate framework for a
nationwide PCB spills cleanup policy: (1) that the policy
should establish requirements designed to be effective in
the large majority of spill situations; and, (2) that the
risks posed by residual contamination (PCBs remaining after
cleanup) vary depending upon the potential for human
exposures.
Because of the tremendous variety of PCB spill situations,
developing a nationwide cleanup policy which incorporated
timely cleanup with prudent numerical cleanup standards
while at the same time maintaining a format that was
practicable in areas of cost and implementation for the
regulated community proved to be a very complicated and
XIV-2
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time-consuming task for the Agency. Consequently, EPA has
developed its National PCB Spill Cleanup Policy based upon
what the Consensus Group and others have indicated are the
more "typical" and thus most common types of PCB spills, as
well as the costs associated with cleanup following these
most common types of spills. Typical PCB spills involve the
limited release of PCBs during the course of EPA authorized
activities such as: the use of electrical equipment (e.g.,
transformers and capacitors), the servicing of electrical
equipment, and the storage for disposal of PCBs.
In establishing the cleanup policy for typical PCB spills,
EPA recognized that the risks posed by spills of PCBs vary,
depending upon the spill location and the amount of PCBs
spilled. Therefore, the PCB Spill Cleanup Policy now
requires cleanup of PCBs to different levels depending upon
spill location, the potential for exposure to residual PCBs
remaining after cleanup, the concentration of the PCBs
initially spilled, and the nature and size of the population
potentially at risk of exposure. Thus, the policy applies
the most stringent requirements for PCB spill cleanup to
areas where there is the greater potential for human
exposures to spilled PCBs. The policy applies less
stringent requirements for cleanup of PCB spills in areas
where the type and degree of contact present lower potential
exposures. Finally, even less stringent requirements apply
to areas where there is little potential for any direct
human exposure.
SCOPE OF THE POLICY
The PCB Spill Cleanup Policy establishes requirements for
the cleanup of spills resulting from the release of
materials containing PCBs at concentrations of 50 ppm or
greater including materials which EPA requires to be assumed
50 ppm or greater (i.e., untested mineral oil dielectric
fluid). The policy became effective on May 4, 1987, and
applies only to spills which occur after that date.
Existing spills which occurred prior to May 4, 1987 are
excluded from the policy and are to be cleaned up in
accordance with requirements established at the discretion
of EPA, usually through its Regional offices.
In addition, EPA excluded certain PCB spills from the policy
based upon location. PCB spills which contaminate surface
water, drinking water, sewers, animal grazing lands, and
vegetable gardens are excluded from the final cleanup
standards in the policy because these spills, due to their
location, potentially pose significantly greater exposure
risks to humans than those "typical" spills around which the
policy has been developed. For these "excluded" spills, the
XIV-3
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responsible party shall report the spill to the Regional EPA
Office and clean up the spill in accordance with site-
specific requirements established by the EPA Regional
Office. For all other PCB spills, EPA generally expects the
final cleanup standards of the policy to apply. In sum:
• EPA's PCB Spill Cleanup Policy went into effect
May 4, 1987.
• The policy applies to all PCB spills in
concentrations 50 ppm or greater (known or
assumed) which occur after May 4, 1987, except for
certain "excluded" spills which occur in higher
risk locations.
• "Excluded" spills are those which contaminate
surface water, drinking water, sewers, animal
grazing lands, and vegetable gardens. The cleanup
levels found in the PCB Spill Cleanup Policy do
not automatically apply to these spills. These
spills must be reported to the appropriate EPA
Regional Office no later than 24 hours after
discovery and cleaned up in accordance with site-
specific requirements as established by the
Regional EPA Office. These spills are subject to
all measures to minimize environmental
contamination in the policy.
Ql: Why does EPA refer to these new cleanup requirements as
"policy" instead of "regulations"?
Al: It is important to note that the PCB Spill Cleanup Policy is
an EPA policy statement which applies to existing
"spill/improper disposal" regulations. That is to say, when
a PCB spill occurs, under existing regulations, "improper
disposal" has taken place. The PCB Spill Cleanup Policy
provides a nationwide set of uniform reporting, cleanup, and
recordkeeping standards which, if followed precisely,
creates a presumption against both enforcement action for
penalties and for further cleanup under TSCA. It is not a
regulatory requirement that a PCB spill be cleaned up in
accordance with the spill policy; however, if a responsible
party wants EPA to presume that the responsible party should
not receive penalties from EPA 'for improper disposal due to
a PCB spill, the PCB Spill Cleanup Policy must be precisely
followed.
XIV-4
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KEY DEFINITIONS
The following are a few of the key definitions found in the
PCS Spill Cleanup Policy. All of the definitions listed in
the policy are not discussed here. Responsible parties
should refer to 40 CFR Part 761.123 for a detailed list of
all definitions found in the policy.
• "Spill" - The term as used in the policy means
both intentional and unintentional spills, leaks,
and other uncontrolled discharges where the
release results in any quantity of PCBs running
off or about to run off the external surface of
the equipment or other PCB source, as well as the
contamination resulting from those releases. The
policy applies to spills of 50 ppm or greater
PCBs. The concentration of PCBs spilled is
determined by the PCB concentration in the
material spilled as opposed to the concentration
of PCBs in the material onto which the PCBs were
spilled. Where a spill of untested mineral oil
occurs, the oil is presumed to contain greater
than 50 ppm, but less than 500 ppm PCBs, and is
subject to the relevant requirements of the
policy.
Q2: The spill policy defines "spill" by including the word
"leak" in the definition. Does this mean that all minor
"leaks" from electrical equipment must be cleaned up in
accordance with the spill policy?
A2: No. The spill policy only applies to leaks where "...the
release results in any quantity of PCBs running off or about
to run off the external surface of the equipment." EPA has
differentiated between these types of "migrating" leaks
which have or are about to contaminate other materials. The
policy does not apply to minor seepage ("weeps") from
electrical equipment bushings or coverplates. However, it
is important to understand that a minor leak of this type is
still considered "improper disposal" of PCBs and must be
controlled, repaired, and cleaned up by authorized servicing
of electrical equipment if the responsible party wishes to
continue to use or store for reuse the electrical equipment
and avoid improper disposal penalties from EPA.
• "Low-concentration PCBs" - This term means PCBs
that are tested and found to contain less than 500
ppm PCBs or those PCB-containing materials which
EPA allows to be assumed to be at concentrations
below 500 ppm (i.e., untested mineral oil
dielectric fluid). Consequently, a "low-
concentration" spill as referred to in the policy
XIV-5
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is a spill of material containing PCBs in
concentrations of 50-499 ppm, including spills of
untested mineral oil which must be assumed to be
50-499 ppm.
• "High-concentration PCBs" - This term means PCBs
that contain 500 ppm or greater PCBs, or those
materials which EPA requires to be assumed to
contain 500 ppm or greater PCBs in the 'absence of
testing. Consequently, a "high-concentration"
spill as referred to in the policy is a spill of
material containing PCBs in concentrations of 500
ppm or greater, including spills of material which
must be assumed to be 500 ppm or greater (e.g., an
untested transformer with no nameplate).
• "Outdoor electrical substations" - Outdoor
electrical substations are outdoor, fenced-off,
and restricted access areas used in the
transmission and/or distribution of electrical
power. For purposes of the spill policy, outdoor
electrical substations are defined as being
located at least 0.1 kilometer (km) from a
residential/commercial area. Outdoor electrical
substations which are located less than 0.1 km
from a residential/commercial area are considered
to be residential/commercial areas.
Q3: If a PCB spill occurs in an outdoor electrical substation
located more than 0.1 kilometer from a residential/
commercial building but less than 0.1 kilometer from the
residential/commercial property boundary line, should the
spill be cleaned up as an outdoor electrical substation
spill or a residential/commercial spill?
A3: EPA has established that when determining which spills fall
under the cleanup requirements for "outdoor electrical
substations," versus the more stringent cleanup requirements
for "residential/commercial areas," the responsible party
shall measure the 0.1 kilometer distance "...from the actual
site of the spill to the edge of the building where people
live or reside, or work."
• "Double wash/rinse" - The double wash/rinse
procedural performance standard applied in the
policy means a minimum requirement to cleanse
solid surfaces two times with an appropriate
solvent or other material in which PCBs are at
least 5 percent soluble (by weight). A volume of
PCB-free fluid sufficient to cover the
contaminated surface completely must be used in
XIV-6
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each wash/rinse. The wash/rinse requirement does
not mean the mere spreading of solvent or other
fluid over the surface, nor does the requirement
mean the once-over wipe with a soaked cloth.
Precautions must be taken to contain any runoff
resulting from the cleansing and to dispose
properly of wastes generated during the cleansing.
Q4: Can liquid cleaners and/or detergents be used throughout the
double wash/rinse procedure, or must more conventional
solvents such as kerosene be used?
A4: The spill policy allows the use of "other materials" in the
double wash/rinse procedure provided that PCBs are at least
5 percent soluble by weight in the material. Currently, EPA
has very little information on the effectiveness of
utilizing various detergents and cleaners in PCB spills
cleanup. The Agency is most interested in receiving input
in this area and encourages those in the regulated oommunity
to submit relevant data pertaining to various detergents and
other cleanup materials.
• "Standard wipe test" - For spills of high
concentration PCBs and large, low-concentration
spills, the policy requires cleanup of solid
surfaces to numerical surface standards and
sampling by a standard wipe test to verify that
the numerical standards have been met. This
definition constitutes the minimum requirements
for an appropriate wipe-testing protocol. A
standard-size template (10 centimeters by 10
centimeters) will be used to delineate the area of
cleanup; the wiping medium will be a gauze pad or
glass wool of known size which has been saturated
with hexane. It is important that the wipe be
performed very quickly after the hexane is exposed
to air.
• "Spill area" - This means the area of soil on
which visible traces of the spill can be observed
plus a buffer zone of 1 foot beyond the visible
traces. Any surface or object (e.g., concrete
sidewalk or automobile) within the visible traces
area, or on which visible traces of the spilled
material are observed, is included in the spill
area. This area represents the minimum area
assumed to be contaminated by PCBs in the absence
of precleanup sampling data and is thus the
minimum area which must be cleaned.
XIV-7
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• "Spill boundaries" - This term means the actual
area of contamination as determined by postcleanup
verification sampling, or by precleanup sampling
to determine actual spill boundaries. EPA can
require additional cleanup when necessary to
decontaminate all areas within the spill
boundaries to the levels required in the policy.
Q5: What is the difference between the "spill area" and the
"spill boundaries"?
A5: The "spill area" is simply that area where traces of the
spilled material can be seen plus a 1-foot buffer zone. The
"spill boundaries" on the other hand means the actual area
of contamination and includes contamination that might not
be visible with the naked eye.
PCS SPILL REPORTING REQUIREMENTS
EPA has established two basic reporting requirements for PCB
spills under the TSCA spill policy. In addition, reporting
may also be required under the Clean Water Act (CWA) or
Comprehensive Environmental Response Compensation and
Liability Act (CERCLA). For example, under the CERCLA
National Contingency Plan, all spills involving 1 pound or
more of PCB material must currently be reported to the
National Response Center (NRC) at 1-800-424-8802. The
reporting requirements found in the PCB Spill Policy are
designed to be consistent with existing reporting
requirements found in other regulatory acts. Simply stated,
only those PCB spills occurring in certain high-risk areas,
or PCB spills involving a significant volume of PCBs
spilled, are required to be reported under the TSCA PCB
Spill Cleanup Policy. These are:
• All PCB spills, 50 ppm or greater, which
contaminate surface waters, sewers and sewer
treatment plants, private or public drinking water
sources, animal grazing lands, and vegetable
gardens must be reported to the appropriate EPA
Regional Office of Pesticides and Toxic Substances
(see page xiv of this document) in the shortest
possible time after discovery, but in no case
later than 24 hours after discovery.
• All PCB spills, 50 ppm or greater, involving 10
pounds or more of PCBs (generally 1 gallon of
Askarel) must be reported to the appropriate EPA
Regional Office of Toxics and Pesticides in the
shortest possible time after discovery but in no
case later than 24 hours after discovery.
XIV-8
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Q6: When the spill policy refers to 10 pounds or more of PCBs,
is the requirement to report a spill of 10 pounds or more of
PCB containing material (i.e., oil and PCBs), or 10 pounds
or more of actual PCBs on a dry-weight basis?
A6: The reporting requirement specified in the PCB spill policy
only requires "...spills of 10 pounds of pure PCBs or more
by weight to be reported."
NOTE: As of August 14, 1989, EPA changed the reportable
quantity for PCBs to 1 Ib. under the CERCLA National
Contingency Plan, so that spills of 1 Ib. or more of PCBs
must be reported to the National Response Center. The PCB
Spill Cleanup Policy has not been revised to reflect this
change. Consequently, a 1 Ib. or greater PCB spill must be
reported to the NRC but not to EPA. A PCB spill of 10 Ibs.
or more must be reported to the appropriate Regional
Administrator.
DETERMINATION OF SPILL BOUNDARIES
For spills where there are insufficient visible traces yet
there is evidence of a leak or spill, the boundaries of the
spill are to be determined by testing the area for PCBs
using a statistically based sampling scheme. (See
Sampling/Testing Requirements.)
CLEANUP. RECORDKEEPING. AND TESTING REQUIREMENTS
The PCB Spill Cleanup Policy establishes four categories of
PCB spills: (1) small, low-concentration spills, (2) large,
low-concentration spills, (3) high-concentration spills, and
(4) excluded spills. As discussed earlier, EPA recognized
that the risks posed by spills of PCBs vary, depending upon
the spill location and the amount of PCBs spilled.
Therefore, the spill policy requires cleanup of PCBs to
different levels depending upon spill location, the
potential for exposure to residual PCBs remaining after
cleanup, the concentration of PCBs initially spilled, and
the nature and size of the population potentially at risk of
exposure. The following is a general overview of the
various cleanup, recordkeeping, and testing requirements
found in the policy. Responsible parties should refer to 40
CFR 761.125 and 761.130 for detailed information.
SMALL. LOW-CONCENTRATION SPILLS
Small, low-concentration spills are spills of materials
containing 50-499 ppm PCBs and which involve less than 1
XIV-9
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pound of PCBs by weight or less than 270 gallons of untested
mineral oil. These spills are considered to be the most
typical and most common types of spills and usually involve
smaller quantities of low-level PCBs. Consequently, EPA has
established a basic "performance standard" for proper
cleanup of spills of this type and requires specific records
and statements of certification to be documented and
maintained by the responsible party.
• CLEANUP REQUIREMENTS:
(1) All contaminated solid surfaces must be
double washed/rinsed.
(2) Any contaminated indoor, residential surfaces
must be cleaned to 10 micrograms per 100
square centimeters (10 /xg/100 cm2) .
(3) All soil within the spill area (i.e., visible
traces plus a 1 lateral foot buffer) must be
excavated and the ground be restored to its
original configuration by back-filling the
area with clean soil (i.e., less than 1 ppm).
(4) The above cleanup must be completed within 48
hours of discovery of the spill.
Q7: Is "wipe testing" required following cleanup of a solid
surface involved in a "small, low-concentration" spill?
A7: The only instance in which wipe testing would be required
after cleanup of a small, low-concentration spill is if PCB
contamination of an indoor, residential surface occurred.
This type of solid surface would have to be wipe tested
after cleanup and shown to contain no greater than 10 /ig/100
cm2 of residual PCB contamination. All other solid surfaces
could simply be double washed/rinsed with no wipe testing
required.
Q8: Is there a minimum depth requirement when excavating soil
within the spill area?
A8: Due to the wide variety of ground media from one area of the
country to another, EPA has placed no specific depth
requirement in the performance standard for cleanup of
small, low-concentration spills. Responsible parties should
review each spill on a case-by-case basis and excavate soil
to a reasonable depth based upon the type of soil and
visible traces of spilled material.
Q9: The spill policy requires the excavated area be restored to
its original configuration by back-filling the area with
clean soil less than 1 ppm PCBs. Does back-fill soil have
to be tested for PCBs prior to being used?
XIV-10
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A9: No. EPA does not require soil to be used for back-filling to
be tested and proven less than 1 ppm. Responsible parties
should simply use soil which, to the best of their
knowledge, contains no PCB contamination.
Q10: Can cleanup of an untested mineral oil spill be delayed to
first test the mineral oil and determine if the spill is in
fact 50 ppm or greater?
A10: Untested mineral oil which must be assumed to contain 50-499
ppm PCBs can be tested to determine the actual PCB
concentration. However, the PCB Spill Cleanup Policy does
not provide for additional "testing time" which would delay
initiation of the cleanup of a small, low-concentration
spill beyond the 48-hour requirement.
Qll: Are there any instances in which the initiation of cleanup
of a small, low-concentration spill may be delayed beyond 48
hours?
All: Yes. Initiation of cleanup may be delayed beyond 48 hours in
case of circumstances including but not limited to: civil
emergency, adverse weather conditions, lack of access to the
site, and emergency operating conditions. The occurrence of
a spill on a weekend or overtime costs are not acceptable
reasons for delay.
• RECORDKEEPING AND CERTIFICATION REQUIREMENTS:
At the completion of cleanup of a small, low-
concentration spill, the responsible party or
appropriate agent must document the cleanup with
records and certification of decontamination. The
records and certification must be maintained for a
period of 5 years. The records and certification
must include the following:
(1) The source of the spill (e.g., type of
equipment).
(2) The date and time the spill occurred {actual
or estimated).
(3) The date and time cleanup was completed or
terminated.
(4) The nature and duration of why initiation of
cleanup was beyond the 48-hour requirement.
(5) A brief description of the spill location.
(6) Precleanup sampling data used to determine
spill boundaries if there were insufficient
visible traces.
(7) A brief description of any solid surfaces
which were double washed/rinsed and the
methods used.
XIV-11
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(8) The approximate depth of soil excavation and
the amount of soil removed.
(9) A certified statement signed by the
responsible party (e.g., facility manager or
foreman) stating that the cleanup
requirements have been met and that the
information contained in the records is true
to the best of his/her knowledge.
LARGE. LOW-CONCENTRATION SPILLS AND HIGH-CONCENTRATION
SPILLS OF ANY QUANTITY
The next two categories of PCB spills established in the PCB
Spill Cleanup Policy are large, low-concentration spills and
high-concentration spills of any amount of PCBs.
Large, low-concentration spills are spills of materials
containing 50-499 ppm PCBs and which involve more than 1
pound of PCBs by weight or more than 270 gallons of untested
mineral oil. These spills involve larger quantities of low-
level PCBs and thus present more widespread contamination
and a greater risk of potential exposure to humans.
High-concentration spills are spills of materials containing
PCBs in concentrations of 500 ppm or greater. PCB spills of
these higher level concentrations, in any quantity, present
a more significant risk of exposure to humans.
Because of the greater risk of potential exposure to humans
from large, low-concentration spills and all high-
concentration spills, EPA requires more stringent and
detailed numerical cleanup standards for these types of
spills. Numerical cleanup standards are based upon the
spill location with the most stringent requirements applied
to PCBs spilled in residential/commercial/unrestricted
access rural areas. The spill policy allows for less-
stringent numerical cleanup standards for PCBs spilled in
industrial and other restricted-access areas such as utility
power plants. And finally, the least stringent numerical
cleanup standards apply to PCB spills in outdoor electrical
substations.
In order to simplify the PCB Spill Cleanup Policy to the
extent possible, EPA structured the policy so that the
cleanup, recordkeeping, and testing requirements for "large,
low-concentration spills" and "high-concentration spills"
are identical. The following is a brief overview of these
requirements based upon spill location. Responsible parties
should refer to 40 CFR 761.125 for detailed requirements and
standards.
XIV-12
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• IMMEDIATE REQUIREMENTS:
The following four actions must be taken as quickly as
possible and within no more than 24 hours (48 hours for
PCB Transformer spills) after discovery of the spill.
(1) Report the spill to the NRC if 1 pound or more of
pure PCBs were spilled, and to the EPA Regional
Office if 10 Ibs. or more of pure PCBs were
spilled.
(2) Effectively cordon off and restrict access to the
spill area plus a 3-foot buffer, and place clearly
visible signs advising persons to avoid the area.
(3) Record and document the spill area noting the
extent and center of all visible traces. If there
are no visible traces, contact the EPA Regional
Office for guidance in completing a statistical
sampling of the spill area to determine spill
boundaries.
(4) Initiate cleanup of all visible traces on solid
surfaces and initiate excavation of any visibly
contaminated soil.
Q12: Are there any instances in which the "immediate
requirements" for large, low-concentration and high-
concentration spills may be delayed beyond 24 hours?
A12: Yes. The above immediate requirements (2), (3), and (4) may
be delayed beyond 24 hours in case of circumstances
including but not limited to: civil emergency, adverse
weather conditions, lack of access to the site, and
emergency operating conditions. The occurrence of a spill
on a weekend or overtime costs are not acceptable reasons
for delay.
• CLEANUP REQUIREMENTS - OUTDOOR ELECTRICAL
SUBSTATIONS:
(1) Contaminated solid surfaces must be cleaned
to a level not exceeding PCB concentrations
of 100 /xg/100 cm2.
(2) Contaminated soil must be excavated to 25 ppm
PCBs, or to 50 ppm PCBs provided that a
notice indicating the 50 ppm PCB level is
visibly placed in the area.
• CLEANUP REQUIREMENTS - OTHER RESTRICTED ACCESS
AREAS:
(1) Contaminated solid surfaces must be cleaned
to either 10 /-ig/100 cm2 or 100 /ig/100 cm2
depending upon whether the contaminated
XIV-13
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surface is indoors or outdoors, high-contact
or low-contact, impervious or nonimpervious.
Responsible parties should refer to 40 CFR
761.125 for a detailed description of final
numerical cleanup standards.
(2) Contaminated soil must be excavated to 25 ppm
PCBs.
• CLEANUP REQUIREMENTS - NONRESTRICTED ACCESS AREAS:
(1) Contaminated furnishings, toys, and other
easily replaceable household items must be
disposed of in accordance with disposal
requirements under 40 CFR 761.60 and replaced
by the responsible party.
(2) Contaminated solid surfaces must be cleaned
to either 10 pig/100 cm2 or 100 pig/100 cm2
depending on whether the contaminated surface
is indoors or outdoors, high-contact or low-
contact , impervious or nonimpervious.
Responsible parties should refer to 40 CFR
761.125 for a detailed description of final
numerical cleanup standards.
(3) Contaminated soil must be excavated to 10 ppm
PCBs provided the soil is excavated to a
minimum depth of 10 inches. The excavated
soil must be replaced with clean soil less
than 1 ppm PCBs and the site restored to its
original configuration.
Q13: Does a "high-concentration" or "large, low-concentration"
spill in a nonrestricted access area always require
excavating the contaminated soil to a minimum depth of 10
inches?
A13: No. Excavation of the soil may be terminated before reaching
a 10-inch depth provided there are no detectible PCBs at the
level of termination (i.e., less than 1 ppm). In other
words, excavation must continue until: (1) there are no
detectible PCBs at the level of termination, or (2) there is
not greater than 10 ppm contamination at a minimum 10-inch
depth, or (3) excavation must continue beyond 10-inch depth
if necessary to achieve the minimum 10 ppm cleanup standard.
Q14: Is there a minimum quantity level for required cleanup of a
"high-concentration" PCB spill?
A14: No. High-concentration spills (500 ppm or greater) must be
cleaned up in accordance with the PCB Spill Cleanup Policy
regardless of the quantity spilled. Even spills from small,
unregulated items such as PCB small capacitors are
XIV-14
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considered improper disposal and should be cleaned up in
accordance with the spill policy.
Q15: Is there a time limit on the final cleanup of "large, low-
concentration" and "high-concentration" spills?
A15: Although the spill policy requires certain "immediate"
actions, as described above, EPA has not placed a time limit
on completion of cleanup since the time required will vary
from case to case. However, EPA expects cleanup to be
achieved promptly in all cases and will consider the
promptness of completion in determining whether a
responsible party made good faith efforts to clean up in
accordance with the policy.
• RECORDKEEPING REQUIREMENTS:
At the completion of cleanup of a large, low-
concentration or high-concentration spill, the
responsible party or appropriate agent must
document the cleanup with records of
decontamination. These records must be maintained
for a period of 5 years. The records must include
the following:
(1) The source of the spill (e.g., type of
equipment).
(2) The date and time the spill occurred (actual
or estimated).
(3) The date and time cleanup was completed or
terminated.
(4) The nature and duration of any delayed
cleanup.
(5) A brief description of the spill location.
(6) Precleanup sampling data used to determine
spill boundaries if there were insufficient
visible traces.
(7) A brief description of any solid surfaces
cleaned.
(8) The approximate depth of soil excavation and
the amount of soil removed.
(9) Postcleanup verification sampling data (test
results).
• SAMPLING/TESTING REQUIREMENTS:
Under the PCB spill policy requirements for large,
low-concentration and high-concentration spills,
responsible parties are required to conduct post-
cleanup sampling to verify the level of cleanup.
The responsible party, or designated agent, may
XIV-15
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use any statistically valid, reproducible,
sampling scheme (either random samples or grid
samples), provided the following requirements are
satisfied:
(1) The sampling area is the greater of: (a) an
area equal to the area cleaned plus an
additional 1-foot boundary, or (b) an area 20
percent larger than the original area of
contamination.
(2) The sampling scheme must ensure 95 percent
confidence against false positives.
(3) The number of samples must be sufficient to
ensure that areas of contamination of a
radius of 2 feet or more within the sampling
area will be detected, except that the
minimum number of samples is 3 and the
maximum number of samples is 40.
(4) The sampling scheme must include calculation
for expected variability due to analytical
error.
EXCLUDED SPILLS
As discussed earlier, certain PCB spills which occur in
areas of higher potential risk and exposure to humans are
specifically excluded from the spill policy. For each of
the following spill situations, the responsible party must
contact the appropriate Regional EPA Office of Pesticides
and Toxic Substances (see page xiv of this document) within
24 hours of discovery of the spill. The EPA Regional Office
will establish cleanup standards and requirements for the
"excluded" spills on a case-by-case basis. The following
six spill situations are "excluded spills" and are not
included in the cleanup, recordkeeping, and sampling
requirements of the PCB Spill Cleanup Policy. They are
subject, however, to all the measures in the policy that
minimize further environmental contamination.
• Spills that result in the direct contamination of
surface waters.
• Spills that result in the direct contamination of
sewers or sewage treatment plants.
• Spills that result in the direct contamination of
any private or public drinking water sources or
distribution systems.
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• Spills which migrate to and contaminate surface
waters, sewers, or drinking water supplies before
cleanup has been completed in accordance with the
policy.
• Spills that contaminate animal grazing lands.
• Spills that contaminate vegetable gardens.
Q16: Are commercial farming crop lands included in the definition
of "vegetable gardens"? Also, are residential gardens
included in the definition?
A16: Generally yes. EPA performed some preliminary analysis of
the risks posed by the consumption of vegetables grown on a
spill area cleaned to 25 ppm PCBs in the case of farmland
and 10 ppm in the case of residential gardens. Assuming
that vegetables grown on a residential garden or farm are
the entire vegetable diet of the site residents, cleaning
soil to the levels in the policy may not be adequate. Also,
EPA has concluded that vegetables are more likely to become
contaminated through contact with contaminated dirt rather
than plant uptake, especially root crops such as carrots and
potatoes.
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CHAPTER XV
RECORDKEEPING
AND REPORTING
40 CFR 761.180(a): PCBs and PCB Items In-Service or Projected for
Disposal (page XV-2)
40 CFR 761.180(b): Disposers and Commercial Storers of PCB Waste
(page XV-6)
Incineration Facilities (page XV-9)
Chemical Waste Landfill Facilities (page XV-10)
High Efficiency Boiler Facilities (page XV-10)
Special Recordkeeping Requirements (page XV-11)
-------
- RECORDKEEPING AND REPORTING -
EPA finalized specific recordkeeping and reporting
regulations with the promulgation of the "PCB Ban Rule" in
1979. These regulations outlined the various records and
reports which owners, storers, and disposers of PCBs and PCB
Items were required to develop and maintain. The
Notification and Manifesting Rule, published on December 21,
1989 (54 FR 52716) changed the format of the recordkeeping
requirements for PCBs that were in place since 1979. Year
after year, "improper recordkeeping" continues to be the
single most frequent area of noncompliance in each of the
ten EPA regions across the country. The following is a
brief overview of the recordkeeping and reporting
requirements for PCBs and PCB Items. One should pay
particular attention to the changes as a result of the
Notification and Manifesting Rule. Responsible parties are
encouraged to refer to 40 CFR 761.180 and the Notification
and Manifesting Rule for a detailed outline of the "Records
and Reports" regulations.
The Notification and Manifesting Rule adopts additional
recordkeeping and reporting requirements to complete the
tracking system for PCB wastes. The rule requires that the
manifests themselves be retained as records by waste
handlers, and it requires reporting to EPA in the event of
irregularities in the transport of regulated wastes. These
reports depend largely on information derived from
particular manifests.
Three of the waste tracking reports are modeled after their
RCRA counterparts. The rule requires "Exception Reports" to
be filed with EPA whenever a generator has not received
verification of delivery within 45 days. Also, a
"Discrepancy Report" is required of storage or disposal
facilities in those cases where the waste actually delivered
to them does not correspond exactly with the types and
quantities described on the manifest. Third, an
"Unmanifested Waste Report" is required of disposers or
storers in those instances in which waste arrives at a
facility unaccompanied by a required manifest.
The rule adds one additional reporting requirement for which
there is no counterpart under RCRA. This requirement is the
"One-year Exception Report," intended to bolster EPA's
ability to enforce the requirement under TSCA regulations
that limits storage of PCBs prior to disposal to no more
than one year. Information on when items of PCB waste were
removed from use is included with the manifests that
accompany the waste from generation to disposal. Disposers
are required to certify to the date of disposal of PCB waste
XV-1
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manifested to them, and in the event more than one year has
elapsed since the PCBs were removed from use, a report must
be filed with EPA.
Finally, the rule adds several amendments to the existing
PCB recordkeeping provisions that concern the Annual
Document requirements for the users, storers, and disposers
of PCBs. The most significant of these amendments is the
requirement that each disposer and commercial storer of PCB
waste submit on July 15 of each year an "Annual Report,"
which is a summary of the previous calendar year's PCB
activity at the facility. The report will be submitted to
the appropriate EPA Regional Administrator.
40 CFR 761.180(a)t PCBs and PCB Items In-Service or
Projected for Disposal
Beginning February 5, 1990, each owner or operator of a
facility, other than a commercial storer or disposer of PCB
waste, using or storing at one time any of the following
quantities of PCBs and/or PCB Items is required to develop
and maintain Annual Records and by July 1 prepare an Annual
Document Log on the disposition PCBs and PCB Items. The
quantity limits are:
• 45 kilograms (99.4 pounds) or more of PCBs (50 ppm
or greater) contained in PCB Containers, or
• one or more PCB Transformers (500 ppm or greater),
or
• 50 or more PCB large, high- or low-voltage
capacitors.
If any of these three quantity limits is met or exceeded,
the owner or operator of the facility must maintain "Annual
Records" for the PCBs and PCB Items, as well as develop and
prepare an "Annual Document Log" each calendar year until
the facility ceases using, storing, or disposing of PCBs and
PCB Items. "Annual Records" and "Annual Document Logs" must
be maintained for at least 3 years after that time.
The Annual Records include the following:
• All signed manifests generated by the facility
during the calendar year.
• All Certificates of Disposal received at the
facility during the calendar year.
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An Annual Document Log is the summary of the detailed
information maintained at the facility on its waste handling
activities, including:
• The identity of the facility and the year covered
by the Annual Document Log.
• The unique manifest number of every manifest
generated by the facility during the calendar year
and from each manifest and for unmanifested waste
that may be stored at the facility, the following
information:
• Weight in kilograms for bulk PCB waste (e.g.,
in a tanker or truck), the first date it was
removed from service for disposal, date it
was placed into transport for off-site
storage or disposal, and the date of disposal
if known.
• The serial number or other means of
identifying each PCB Article, the weight in
kilograms of the PCB waste in each PCB
Article, the date removed from service for
disposal, the date placed in transport for
off-site storage or disposal, and the date of
disposal if known.
• The unique number identifying each PCB
Container, a description and total weight in
kilograms of the contents of the container,
the first date material was placed into the
container for disposal, the date each
container was placed in transport for storage
or disposal, and the date of disposal if
known.
• The unique number identifying each PCB
Article Container, a description and total
weight in kilograms of the contents of the
PCB Article Container, the first date a PCB
Article was placed into the container for
disposal, the date the PCB Article container
was placed in transport for off-site storage
or disposal, and the date of disposal if
known.
• The total number by specific type of PCB Articles
and the total weight in kilograms of PCBs in PCB
Articles, the total number of PCB Article
Containers and total weight in kilograms of the
contents of the PCB Article Containers, the total
XV-3
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number of PCB Containers and the total weight in
kilograms of the contents of the PCB Containers,
and the total weight in kilograms of bulk PCB
waste that was placed into storage for disposal or
disposed during the calendar year.
• The total number of PCB Transformers and total
weight in kilograms of the PCBs contained in the
transformer remaining in-service at the end of the
calendar year.
• The total number of Large, High- or Low-Voltage
PCB Capacitors remaining in-service at the end of
the calendar year.
• The total weight in kilograms of any PCBs and PCB
Items in PCB Containers, including the
identification of container contents, remaining
in-service at the facility at the end of the
calendar year.
• Weights in kilograms, number and description of
any PCBs or PCB Item shipped from or shipped to
another facility owned or operated by the same
generator.
• A record of each telephone call or other means of
verification agreed upon by both parties to each
designated commercial storer or designated
disposer to confirm receipt of PCB waste
transported by an independent transporter, as
required by § 761.208.
NOTE: Readers are requested to closely review
761.180(a)(2) for the detailed information
required in this Annual Document Log.
Ql: Are the Annual Records and Annual Document Logs as specified
at § 761.180(a)(1) and (2), required to be sent in to EPA?
Al: No. Unless specifically requested, a facility's PCB records
should be maintained in-house and made available for
inspection by authorized EPA personnel. [The Annual Report
as specified at § 761.180(b) (which is discussed in the next
section) is the only recordkeeping document that need be
sent to EPA.]
Q2: Is a facility required to obtain a "Certificate of Disposal"
for each shipment of PCBs for disposal?
XV-4
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A2: "Certificates of Disposal" are industry-developed documents
normally used by PCB brokers and disposal companies to
assure their customers that final disposal has, in fact,
taken place. Under §761.218 owners and operators of
disposal facilities are now required to prepare a
Certificate of Disposal for PCB waste. The generator of the
waste (i.e., either the original generator or the
owner/operator of a storage facility that has co-mingled PCB
wastes) would be required to maintain signed Certificates of
Disposal.
Q3: Is an Annual Document Log and Annual Record supposed to
report activity from July 1 of the preceding year to June 30
of the year the records are developed?
A3: No. An Annual Document Log and Annual Record should cover
activity which took place the previous calendar year
(January 1 - December 31). The regulations allow a 6-month
period to July 1 to develop and complete the Annual Document
Log and Annual Record. NOTE: For 1989 the documents shall
cover the period from January 1, 1989 to February 5, 1990
(the effective date of the Notification and Manifesting
Rule). For 1990 the documents shall cover the period from
February 6, 1990 to December 31, 1990.
Q4: Our facility is past due on several years of Annual
Documents [NOTE: "Annual Documents" is the term used to
describe the records and reports that were to be developed
and kept at the facility before the Records and Monitoring
section (761.180) of the regulations was amended in the
Notification and Manifesting rule.] Is it illegal to go
back now and develop these required reports?
A4: If a facility has accurate past records and information, it
is advisable to prepare all required Annual Documents, even
those that are currently delinquent. A facility compiling
such reports may receive an EPA penalty for completing
Annual Documents after the allowed 6-month period.
Penalties will be assessed for those who do not file these
reports.
Q5: What exactly does the term "removed from service" mean?
A5: "Removed from service," when used in the context of the PCB
regulations, specifically refers to the designation of a PCB
Item for the end of its useful life or, in other words,
"date of removal from service for disposal." Unfortunately,
the term "removed from service," as used in the regulations,
has often been misinterpreted by those in the regulated
community. This is particularly so in the case of electric
utilities where the term has been used for years in
conjunction with a transformer or other piece of electrical
XV-5
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equipment being "changed out" and/or "brought in from the
field." Many times these types of "change outs" involve
electrical equipment that is in sound functional condition
(intact and nonleaking) and is simply placed back into
"stock" (storage for reuse) to be reused on an as-needed
basis. In other instances, equipment is "changed-out" when
it is in need of and will receive repair work before going
back into "stock" for future use. In either case, this is
not what EPA means when by "removed from service." On the
other hand, electrical equipment which is legally stored for
reuse, or stored for repair by authorized servicing, is just
as much "remaining jji service" as a unit in the field
operating under loaded conditions. In fact, once a PCB Item
(50 ppm or greater) has been "removed from service for
disposal," EPA does not allow that unit to be placed back
into service, repaired, rebuilt, or sold for reuse. In
addition, the one year storage for disposal requirement
begins on the date of removal from service for disposal.
Q7: If I drain a PCB-Contaminated Transformer (50 - 499 ppm
PCBs) prior to shipment for disposal, must I prepare an
annual document?
\
A7: If the total weight of the liquid drained into the
container(s) is 45 kgs. (99.4 Ibs.) or more you must prepare
an annual document for the PCB Container(s). If you are
shipping only the drained transformer carcass you need not
prepare an annual document.
40 CFR 761.180(b); Disposers and Commercial Storers of PCB
Waste
Beginning February 5, 1990, each owner or operator of a
facility (including high efficiency boiler operations) used
for the commercial storage or disposal of PCBs and PCB Items
is required to prepare and maintain an Annual Record on the
disposition of all PCBs and PCB Items at the facility and
prepare and maintain a written Annual Document Log for PCBs
and PCB Items by July 1 that were handled as PCB waste at
the facility during the previous calendar year. In
addition, by July 15, the owner or operator of the facility
must submit to the appropriate EPA Regional Administrator an
"Annual Report" which is a brief summary of the information
included in the Annual Document Log. (See § 761.180(b)(3)
for further detail.) NOTE: For 1989 the documents shall
cover the period from January 1, 1989 to February 5, 1990
(the effective date of the Notification and Manifesting
Rule). For 1990 the documents shall cover the period from
February 6, 1990 to December 31, 1990.
XV-6
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The Annual Records include the following:
• All signed manifests generated or received at the
facility during the calendar year.
• All Certificates of Disposal that have been
generated or received by the facility during the
calendar year.
The written Annual Document Log includes the following:
[Readers are requested to closely review § 761.180(b) (2) for
the detailed information required in this Annual Document
Log.]
• The name, address, and EPA identification number
of the storage or disposal facility covered by the
annual document log and the calendar year covered
by the annual document log.
• For each manifest generated or received by the
facility during the calendar year, the unique
manifest number and the name and address of the
facility that generated the manifest the
following information:
• The date when any PCBs and PCB Items were
disposed of at the facility or transferred to
another disposal or storage facility,
including the identification of the specific
types of PCBs and PCB Items that were stored
or disposed of.
• A summary of the total weight in kilograms of
PCBs and PCB Articles in containers and the
total weight of PCBs contained in PCB
Transformers that have been handled at the
facility during the previous calendar year.
This summary shall provide totals of the
above PCBs and PCB Items which have been:
(1) received during the year; (2) transferred
to other facilities during the year; and (3)
retained at the facility at the end of the
year.
• The contents of PCB Containers shall be
identified. When PCB Containers and PCBs
contained in a transformer are transferred to
other storage or disposal facilities, the
identification of the facility to which such
PCBs and PCB Items were transferred shall be
included in the document.
XV-7
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• The total number of any PCB Articles or PCB
Equipment not in PCB Containers received
during the calendar year, transferred to
other storage or disposal facilities during
the calendar year, or remaining on the
facility site at the end of the calendar year
shall be included.
• The identification of the specific types of
PCB Articles and PCB Equipment received,
transferred, or remaining on the facility
site shall be indicated.
• When PCB Articles and PCB Equipment are
transferred to other storage or disposal
facilities, the identification of the
facility to which the PCB Articles and PCB
Equipment were transferred must be included.
Q7: Do the above requirements for a PCB storage facility apply
to an electric utility which has set up a PCB storage
facility for their own PCBs and PCB Items?
A7: No. An electric utility which has set up a PCB storage
facility for their own PCBs and PCB Items is only required
to prepare a document under the criteria outlined for owners
and users of PCBs at 761.180(a). The recordkeeping
requirements for disposal and storage facilities outlined
under 761.180(b) do not apply to electric utilities or
others who are simply storing their own PCBs. They are not
commercial storers of PCB waste.
The above documents must be completed for each calendar year
until the facility is no longer used for the storage or
disposal of PCBs and PCB Items. All documents that are
required to be maintained at the facility must be maintained
for at least 3 years after that time; except in the case of
chemical waste landfills. These documents must be
maintained at least 20 years after the chemical waste
landfill is no longer used for the disposal of PCBs and PCB
Items.
Other PCB Records: In addition to "Annual Records" and
"Annual Documents," owners or operators of facilities using
or storing PCBs and PCB Items are required to maintain the
following records and reports when applicable:
• PCB Transformer Inspections (Quarterly and/or
Yearly)
• PCB Transformer Registrations (Fire Departments
and Building Owners)
XV-8
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PCB Container/Drum/Bulk Tank Identification Logs
PCB Spill Reports (See "PCB Spill Cleanup Policy")
Spill Prevention Control and Countermeasure (SPCC)
Plans for Storage of Large Tanks
PCB Test/Sampling Data (See "PCB Spill Cleanup
Policy")
Data on PCB Transformers installed for either
emergency or reclassification purposes
INCINERATION FACILITIES
In addition to the required documents which must be prepared
by all PCB disposal facilities, each owner or operator of a
PCB incinerator facility shall also collect and maintain the
following information:
• When PCBs are being incinerated, the following
continuous and short-interval data:
(1) the rate and quantity of PCBs fed to the
combustion system as required in
761.70(a)(3);
(2) the temperature of the combustion process as
required in 761.70(a)(4); and
(3) the stack emission product to include O2, CO,
and C02 as required in 761.70(a)(7).
• When PCBs are being incinerated, data and records
on the monitoring of stack emissions as required
in 761.70 (a) (7) .
• The total weight in kilograms of any solid
residues generated by the incineration of PCBs and
PCB Items during the calendar year.
• The total weight in kilograms of any solid
residues disposed of by the facility in chemical
waste landfills during the calendar year.
• The total weight in kilograms of any solid
residues remaining on the facility site.
• When PCBs and PCB Items are being incinerated,
additional periodic data shall be collected and
XV-9
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maintained as specified by the Regional
Administrator pursuant to 761.70(d)(4).
• Upon any suspension of the operation of any
incinerator pursuant to 761.70(a)(8), the owner or
operator of such an incinerator shall prepare a
document. This document shall, at a minimum,
include the date and time of the suspension and an
explanation of the circumstances causing the
suspension of operation. The document shall be
sent to the appropriate Regional Administrator
within 30 days of any such suspension.
PCB incinerator facilities must collect and maintain the
above information for a period of at least 3 years from the
date the information was collected.
CHEMICAL WASTE LANDFILL FACILITIES
In addition to the required documents which must be prepared
by all PCB disposal facilities, each owner or operator of a
chemical waste landfill facility shall also collect and
maintain the following information:
• Any water analysis obtained in compliance with
761.75(b) (6) (iii); and
• Any operations records including burial
coordinates of wastes obtained in compliance with
761.75(b) (8) (ii) .
Chemical waste landfill facilities must collect and maintain
the above information until at least 20 years after the
chemical waste landfill is no longer used for the disposal
of PCBs and PCB Items.
HIGH EFFICIENCY BOILER FACILITIES
In addition to the required documents which must be prepared
by all PCB disposal facilities, each owner or operator of a
high efficiency boiler used for the disposal of liquids
containing between 50 and 500 ppm PCBs shall also collect
and maintain the following information:
• For each month PCBs are burned in the boiler, the
carbon monoxide and excess oxygen data required in
761. 60 (a) (2) (iii) (A) (8) and
761.60 (a) (3) (iii) (A) (8) .
XV-10
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• The quantity of PCBs burned each month as required
in 761.60(a)(2)(iii)(A) (7) and
761.60(a) (3) (iii) (A) (7).
• For each month PCBs (other than mineral oil
dielectric fluid) are burned, the chemical
analysis data of the waste as required in
761.60(a) (3) (iii) (B) (6).
High efficiency boiler facilities used for the disposal of
liquids containing between 50 and 500 ppm PCBs must collect
and maintain the above information for a period of at least
3 years from the date the information was collected.
SPECIAL RECORDKEEPING REQUIREMENTS
In addition to the documents and other records outlined in
Units II through V above, each owner or operator of a PCB
storage or disposal facility (including high efficiency
boiler operations) shall collect and maintain the following
information:
• All documents, correspondence, and data that have
been provided to the owner or operator of the
facility by any state or local government agency
and that pertain to the storage or disposal of
PCBs and PCB Items at the facility.
• All documents, correspondence, and data that have
been provided by the owner or operator of the
facility to any state or local government agency
and that pertain to the storage or disposal of
PCBs and PCB Items at the facility.
• Any applications and related correspondence sent
by the owner or operator of the facility to any
local, state, or Federal authorities in regard to
waste water discharge permits, solid waste
permits, or other permits or authorizations such
as those required by 761.70(d) and 761.75(c).
Each owner or operator of a PCB storage or disposal facility
must collect and maintain these special records for a period
of at least 3 years after the facility is no longer used for
the storage or disposal of PCBs and PCB Items except that in
the case of chemical waste landfills, the special records
must be maintained at least 20 years after the landfill is
no longer used for the disposal of PCBs and PCB Items.
XV-11
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CHAPTER XVI
PCS TESTING PROCEDURES
Oil-Filled Electrical Equipment (page XVI-l)
Waste Oil (page XVI-2)
PCB Spills (page XVI-3)
-------
- PCB TESTING PROCEDURES -
OIL-FILLED ELECTRICAL EQUIPMENT
The PCB regulations under TSCA do not require electrical
equipment containing mineral oil dielectric fluid to be
tested for PCB contamination. Instead, EPA allows the
continued use and storage for reuse of untested mineral oil
electrical equipment provided the equipment is intact and
nonleaking, and provided the equipment is used in compliance
with all applicable "assumption" requirements. However,
owners or operators of mineral oil dielectric fluid
electrical equipment may use the following procedures to
determine the concentration of PCBs in the dielectric fluid:
• Mineral oil dielectric fluid removed from
electrical equipment may be collected in a common
container, provided that no other chemical
substances or mixtures are added to the container.
This common container option does not permit
dilution of the collected oil. Mineral oil that
is assumed or known to contain 50-ppm PCBs or
greater must not be mixed with mineral oil that is
known or assumed to contain less than 50-ppm PCBs
to reduce the concentration of PCBs in the common
container. If dielectric fluid from untested oil-
filled circuit breakers, reclosers, or cable is
collected in a common container with dielectric
fluid from other oil-filled electrical equipment,
the entire contents of the container must be
treated as PCBs at a concentration of at least 50
ppm.
• For purposes of complying with the marking and
disposal requirements, representative samples may
be taken from either the common containers or the
individual electrical equipment to determine PCB
concentration. Except, that if any PCBs at a
concentration of 500 ppm or greater have been
added to the container or equipment, then the
total contents must be considered as having a PCB
concentration of 500 ppm or greater for purposes
of complying with the disposal requirements at
761.60. Representative samples are either samples
taken in accordance with the American Society of
Testing and Materials (ASTM) method D-923, or
samples taken from a container that has been
thoroughly mixed in a manner such that any PCBs in
the container are uniformly distributed throughout
the liquid in the container.
XVI-1
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Ql: Can a facility utilize "screen tests" to prove that mineral
oil dielectric fluid electrical equipment is not
contaminated with PCBs?
Al: EPA currently finds gas chromatography (GC) to be the
minimally acceptable method for determining the
concentration and nature of PCBs in oils and uses GC for
verification purposes. EPA neither requires nor prohibits
use of any particular test method to determine PCB
concentration or total chloride ion detection methods.
Total organic chlorine or chloride analysis is not as
specific as gas chromatography for determination of PCB
content (i.e., it cannot distinguish between PCBs and other
chlorine containing compounds). Since PCB-Containing
Materials frequently contain organic chlorine from sources
other than PCBs (e.g., trichlorobenzenes), test data
obtained by total chlorine or chloride analysis are not as
reliable for PCB quantitation as gas chromatography.
Therefore, EPA will not accept total chlorine analysis data
as proof that a company has satisfied any of the testing
requirements, or achieved any of the concentration levels
found in the PCB regulations. There is no prohibition on
the use of total organic chlorine or chloride analysis as a
rough field screening device to determine whether further
testing is needed. However, the Agency finds gas
chromatography to be the minimally acceptable method for
ascertaining the level of PCBs in oils.
WASTE OIL
Owners or users of waste oil may use the following
procedures to determine the PCB concentration of waste oil:
• Waste oil from more than one source may be
collected in a common container, provided that no
other chemical substances or mixtures, such as
non-waste oils, are added to the container.
• For purposes of complying with the marking and
disposal requirements, representative samples may
be taken from either the common container or
individual containers to determine the PCB
concentration. Except, if any PCBs at a
concentration of 500 ppm or greater have been
added to the container, then the total container
contents must be considered as having a PCB
concentration of 500 ppm or greater for purposes
of complying with the disposal requirements at
761.60. Representative samples are either samples
taken in accordance with the American Society of
Testing and Materials (ASTM) method D-923, or
XVI-2
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samples taken from a container that has been
thoroughly mixed in a manner such that any PCBs in
the container are uniformly distributed throughout
the liquid in the container.
PCS SPILLS
See the chapter XIV on "PCB Spill Cleanup -Policy" for a
detailed discussion of proper sampling/testing methods for
PCB spills.
XVI-3
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CHAPTER XVII
IMPORT AND EXPORT
Closed Border Policy (page XVII-1)
Exemptions to Closed Border Policy (page XVII-1)
-------
- IMPORT AND EXPORT -
CLOSED BORDER POLICY
EPA has generally established a "closed border" policy which
went into effect May 1, 1980, pertaining to the importing
and exporting of PCBs and PCB Items. In the Federal
Register of May 31, 1979, EPA recognized that PCB contamina-
tion is a global problem, and that PCBs used outside the
United States can cause PCB contamination of this country
due to the extreme persistence of the substance and the ease
with which it is transported in the environment. Conse-
quently, the Agency concluded in 1979 that the distribution
in commerce of PCBs for export constitutes an unreasonable
risk to health and the environment in the United States.
However, certain activities involving the import and export
of PCBs have been specifically exempted from the regulatory
prohibitions on distribution in commerce (import and export)
of PCBs.
EXEMPTIONS TO CLOSED BORDER POLICY
These exemptions are:
• Persons who import or export products containing
PCBs generated as unintentional impurities in
"excluded manufacturing processes" as defined in
76"!.3, are exempt from the distribution in
commerce prohibitions provided that such persons
comply with the records and certification
requirements at 761.185, 761.187, and 761.193.
• Persons who import or export products containing
"recycled PCBs" as defined in 761.3, are exempt
from the distribution in commerce prohibitions
provided that such persons comply with the records
and certification requirements at 761.185,
761.187, and 761.193.
• Persons who import or export products containing
"Excluded PCB Products" as defined in 761.3 are
exempt from the distribution in commerce
prohibitions.
• Persons who import or export products that were
contaminated with PCBs because of a spill from, or
proximity to, a PCB Item 50 ppm or greater, and
which have been decontaminated in accordance with
applicable EPA spill cleanup policies, are exempt
from the distribution in commerce prohibitions.
XVII-1
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• PCBs at concentrations less than 50 ppm may be
imported or exported for purposes of disposal
(761.20(b)(2)).
• PCBs at any concentration may be exported for
reuse provided they were sold for purposes other
than resale prior to July 1, 1979 and are in a
totally enclosed manner.
Ql: Can PCB samples be imported for purposes of analysis?
Al: No, not without an exemption. Since TSCA defines import as
manufacture (TSCA section 3), and the manufacture of PCBs is
banned unless exempted by rule (TSCA section 6(e)), a person
may not import PCBs other than at less than 50 ppm for
purposes of disposal.
XVII-2
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CHAPTER XVIII
PCS TRANSFORMER FIRE-RELATED REQUIREMENTS
Installation of PCB Transformers (page XVIII-2)
Enhanced Electrical Protection (page XVIII-3)
Phaseout of Lower Secondary Voltage Network PCB
Transformers in Sidewalk Vaults (page XVIII-3)
Discovery of a PCB Transformer (page XVIII-3)
-------
- PCB TRANSFORMER FIRE-RELATED REQUIREMENTS -
In the August 25, 1982 "Electrical Equipment Use Rule," EPA
authorized the continued use of all nonrailroad transformers
containing or contaminated with PCBs for the remainder of
their useful lives. The only exceptions were PCB
Transformers (500 ppm or greater) whose use was prohibited
after October 1, 1985 if they posed an exposure risk to food
or feed. In making its August 1982 decision, EPA determined
that authorizing the use of transformers containing PCBs for
the remainder of their useful lives did not present an
unreasonable risk to public health or the environment. In
evaluating the risks posed by the continued use of
transformers containing PCBs, EPA considered the principal
route of release and exposure to PCBs to result from leaks
and spills from this equipment. However, since that time,
EPA has learned that fires involving transformers can also
be significantly responsible for the release of PCBs, and
that PCBs released from transformers in a fire situation can
be volatilized and converted into dioxins and dibenzofurans
which are many times more toxic than PCBs.
Originally, EPA believed that PCB Transformer fires were
very rare and isolated events. Thus, EPA did not directly
consider the public health and environmental risk posed by
fire-related events until after the 1982 "Electrical
Equipment Use Rule" when additional information came to
EPA's attention indicating that PCB Transformer fires may
occur more frequently than previously expected, and that
transformer fire-related hazards are not restricted solely
to transformers located inside buildings.
In an attempt to reduce fire-related risks posed by the use
of PCB Transformers, EPA issued a final rule published in
the Federal Register of July 17, 1985 (50 PR 29170) which is
referred to as the "PCB Transformer Fires Rule." In
addition to the existing use and servicing regulations for
PCB Transformers, this 1985 rule further regulated the use
of PCB Transformers. Among other provisions, the rule
specifically:
• prohibited the use of higher secondary voltage
(secondary voltages equal to or greater than 480
volts including 480/277 volt systems) network PCB
Transformers, located in or near a commercial
building, after October 1, 1990;
• prohibited the further installation of PCB
Transformers in or near a commercial building;
XVIII-1
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• required, as of October 1, 1990, the enhanced
electrical protection of all radial and lower
secondary voltage (secondary voltages below 480
volts) network PCB Transformers, located in or
near a commercial building;
• required the registration of all PCB Transformers
with the Fire Department having primary
jurisdiction by December 1, 1985;
• required the registration of any PCB Transformers
located within 30 meters (roughly 100 feet) of a
commercial building to be registered with the
building owner;
• required the marking of the means of access (vault
door, fence, hallway, etc.) to a PCB Transformer
with the mark ML (PCB label);
• required the removal of all combustible materials
stored within 5 meters (roughly 15 feet) of a PCB
Transformer; and
• required immediate notification of the National
Response Center (NRC) in the event of a PCB
Transformer fire-related incident.
Shortly after the promulgation of the 1985 "PCB Transformer
Fires Rule," Mississippi Power Company filed a petition for
review of the rule. After reviewing new information
submitted by Mississippi Power and others, and considering
their requests for clarification and amendments to the "PCB
Transformer Fires Rule," EPA determined that the issues
raised warranted further Agency consideration and
subsequently, in the Federal Register of December 31, 1986
(51 FR 47241), published a document responding to issues
that needed clarification and in the Federal Register of
July 19, 1988, EPA promulgated final amendments to the
original 1985 "PCB Transformer Fires Rule." These
amendments included:
• INSTALLATION OF PCB TRANSFORMERS:
The "PCB Transformer Fires Rule" banned the
installation of PCB Transformers in or near
commercial buildings after October 1, 1985. EPA
has amended the 1985 rule to allow the
installation of a PCB Transformer under "emergency
situations" as described in 761.30(a)(1)(iii)(B);
and, installation for purposes of reclassification
as described in 761.30(a) (1) (iii) (C) .
XVIII-2
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ENHANCED ELECTRICAL PROTECTION:
The "PCB Transformer Fires Rule" required the
installation of enhanced electrical protection on
all radial and lower secondary voltage network PCB
Transformers, located in or near a commercial
building, by October 1, 1990. On July 19, 1988
(53 FR 27322) EPA amended the 1985 rule by
allowing the use of nonsidewalk vault, lower
secondary voltage network PCB Transformers in or
near commercial buildings without enhanced
electrical protection until October 1, 1993,
provided EPA is notified as of October 1, 1990.
These PCB Transformers must then be removed by
October 1, 1993.
On November 26, 1990 (55 FR 49043) EPA further
amended the PCB Transformer Fires rule by allowing
for partial deenergization, i.e., deenergizing
only the faulted phase(s), of certain low voltage
radial transformers. In some circumstances this
may be equivalent to total deenergization of such
transformers in the event of a high current fault.
See "History of the PCB Regulations" earlier in
this manual for greater discussion on this issue.
PHASEOUT OF LOWER SECONDARY VOLTAGE NETWORK PCB
TRANSFORMERS IN SIDEWALK VAULTS:
The 1985 fires rule prohibited the use of all
network PCB Transformers with higher secondary
voltages, in or near a commercial building, after
October 1, 1990. EPA added to this original
phaseout requirement in the 1988 final amendments
by also requiring that all lower secondary voltage
network PCB Transformers, located in sidewalk
vaults, be removed from service by October 1,
1993.
DISCOVERY OF A PCB TRANSFORMER:
In the event a mineral oil transformer, assumed to
contain less than 500-ppm PCBs as provided in
761.3, is tested and found to be contaminated at
500 ppm or greater, it will be subject to all of
the requirements for "PCB Transformers." In
addition, efforts must be initiated immediately to
bring the transformer into compliance. The
following is a partial listing of compliance
requirements for newly discovered PCB
Transformers:
XVIII-3
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(1) Mark/label the PCB Transformer within 7 days
after discovery.
(2) Mark/label the means of access to the PCB
Transformer within 7 days after discovery.
(3) Register the PCB Transformer with fire
response personnel and with the commercial
building owner (if within 30 meters), within
30 days of discovery.
NOTE: Responsible parties should refer to 40 CFR
761.30 for detailed requirements.
Ql: Are single family residential homes considered "commercial
buildings"?
Al: Commercial buildings are described in the regulations as
including residential properties. However, in promulgating
the 1985 fires rule, EPA was concerned with residential
properties where groups of people live and reside (e.g.,
apartments, hotels, dormitories). Consequently, EPA is
clarifying that the term "residential properties" as used in
the definition of "commercial building" does not include
single family residential homes.
Q2: Is it allowable to send PCB Transformer registration letters
to building managers instead of the owners if there are
multiple owners?
A2: Yes. Registration of PCB Transformers with the property
manager is acceptable when there are multiple owners (e.g.,
condominiums).
Q3: Could you please clarify the term "combustible materials"
and their prohibited storage within "5 meters" of a PCB
Transformer as referenced in the PCB Transformer Fires Rule?
A3: Although EPA did not specifically define "combustible
materials," examples were set forth in the regulation to
help in understanding what EPA meant by "combustible
material." (See 50 FR 29200.) These combustible materials
include, but are not limited to, paints, solvents, plastics,
paper, and sawn wood. EPA's intent in promulgating this
rule was to prevent the storage of materials near a PCB
Transformer that would start or feed a fire.
The regulation, at 50 FR 29200, specifically requires that
combustible material not be stored within a PCB Transformer
enclosure, or within 5 meters of a transformer enclosure, or
if unenclosed (unpartitioned), within 5 meters of a PCB
Transformer. Wood walls, platforms, and other integral
XVIII-4
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building structures, even if considered combustible, do not
constitute "stored" materials. Any item "in use" cannot be
considered a stored item within the purview of the rule.
EPA's intent in promulgating this requirement was to reduce
the risk of fire by mandating that combustible materials
stored near transformers be moved to other locations. Wood
walls, platforms, and other integral building structures, if
they are not "stored" items, do not fall within the purview
of the stored combustible rule.
The 5-meter distance requirement does not apply where
combustible materials are in a storage room adjacent to a
PCB Transformer vault if the common wall between the storage
room and vault is constructed in a manner which would
effectively reduce the risk of the stored combustible
starting or feeding a fire. The purpose of the "5-meter
requirement" is to provide an adequate distance between a
PCB Transformer and stored combustible materials, thus
reducing the potential for these materials to ignite in the
event of an electrical fault or transformer fire, or prevent
a fire external to the transformer from involving the
transformer. EPA recognizes that equivalent levels of
protection can be provided by other means including
separating a PCB Transformer from stored combustibles by a
barrier or enclosure that would contain a fire until it
could be extinguished or until the transformer could be
deenergized. Six-inch-thick reinforced concrete is a
typical 3-hour fire-resistant construction, as specified in
ASTM Standard E119-75; Fire Tests of Building Construction
and Materials, NFPA 251-1972; and Methods of Fire Tests of
Building Construction and Materials, ANSI A2.1-1972. For
PCB Transformer fires, EPA believes that a 2- to 3-hour
fire-rated wall or enclosure constructed of noncombustible
materials, such as concrete, separating a PCB Transformer
from stored combustibles would present an adequate barrier
to fire. If the wall can accomplish this purpose, the 5-
meter rule does not apply.
The 5-meter distance requirement, although not specified in
the regulation, applies not only to horizontal distances,
but to vertical distances as well, unless the vertical
distance is separated by a continuous, permanent ceiling or
floor. EPA did not intend that a 5-meter distance be
measured through separate and distinct rooms located above
or below the transformer.
XVIII-5
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CHAPTER XIX
PCS NOTIFICATION AND MANIFESTING RULE
Background (page XIX-1)
Tracking System for PCB Waste (page XIX-2)
Notification Requirement (page XIX-2)
Manifesting of PCB Waste (page XIX-4)
Records and Report (page XIX-7)
Commercial Storage Approvals (page XIX-8)
-------
-PCS NOTIFICATION AND MANIFESTING RULE-
The general provisions of the PCB Notification and
Manifesting Rule are outlined in this chapter as well as a
number of common questions and answers that have been raised
since the effective date of the rule (February 5, 1990).
Readers should refer to the Federal Register of December 21,
1989 (54 FR 52716) for the specific provisions of the final
rule. In addition, readers should be aware that there are
many State programs which impose overlapping transportation,
storage, or disposal requirements on the Federally regulated
PCB disposal community. Compliance with Federal rules does
not provide relief from compliance with State requirements.
Conversely, compliance with State requirements does not
provide relief from compliance with Federal rules
First, the rule adds to the TSCA disposal regulations a PCB
waste tracking system modeled after the "cradle-to-grave"
tracking system for hazardous wastes under RCRA. At the
heart of the tracking system are the requirements that PCB
waste handlers notify EPA of their PCB waste activities, and
use the RCRA Uniform Manifest (Form 8700-22) in connection
with their shipments of regulated PCB waste.
Second, the Rule requires all persons who commercially store
PCB wastes to obtain an approval from their EPA Regional
Administrators, or from the Director, Chemical Management
Division (CMD)/Office of Pollution Prevention and Toxics
(OPPT) (when they seek approval for commercial storage areas
ancillary to disposal facilities that were approved by
Headquarters). The approval process will enable EPA to
evaluate the qualifications of applicants to engage in the
business of PCB waste storage, and more particularly, to
impose standards relating to closure plans, financial
responsibility, and maximum storage capacity.
BACKGROUND
Congressional oversight committees have probed into several
incidents which the committees believed demonstrated a need
for additional controls to ensure that PCB waste is in fact
properly disposed of at permitted facilities. In
particular, the House Subcommittee on Environment, Energy,
and Natural Resources (Rep. Synar, Chairman) held hearings
in August 1986, and again in April 1987, on PCB disposal
incidents. The testimony elicited at these hearings
highlighted the fact that the national PCB disposal program
lacked a means of tracking PCB waste from the point of
generation to the point of disposal at approved facilities.
These proceedings also highlighted another shortcoming which
XIX-1
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the Subcommittee found to be especially troubling--the lack
of any Agency oversight of the qualifications and activities
of certain PCB waste brokers and others who act as
intermediate storers of PCB waste generated by others. The
Agency was criticized for not having a means of identifying
definitively the intermediate handlers of PCB wastes, and
for not having a means of evaluating the qualifications and
financial responsibility of those who engage in these
commercial activities.
TOPICS ADDRESSED BY THIS RULE
TRACKING SYSTEM FOR PCB WASTE
The rule adopts a tracking system for PCB waste modeled
after the "cradle-to-grave" tracking system for RCRA
hazardous wastes. Specifically, the tracking system
consists of the following components:
• A requirement that certain PCB waste handlers
notify EPA of their PCB waste activities, and
receive from the Agency unique identification
numbers;
• A requirement that generators of regulated PCB
wastes initiate shipping documents (manifests),
which physically track the waste from the point
of generation to the site of storage and/or
disposal; and
• Recordkeeping and reporting requirements that
complete the tracking system and facilitate
enforcement of the PCB disposal regulations.
NOTIFICATION REQUIREMENT; (40 CFR 761.202 and 205)
The notification requirement imposed on PCB waste handlers
is similar to that which EPA requires under the Resource
Conservation and Recovery Act (RCRA) section 3010 for
notification of hazardous waste activities. It is illegal
to engage in PCB waste handling activities unless one has
notified EPA in advance, and received a unique
identification number. The persons who are required to
notify EPA consist of generators, transporters, commercial
storers, and disposers of PCB wastes. To maintain, as far
as possible, consistency with existing RCRA requirements,
the "Notification of PCB Activity" form is similar to the
RCRA notification form. Importantly, PCB waste handlers who
have previously notified and received identification numbers
XIX-2
-------
under RCRA do not need to obtain a new identification number
from EPA under this rule, but they still must notify EPA in
order to confirm the existing identification number.
Identification numbers issued under this rule will be based
upon the same 12-digit numbering system (DUNS) which RCRA
uses to designate hazardous waste entities.
The rule differs slightly from RCRA in that it requires only
a limited class of PCB waste generators to notify EPA and
obtain unique identification numbers. The generator
notifications are limited to the generator-owned or operated
storage facilities that are subject to the TSCA storage
facility standards (761.65(b) and/or (c)(7)) for PCB waste.
The purpose in designating this class of facilities is to
focus on those larger volume users, owners, and processors
who store PCB waste which they generate and may be expected
to utilize PCB disposal services on a fairly regular and/or
large scale basis. For the generators exempted from
notification, this rule specifies a generic identification
number (40 CFR PART 761) for use on their manifests.
This rule treats notification by transporters and commercial
storers and disposers of PCB waste like they would be
treated under RCRA. All such facilities are required to
notify and receive from EPA unique identification numbers as
a condition of doing business.
Ql: Are transfer facilities required to notify EPA of their PCB
waste handling activities?
Al: Transfer facilities may hold PCB waste for up to 10
consecutive days to provide trains, trucks and other
transport vehicles the opportunity to unload or transfer the
PCB waste to the next connecting transport vehicle. If the
waste is held for more than 10 consecutive days, then the
facility becomes a commercial storer subject to the
notification requirements (§761.205), the storage area
requirements (§761.65(b)), and the requirements associated
with obtaining commercial storage approval (§761.65(d)-(h)).
Q2: Does the EPA have to be notified when fluorescent light
ballasts are removed from a building?
A2: No. If the business does not conduct any other PCB handling
activities, they need not notify EPA under the PCB
regulations, but you must notify the NRC pursuant to CERCLA
if more than 1 Ib. of PCBs is involved.
Q3: If we have an existing RCRA EPA identification number, do we
need a different TSCA identification number?
XIX-3
-------
A3: No. You may use your RCRA number but still must notify EPA
under TSCA in order to confirm that number. EPA must
confirm that number before you may commence any PCB waste
handling activity.
MANIFESTING OF PCB WASTE; (40 CFR 761.207-211. 215 and 218)
The centerpiece of the tracking system for PCB waste is the
requirement that all who handle regulated PCB wastes use
shipping documents known as manifests to track the movement
of PCB waste from the point of generation to the point of
delivery to off-site storage or disposal facilities. The
generator bears the primary burden of preparing the
manifest, which at all times physically accompanies the
waste to its destination.
Most importantly, the manifest establishes a paper trail of
accountability that documents each waste handler's
completion of his responsibilities with regard to the waste.
Each person (generator, transporter, etc.) who handles the
waste must obtain the signature of the next person in the
chain of distribution, and he must keep a copy signed by the
"next-in-line" handler in his files as a record of his
involvement with the waste shipment. Finally, an additional
copy signed by the storage or disposal facility designated
on the manifest is returned to the generator who initiated
the shipment, signifying the successful completion of the
waste delivery transaction. In effect, the manifest serves
notice of the types and quantities of waste being shipped;
it creates a paper trail documenting that the waste was
properly delivered; and it is a source of information for
other records and reports that summarize a facility's
overall waste activities.
EPA is requiring that the same manifest document used in
connection with RCRA hazardous waste--the Uniform
Manifest--be the shipping document for tracking PCB waste.
The existing Uniform Manifest is designed to elicit basic
information identifying the persons handling the waste, as
well as the nature and quantity of the waste. This format
lends itself well to the tracking of PCB waste.
The rule requires that manifests be used in connection with
the off-site transport of PCB wastes at the 50 ppm or
greater level (see 761.207 (j) for a discussion of
manifesting and anti-dilution). The 50 ppm threshold for
manifesting matches the existing cut-off for the disposal of
PCBs under the TSCA PCB regulations. The 50 ppm threshold
also corresponds to the level at which a number of States
require manifests under their hazardous waste programs, and
it corresponds to the level at which disposers are currently
XIX-4
-------
requiring manifests as a means of limiting their
liabilities.
Q4: When states require the use of a manifest for shipping PCB
waste, which form should I use?
A4: If both the consignment state and the generator state
require the use of a specific manifest for use in their
state, the PCB rules require that the consignment state's
manifest must be used. EPA suggests that both manifests be
prepared, but only the consignment state's manifest be
retained in the TSCA annual PCB records, when any state is
unwilling to use a form of manifest used in another state.
Q5: Do I need to manifest drained PCB-Contaminated Transformers?
A5: No. Since drained PCB-Contaminated Transformers are not
subject to the disposal requirements of Subpart D, 40 CFR
Part 761, they are not subject to the manifesting
requirements.
Q6: If a generator owns two storage facilities which have
different EPA identification numbers and ships PCB waste
from one facility to another for purposes of consolidation,
must the waste be manifested?
A6: No. The PCB waste has not left the generator's control and,
therefore, need not be manifested at this time.
Q7: I own a transformer service shop. Am I considered the
generator of the residual oils that are collected during
repair and servicing operations?
A7: Yes. You are the generator of this waste because you have
physical control of the equipment when the oil was removed.
If the residuals were generated on-site at the owner's
facility, the owner would be the generator of this waste.
Q8: A transformer is shipped off-site for purposes of inspection
and repair. It is determined by the repair shop that the
cost of repair would exceed the cost of replacing the unit.
The repair shop contacts the owner of the unit for
instructions on how to proceed and is instructed by the
owner to dispose of the unit. Who is the generator? If it
is the repair shop, how would the transformer show up on the
annual records of the original owner and how would the
original owner ensure receipt of a Certificate of Disposal
(CD) ?
A8: The repair shop is the generator of the waste (i.e.,
transformer) because it "has physical control over the PCBs
when a decision is made that the use of the PCBs has been
XIX-5
-------
terminated and is subject to the disposal requirements," (40
CFR 761.3 -- definition of "Generator of PCB Waste"). The
day that the original owner made the decision to dispose of
rather than repair the unit is the day the unit is
considered to be "removed from service for disposal." This
information is required to be recorded in the repair shop's
annual document log as per 40 CFR 761.180(a)(2)(ii)(B). The
original owner would not receive a CD because he was not the
generator of the waste, but he could make arrangements with
the repair shop to receive a copy of the CD when the repair
shop gets its copy from the disposer. Likewise, the repair
shop could not "return" the waste oil to the original owner
unless that owner was a commercial storer or disposer who
had notified the Agency of such activities.
Q9: In which of the following situations is a generator required
to make a confirmation telephone call to the designated
facility to confirm receipt of PCB waste?
a. The designated facility provides transportation
services with vehicles owned and operated by them.
b. The designated facility provides transportation through
a wholly-owned subsidiary.
c. Through a contract with the generator, the designated
facility is responsible for the transportation and
chooses an independent company.
A9: The only time a confirmation telephone call need be made is
when an "independent transporter" is used. Section
761.208(a)(4). Therefore, in situations "a" and "b" a
confirmation call would not be needed and in situation "c"
one would.
Q10: When completing the manifest form, can the weight in
kilograms be entered in the space provided in item 14?
A10: Yes. The instructions for filling out the Uniform Hazardous
Waste Manifest allow for the use of various units of
measure; kilograms is one of those units. DOT currently has
no rule that limits the unit of measure to only gallons or
pounds.
Qll: Is it mandatory to use the waste codes "PCB 1" and "PCB 2"
on the manifest?
All: No. The use of these waste codes is intended to facilitate
data exchange among cooperating states and is, therefore,
optional.
XIX-6
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Q12: (a) Can estimates for weight be used when facilities do not
have scales to weigh drums? (b) If so, is the difference of
more than 10 percent in weight still significant if the
generator and the disposal firm have reached an agreement
that the disposal firm's weighing will be the accepted
figure?
A12: (a) Estimates may be used. The PCB regulations take into
account that it is not always feasible to weigh the
material. When it is not possible to weigh the material, it
is acceptable either to weigh a 1 gallon sample or estimate
the weight using 12 pounds per gallon of askarel and 8
pounds per gallon for contaminated mineral oil. You must
indicate on the manifest whether the weight is actual or
estimated. (b) There would be no need to submit a
discrepancy report if a weight difference of greater than 10
percent can be reconciled, i.e., it is mutually agreed to
use the disposal firm's scales.
Q13: Who is the generator in the following cases of shipped
laboratory samples?
a. The laboratory ships the unused portion back to the
person from whom it was originally received.
b. The person submitting the sample for analysis
subsequently ships that sample for commercial storage
or disposal.
c. The sample is manifested by the lab to a disposal
facility.
A13: Laboratory samples are implicitly authorized for use, as
opposed to being under the disposal regulations, and are
considered to remain in use until their use for analysis or
for an enforcement case has ended. Therefore, in case "a"
no one is the generator since no waste is being generated.
In case "b" the sample is now subject to the disposal
regulations since it is being shipped to a commercial storer
or disposer. In this case then, the person shipping the
sample for storage or disposal is the generator. In case
"c" the sample is obviously no longer in use since the lab
is manifesting it to the disposal facility; the lab is the
generator.
RECORDS AND REPORTS; (40 CFR 761.180. 209. 210. 211. 215.
and 218)
The rule adopts additional recordkeeping and reporting
requirements to complete the tracking system for PCB wastes.
The rule requires that the manifests themselves be retained
as records by waste handlers (761.209), and it requires
XIX-7
-------
reporting to EPA in the event of irregularities in the
transport of regulated wastes (761.210). In addition, there
are reporting requirements for: unmanifested waste
(761.211), exception reporting -- when the one-year storage
for disposal requirement is breached (761.215), or a
Certificate of Disposal is not received in a timely manner
by the generator (761.218). These reports depend largely on
information derived from particular manifests.
The rule adds several amendments to the existing PCB
recordkeeping provisions that concern the annual document
requirements for the users, storers, and disposers of PCBs.
The most significant of these amendments is the requirement
that each disposer and commercial storer of PCB waste submit
by July 15 of each year an Annual Report, which is a summary
of the previous calendar year's PCB activity at the
facility. Section 761.180(b)(3). The report must be
submitted to the appropriate EPA Regional Administrator.
Chapter XV discusses the new recordkeeping provisions of the
Notification and Manifesting Rule in greater detail.
Q14: As the ultimate disposer of manifested PCB waste, do I send
the Certificate of Disposal to the generator or to the
commercial storer from which I received the waste directly?
A14: The Certificate of Disposal must be sent to the generator
indicated on the manifest. In the event the storer
generates a new manifest because he consolidates a number of
PCB waste shipments prior to sending the waste to the
disposal facility, the original generator may make
arrangements with the commercial storer to receive a copy of
the Certificate of Disposal.
COMMERCIAL STORAGE APPROVALS; (40 CFR 761.65(d)-M))
The rule adopts an approval process for commercial PCB waste
storers. The term "commercial storer" is defined broadly to
mean any facility that stores PCB wastes generated by
others, or that brokers waste generated during electrical
equipment servicing.
The rule allowed existing commercial storers a 180-day
period from the effective date (February 5, 1990), within
which they must have applied for approvals from their EPA
Regional Administrators (or from the Director, CMD/OPPT for
approval of commercial storage areas at disposal facilities
approved by Headquarters). If a facility submitted a
complete application (including but not limited to: identity
of principals and key employees, a list of State and/or
Federal environmental violations occurring over the past 5
years, description of the design and capacity of the
XIX-8
-------
facility, a closure plan, a demonstration of financial
assurance, and a closure cost estimate) by August 4, 1990,
the applicant was granted interim approval to operate until
the facility's application was either approved or denied at
which time interim authorization was terminated.
The issuance of a final storage approval is contingent upon
the company satisfying the seven criteria in 40 CFR
761.65(d)(2). Among other things, the Regional
Administrator must be satisfied that the applicant is
qualified to engage in the commercial storage business.
Also, applicants are required to submit acceptable closure
plans and demonstrate their financial responsibility for
closure. The requirement to demonstrate one's financial
responsibility can be satisfied by using one or more of the
financial assurance mechanisms described in current RCRA
regulations for permitted hazardous waste facilities (40 CFR
264, Subpart H). Applicants will also be required to
certify their compliance with the TSCA storage facility
standards, and to estimate the maximum quantities of PCB
waste that will be handled at the facility.
The final rule contains a small quantity exemption from the
definition of "commercial storer" for facilities that store
less than 500 gallons of PCBs at any time. Such facilities
need not seek approvals to operate under 761.65(b). At the
time of this printing, the Agency is considering proposing a
similar small quantity exemption for solid PCB waste.
Q15: Does the small quantity exemption for applying for a
commercial storage approval apply only to less than 500
gallons of liquid PCB waste?
A15: In the Federal Register of June 27, 1990, EPA clarified this
exemption by stating that one need not apply for a
commercial storage approval if the facility's storage of PCB
waste at no time exceeds 500 liquid gallons of PCBs.
Pending publication of a final amendment in the Federal
Register. EPA will not bring enforcement actions against
facilities storing less than 70 cubic feet of solid PCB
waste, provided such facilities notify EPA of their waste
activities and comply with all other TSCA and PCB
regulations.
Q16: I operate the central PCB storage facility which is owned by
and accepts waste from members of our public power
association. Am I considered a commercial storer and
therefore required to submit a commercial storage
application?
XIX-9
-------
A16: No. Storage of one company's PCB waste by a "related
company" is not commercial storage. Therefore, storage
between "related companies" is exempt from commercial storer
status. Storage of any waste generated by a non-affiliated
organization would change this status to that of a
commercial storer. "Related companies" include a parent
company and its subsidiaries, sibling companies owned by the
same parent company, companies owned by a common holding
company and members of an electric cooperative. The test is
whether the "related" companies have a financial or
managerial relationship that would provide for a mutual role
in the financial assurance for the storage area. By this
definition, companies are not related if they merely belong
to the same trade association.
Q17: Would all Department of Defense (DOD) facilities be
considered "related" under this rule?
A17: Yes. DOD facilities are considered related so there will be
no commercial storage involved when one DOD facility stores
PCB waste that is generated by another DOD facility.
However, storage of PCBs at a DOD facility generated by
another Federal, State, or local government
departments/agencies, or other (i.e., private) facilities
will constitute commercial storage.
Q18: Are independent laboratories required to get commercial
storage approval?
A18: No. As long as they are independent (i.e., separate from
any firm whose activities involve PCB waste handling) and
store their waste in an area that complies with 40 CFR
761.65(b)(i)-(iv), such facilities are not required to get
commercial storage approvals.
Q19: A power marketing agency has contracts with its customers to
operate and maintain equipment that the customer owns. The
agency may operate a customer's equipment located either on
the customer's property or the agency's property. Is the
power marketing agency a commercial storer if it stores PCB
waste owned by its customers?
A19: Yes. The power marketing agency is providing a service for
a fee. That is not the same interwoven managerial or
financial interest that exists between electrical
cooperatives, sibling corporations, or other relationships
where there would be a mutual role in financial assurance
for the storage area.
XIX-10
-------
APPENDIX I
CODE OF FEDERAL REGULATIONS
40 CFR PART 761
(Revised as of July 1, 1993)
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APPENDIX II
PCB DISPOSAL COMPANIES
COMMERCIALLY PERMITTED
-------
PCB DISPOSAL COMPANIES
COMMERCIALLY PERMITTED
MAR -41994
*Permitted to operate in all ten EPA Regions
COMPANY
INCINERATORS
Aptus, Inc.
Chemical Waste
Management
Rollins
WESTON
ADDRESS
P.O. Box 1328
Coffeyville, KS 67337
P.O. 27448
Salt Lake City, UT
1160 N. Aptus Road
Aragonite, UT
P.O. Box 2563
Port Arthur, TX 77643
P.O. Box 609
Deer Park, TX 77536
One Weston Way
West Chester, PA 19380
PHONE NO.
312-251 6380
801-521-9009
409-736-2821
713-930-2300
215-692-3030 *
ALTERNATE THERMAL TECHNOLOGIES
General Electric
100 Woodlawn Avenue
Pittsfield, MA 01201
413-494-2700
CHEMICAL DECHLORINATION
Chemical Waste
Management
Exceltech, Inc.
(ENSCO Subsidiary)
Aptus, Inc.
PPM, Inc.
(USPCI Subsidiary)
ENSR Operations
(formerly Sunohio)
1550 Balmer Road
Model City, NY 14107
41638 Christy Street
Fremont, CA 94538
P.O. Box 1328
1875 Forge Street
Tucker, GA 30084
1700 Gateway Blvd. S.E.
Canton, OH 44707
Coffeyville, KS 67337
716-754-8231
415-659-0404
316-251-6380
404-934-0902 *
216-452-0837 *
-------
-2-
COMPANY ADDRESS
CHEMICAL DECHLORINATION (Continued)
Transformer
Consultants, Div. of
S.D. Myers, Inc.
Trinity Chemical Co.
Inc.
180 South Avenue
Tallmadge, OH 44278
6405 Metcalf, Cloverleaf 3
Suite 313
Shawnee Mission, KS 66202
PHONE NO.
800-444-9580 *
913-831-2290
PHYSICAL SEPARATION
CECOS International
Process Center
Aptus, Inc.
Unison Transformer
Services, Inc.
Quadrex Environmental
Company
General Electric
S. D. Myers, Inc.
PIPELINE REMOVAL
Alguonguin Gas
Transmission Company
CNG Transmission
Corporation
Columbia Gas
Transmission Corp.
Columbia Gulf
Transmission Co.
Natural Gas Pipeline
Company of America
Northern Natural Gas
Company
4879 Spring Grove Ave.
Cincinnati, OH 45232
P.O. Box 1328
Coffeyville, KS 67337
5801 Riverport Road
Henderson, KY 43420
1940 N.W. 67th Place
Gainesville, PL 32606
One River Road
Schenectady, NY 12345
180 South Avenue
Tallmadge, Ohio 44278
1284 Soldiers Field Rd.
Boston, MA 02135
445 West Main Street
Clarksburg, WV 26302
P.O. Box 1273
Charleston, WV 25325-1273
P.O. Box 1273
Charleston, WV 25325-1273
701 East 22nd Street
Lombard, Illinois 60148
P.O. Box 2511
Omaha, NB 68103-
513-681-5738
316-251-6380
502-827-0541
904-373-6066 *
518-385-2426 *
800-444-9580
617-254-4050 *
304 623-8446
304-359-2727 *
304-359-2727 *
708 691-3808
515-226-2011 *
-------
OMPANY
PIPELINE REMOVAL (Continued)
Tennessee Gas Pipeline
Company (Tenneco)
Texas Eastern Gas
Pipeline Company
Texas Gas Transmission
Corporation
Transwestern Pipeline
Corporation
-3-
ADDRESS
P.O. Box 2511
Houston,TX 77252-2511
P.O. Box 2521
Houston, TX 77252-2521
3800 Frederica Street
Owensboro, KY 42302
3800 Frederica Street
Owensboro, KY 42302
PHONE NO.
713-757-5687 *
713-759-5472 *
502-926-8686 *
713-853-7237 *
PIPELINE AND COMPRESSOR
SYSTEMS DECONTAMINATION
Burlington Environmental
Inc.
LQuadrex Environmental
Company
Vector Group, Inc.
2203 Airport Way South
Suite 400
Seattle, WA 98134
1940 N.W. 67th Place
Gainesville, FL 32606
1118 Ferris Road
Cincinnati, OH 45102
206-223-0500 *
904-373-6066 *
513-752-8988 *
PCB TRANSFORMER DECOMMISSIONING
(Disassembly/Smelting)
Aptus, Inc.
Transformer Consultants
Div of S.D. Myers, Inc
Unison
P.O. Box 1328
Coffeyville, KS 67337
180 South Avenue
Tallmadge, OH 44278
1302 West 38th Street
Ashtabula, OH 44004
3126 Brinkerhoff Road
Kansas City, KS 66115
316-251-6380
800-444-9580
216-992-8665
913-321-3155
-------
COMPANY
CHEMICAL WASTE LANDFILLS
Chemical Waste
Management
Chem-Security Systems
Incorporated
Envirosafe Services
Inc. of Idaho
CWM Chemical Services
Control, Inc.
U.S. Ecology, Inc.
U.S. Pollution
Control, Inc.
BIOLOGICAL
Detox Industries, Inc,
-4-
ADDRESS
Alabama Inc. Box 55
Emelle, AL 35459
Box 471
Kettleman City, CA 93239
Star Route, Box 9
Arlington, OR 98712
P.O. Box 16217
Boise, ID 83715-6217
1550 Balmer Road
Model City, NY 14107
Box 578
Beatty, NV 89003
Grayback Mountain
8960N Hwy 40
Lake Point, UT 84074
12919 Dairy Ashford
Sugar Land, TX 77478
PHONE NO.
205-652-9721
209-386-9711
503-454-2643
800-274-1516
716-754-8231
702-553-2203
801-595-3900
713-240-0892
------- |