Document qkJYj30g8xy3od178vQxdRxxM
X. SCOPS
This standard establishes guidelines for the safe transport, use, maintenance, and dis posal of askarel and askarel-soaked material used in capacitors and transformers*
2* GENERAL INFORMATION
2*1 General. The term "askarel" generally describes a broad class of nonflammable synthetic chlorinated hydrocarbon.insulat ing- liquids widely used in capacitors, transformers, reactors, and accessory equipment operated at power frequencies*
Askarels consisting of or containing polychlorinated biphenyls (PCBs ) have been used in many applications since the early 1930's, but only recently was it dis covered that PCBs are widely dispersed in the environment. Systematic investigations of the biological effects of PCBs have been undertaken within the past few years to establish the effects of specific for mulations on specific species. Studies have shown that PCBs are an environmental contaminant. Significant steps have been taken by U.S. industry to limit further re leases of PCBs to the environment.
PCBs have been used in three broad types of applications as follows!
(1) "Open-ended" applications! for example, in paints, speciality inks, paper coatings, plastics, etc*
(2) "Nominally closed" applications; For example, as the working fluid in hydraulic and heat transfer sys tems.
(3) "Closed electrical system" applications, specifically as the insulating fluid in certain kinds of transformers and capa citors.
Effective January 15, 1972, the Monsanto Company, sole domestic producer of PCBs discontinued supplying PCBs to all except manufacturers of electrical transformers and capacitors.
Evaluations of the benefits, risks, and alternatives involved in the continued use of PCBs in closed electrical systems are summar ized in 2.2 through 2.4. 2.2 Benefits. Askaral-filled transformers are used where fire-resistant properties are important. Askarel-filled power and indus trial capacitors are significantly smaller, more reliable, more durable, and safer than oil-filled capacitors. As a result, askarels have supplanted mineral oils in more than 90% of the power and industrial capacitors made today. Over the past few decades most of the equipment that incorporates such capacitors has been designed to take particular advantage of the si2e, safety, and reliability benefits of askarel capacitors (for example, many types are today less than 14% of the size of equiv alent oil capacitors and have a life expectancy of 10 to more than 20 years}
Various federal, state, and local codes dictate the present use of askare1-containing equipment in or adjacent to public, commercial, and industrial buildings, which locations pre sent the greatest potential danger to life and , property.
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2*3 Risks. Xn the United States, medical re cords since the early 1930's show that the only adverse health effects experienced by U.S. workers exposed to askarels, either during the manufacture of these liquids or of electrical equipment containing these liquids, have been limited to occasional cases of nonchronic chloracne or other tem porary skin lesions or irritations*
Askarel-filled transformers and capac itors are delivered to customers as sealed units from which there is no escape of
changes that would be required to compensate for the fire resistance of the askarel-filled units. For certain applications and locations, dry-type transformers may replace askarelfilled transformers.
For new installations, although many of the foregoing limitations would still apply, building and installation design provisions could be made to accommodate the use of oilfilled, open dry-type or sealed dry-type trans formers , provided that necessary technical, code, physical size, and cost considerations
askarel under normal operation. Although certain types of equipment failures can re sult in loss of some askarel to the en
are properly evaluated. Several potential alternative transfimnarfluids
are under intensive-investigation .to determine ,
vironment, transformer- failures are limited
if they will have satisfactory electrical and
to approximately 0.02% of the units in ser vice per year. With respect to capacitors, such losses are limited to approximately
operating performance .characteristics. Such liquids must be acceptable environmentally, to the users, and from the fire risk standpoint.
0.04% of the units in service per year. In
*
addition, limited amounts of PCBs can get
The principal alternatives to askarels for
into the environment during the manufacture,
capacitors are either mineral oil or various
delivery, improper use, maintenance, repair,
types of synthetic fluids. The latter types
and disposal of transformers and capacitors.
are under intensive investigation by the in
Specific control measures have been in
dustry. Mineral oil And these newer fluids are
stituted by individual manufacturers, and
flammable. The use of mineral oil would return
users and are supplemented and strenghtened
capacitor technology to its pre-1932 level and
by national standards and procedures such as
would necessitate the redesign and replacement
this standard, which provides information to
of such widely used equipment as flourescent
prevent the inadvertent loss of KSs to the
light fixtures and racks for power and in
duction-heating capacitors, which could not environment at all stages from initial askarel
manufacture through ultimate disposal.
now accommodate the increased size of oil
2.4 Alternates. For technical and local and
capacitors while maintaining their present
ratings. For the newer types of synthetic national code reasons, it would be impossible .
to replace most askarel-filled transformers
fluids under investigation it must be determined ;
now in service with oil-filled units of
if they will yield satisfactory operating per
equivalent ratings without major construction
formance, are environmentally acceptable and
that liquid non-flammability is not required.
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Long before there were any environmental
stability, chemical stability, and degree of
concerns about PCB, there vaa a strong eco
flammability (both are recognized as highly
nomic incentive to find other lets expensive
resistant to burning. It is for these reasons
insulating liquids with the desirable charac
that Section 3 of this standard is intended
teristics of eakarels. Omitting economic con
to apply to capacitor-grade askarel.
siderations there are no technically equiv
3.2 Capacitor Grade Askarel. In September
alent fluids available today.
1971, a new grade of capacitor impregnant,
3. CAPACITOR GUIDELINES
Aroclor 101$, was made available to the in
3.1 General. The environmental effects of
dustry. This new grade contains s typical con
askarels are under in-depth study by govern
centration of 0.4t or less by weight of the
mental and other agencies. Askarels have been considered relatively harmless to humans based
higher boiling homologues of the chlorinated blphuyli. I Sm ASTHD3303 -74a)11 Aroclor 1016
on safe industrial usage, since the 1930's,
replaces Aroclor 1242, which previously wss
except for minor skin end eye irritation.
the major capacitor impregnant and contained
There have been no known instance of human in
around 7% of the higher-boiling homologues (the
juries when they were used under the normally
more persistent in nature). This 0.4% level of
accepted precautions and conditions of handling the higher-boiling homologues should be the
in both manufacturing and user applications.
maximum concentration acceptable in any capacitor
Askarels are being found in the environment
impregnant. Aroclor 1242 and 1254, previously
and in fish and bird life. The long-term
used es impregnanta, do not meat this requirement
genetic and ecological affects are not yet
and should no longer be used in capacitors de
completely understood. For these reasons, care signed and manufactured for alternating-current
should be taken to contain askarels and minimize applications.
their entry into the environment.
Aroclor 1016 has the same Underwriters' Labora
There are two general classes of askarels
tories, Inc. flammability rating as Aroclor
used by the electrical industry. The higher
1242.
chlorinated grades are the more persistent in
Commonly used solvents for clean-up purposes,
nature. Because of their higher degree of re
include benzenn; kerosene, acetone, trichloroe-
sistance to burning, they are used in trans
thane, trichloroethylene, and perchloroethylene.
formers where personnel safety is of paramount
Typical vapor pressure data for Aroolor 1016 are?
importance. Capacitor-grade askarel has a lower degree
of chlorination (composed primarily of the 3chlorine insomer# of biphenyl) and a higher de gree of biodegradability. Generally, it has
0C 25C 150C -
200 C -
0.001 0.006 4.3
29.0
mmHG mmHG mmHG
mmHG
At 25C and 760 mmHG pressure, saturated air
contains approximately 0.09 mg/1.
not bsan found in animal life. It is used in capacitors, where the extreme resistance to
NOTE* 1 mg/1 90.0 ppm (v/v) 1 ppm (v/v) 0.011 mg/1
burning required in transformers is of less im portance .
1 Numbers in brackets refer to corresponding
numbers in 7.1, References to the Text.
Although capacltor-and transformer-grade
askarels both contain members of the PCB family,
they do differ in composition, degree of bio
degradability, persistence in nature, electrical
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JiJ Employe* Safety and Plant Housekeeping. The procedures end limits given in 3.3 are intended to be minimum requirements to be met by manufacturers and users of capacitors containing askarel. Handling, control, and
' combination of gases are very unpleasant and irritating, thus giving ample warning of their presence. If exposure to high concentrations of askarel is necessary under emergency con ditions, an approved gas mask or self-con
disposal procedures are given, together with exposure limits and indicated antidotes and clean-up procedures. 3.3.1 General Safety Precautions. Although It is generally accepted that exposure to capacitor-grade askarel is not hazardous provided that simple precautions are taken, exposure should still be avoided. 3.3.1.1. Vapors. The odor of askarel is noticeable well below the maximum air con centrations considered safe. Up to 1.0 , milligram per cubic metre of air has been determined to be the maximum safe level of exposure during an 8-hour workday. (See re ference 19) The procedure for performing the necessary analyses.of vapors is referenced in
tained breathing apparatus should be worn.. Such exposure should be under the surveillance of other personnel capable of effecting rescue in case of an accident. If the odor of askarel is detected by the person wearing protective equipment, he should immediately go into fresh air. All gas masks, respirators, and replace ment parts should have U.S. Bureau of Mines approval and be maintained on a regular schedule in accordance with the manufacturer's recommendation. 3.3.1.2 Liquid. In contrast to the situation in which mineral Insulating oils are handled, there is virtually no fire hazard in handling askarel. A limited solvent action (similar to that for paint thinner) on the fats and oils of the skin with prolonged contact may lead to
Section B3 of Appendix B. This procedure or
drying and chapping of the skin. As with in
its equivalent should be used. Breathing vapor or fumes from heated
askarel should be avoided. Provisions should be made for adequate ventilation and regula tion of manufacturing operations to avoid
sulating oil, some people are allergic to askarel, and continued exposure may result in skin irritation. Both the liquid and vapor are moderately irritating to eye tissue.
Operating procedures should be such as to
open exposure to askarel (especially at tem peratures of 55C or higher). The gases pro duced when askarel is decomposed by very high temperatures (such as that of an electric
minimize or eliminate contact with askarels. The use of porous;gloves that can absorb.and retain askarel is to be avoided. Resistant gloves2 should be used if contact:is.unavoidable.
arc) in the presence of air or organic in sulating materials contain a very high per
Use of enclosed . transfer and .handling ..equipment, processing equipment, and mechanical washers re
centage of hydrogen chloride, and small per centages of carbon dioxide, carbon monoxide, and oxygen. Minute concentrations of this
duces direct contact.
2 For example, Edmont-Solvit 5-352 (Mersick of Bridgeport, Bridgeport, Conn), or the equiva lent.
,,
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Medicinal washes or mild detergents fol- - $e8 section 3.5). Containers used to transport
lowed by the application of cold cream will
askarel should not be used for storage or to
reduce the irritation resulting from the con-* transport other material without being com
tact of an open cut or abrasion with askarel. pletely cleaned of all traces of askarel.
Safety glasses with side shields or a
(Cleaning procedures must take cognizance of
face shield should be worn when handling
precautions against excessive exposure and of
askarels. If liquid askarel contacts the
the need for proper disposal of contaminated
yes, the eyes Should be irrigated immediately cleansing solvents and materials as set forth
with large quantities of running water for
in 3.5) Transfer from shipping containers to
approximately 15 minutes and then examined
processing systems should be through closed
by a physician (A drop of (O.S.P.) castor '
piping or tubing with appropriate valves,
oil has been found to reduce irritation)
pumps, etc. Provision should be made for
Persons developing a skin irritation or
trapping and disposing of fluid lost by leak
respiratory tract irritation while working
age or spills from the transfer system and
with askarels should be placed under the
from the storage containers.
supervision of a physician. Ingestion or
Drums to be retired from use should be
wallowing of askarels is not generally re
cleaned before crushing, delivery to scrap
garded as a problem of the industry; However,
dealers, or other disposal. Contaminated
should accidental ingestion occur, a physician cleaning fluids and materials should be dis
should be consulted.
posed of as Indicated in 3.5.
Hands should be cleaned of askarel before 3.3.3 Manufacturing Housekeeping. Manufactur
eating, drinking, smoking, or using toilet
ing equipment and operating procedures should
facilities by means of waterless hand clean ers3 and wipe towels which should then be
safeguard against loss of askarels to the en vironment through proper containment and dis
properly disposed of.
posal procedures.
3.3.2 Bulk fluid Shipment? Receiving and
3.3.3.1 Processing Area Control. Enclosed sys
Transfer. Shipment of askarel from point of
tems of sealed piping, properly gasketed joints,
manufacturing to point of receiving should
valves, containers, and processing chambers
be done in closed containers such as rail
should be used for all operations where askarel
tank cars, truck tanks, marine or barge tanks, temperatures may exceed 55C. Enclosure should
or sealed drums. In case of an askarel spill preferably extend to all other portions of the
during bulk fluid shipment, reference should
system insofar as practicable.
be made to paragraph 5.0 which provides pro
Establish containment methods and/or pro
cedures for control and listed authorities to cedures for all askarel processing areas to
be notified. Containers should be labeled
prevent loss to sewer systems by spillage,
as to contents and carry a label cautioning
leakage or other uncontrolled conditions or
against loss of fluid to the open environment events.
For example, Pow'r Kleen Handcleaner, (Woodbine Chemical and Research, Inc., Medina, Ohio or Man's Hands, Oak Industries, Inc., Uoosick Falls, Hew York)
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3.3.3.2 Types end Control of Liquid Askarel Wastes. Askarel-containing liquid wastes may
should be collected within the containment area for properly controlled laundering.
occur in manufacturing from sources such as the following} 1) Liquid askarel contaminatod during processing which is unsuitable for reclaiming as a dielectric fluid# 2) liquid askarel from solvent operations or water and detergent type washeri, 3) vacuum
3.4 Control of Plant Effluents. 3.4.1 Water Effluents. The industry goal is to eliminate askarel in plant water effluent streams. However# it is recognized that existing drain systerns in capacitor manufacturing plants are probably contaminated as a result of past practices.
pump oils contaminated with askarel# 4) steam jet vacuum system condensates contaminated
and askarel traces may continue to decrease with the proper containment of askarel wastes and no
with askarels, and 5) askarel containing materials from laboratory samples.
further discharges into drain systems. Other sections of this standard provide that no askarel
Waste fluids containing askarel should be
wastes of any kind be disposed of in any water
,
collected (by means of traps# drip pans# trays# etc) and disposal should be in accordance with
.Txtj luent streams and that accidental spills be'prevented from getting into such streams.
3.5. Spills of askarels should be contained and
cleaned up promptly by means of absorptive
3.4.1.2 Concentration Limits. The EPA has proposed water quality criteria to maintain PCB concentration in rivers and lakes below detec-
material# such as sawdust# or trapped and re*moved by pumping or other suitable means. Disposal should be per 3.5. 3.3.3.3 Types and Control of Other Askarel Con-
tion level. Requirements under Sections 307(a), 307(b) and 311 of the 1972 Amendments to the Federal Water Pollution Control Act are under review (1976-77) and the latest revisions will
taining Wastes. Saturation of materials with
apply. State and municipal requirements must
askarels may occur in manufacturing from the following eourcest 1) Saturated earth or other
also be met. Further information may be obtained from an
absorbent media from filtering operations or from cleaning up spills# 2) saturated filters from vapor control devices and other filters#
Environmental Protection Agency Regional Office. A listing of these offices is contained in Appendix D.
3) saturated wastes such as paper# rags# etc.
3.4.1.3 Monitoring Streams. On a regular basis
4) saturated spent gasket materials and 5} capac- consistent with plant situations, all effluent
itors failing tests or otherwise designated for
streams should be analyzed. The procedure for
disposal.
performing the necessary analyses is per ASTM
All of the above items should be collected
Method D3304. This procedure or its equivalent
for proper disposal. Wiper rags, protective clothing4 and other extraneous materials which
should be used.
are likely to be soiled should preferably be made of disposable materials. Other materials
4 For example, Edmont-Wilson, 1294 Walnut St., Coshocton# Ohio 43812# or Slosman Corp.# P.0. Box 3014, Asheville# N.C. 28802
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3.4.1.4 Methods for Minimizing Effluent Stream Disposal should be done in a manner which is
Contamination. The ideal approach is to isolate- consistent with proper concern for the environ
totally all effluents that could be contamina- ment and minimizes any release of askarels to
. ted with askarels during manufacturing processes the environment.
and prevent them from being discharged from the 3.5.1 Disposal of Capacitor Units. Scrap ca
plant. Carbon absorption,limestone beds,and sol pacitor units can be generated during manufactur
vent extraction'are techniques that could be ap ing processes or during field service. Produc
plied to reduce the askarel content of effluent tion rejects are those capacitors that are re
streams. These techniques may be most useful in cleaning up water used in plant processing and to permit recycling. 3.4.2 Air Effluents. The Industry goal Is to
jected after the impregnation process in the course of production by the capacitor manufactur er. They may be rejected for mechanical or
eliminate askarel vapors in plant air effluents. electrical reasons.
Bant operations involving askarels at elevated temperatures in excess of 55C should be per
Field rejects are those units that are re jected or, for other reasons, are to be scrapped
formed, wherever possible, within closed sys tems. Piltration of plant air effluents, to
after shipment from the plant where they were manufactured.
minimize PCBs entry into the environment,
Capacitor units should be disposed of intact,
should be accomplished where envoivement of air borne PCBs may occur from open operations.
or if leaking, in sealed drums. The small amount of liquid to be drained, the integrity of intact
3.4.2.1 Monitoring. All plant air effluents
units and the necessity for complex control over
should be sampled and analyzed on a routine basis consistent with plant situations. The
drainage procedures make intact disposal prefer able.
procedure for performing the analysis is per A5TM Method D3304 (See Appendix B3). 3.5 Scrap-Disposal Procedures. The manufac
3.5.1.1 Production Rejects. Rejected capacitors in capacitor manufacturing plants represent a concentration of askarel. Zt is, therefore, im
ture and use of capacitors involves processes
portant that disposition be made in a manner con
which produce askarel-saturated solids and liquids containing or composed entirely of
sistent with proper concern for the environment. Preference should be given to disposal of capac
askarel, which should be disposed of as wastes. itors in sites approved for hazardous waste dis
Specific sources of these materials are de
posal (See Appendix A). Another alternative,but
scribed throughout this standard. They may
less desirable, would be disposal In approved
be placed into three categories *
landfill sites.
1) Capacitor units impregnated with
askarel, production and field re
jects
"
Care should be exercised to insure that no loss of liquid will occur during transportation
2) Manufacturing process liquid wastes containing askarel
3) Solid waste purposely or accidentally saturated with askarel
to the disposal site. Incineration of scrap capacitors in facili
ties designed to accept such solids would pro vide a preferential alternative to approved land
fill sites when such services become available.
( >;
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l.s.l.2 Field Ralecti. Wherever practical, ell preferable disposal procedure is an approved
askare1 containing capacitors should be re
landfill site. See Appendix A for listing of
roved prior to disposal of equipment. This
Facilities.
,
precaution will enhance environmental control
3.5.4 Packaging and Shipment.
procedures and insure that by removing these
3.5.4.1 Transportation to the disposal facility
capacitors they do not ultimately disperse
should be in containers that will prevent leak
their aekarel contents into an unapproved
landfill site.
'
age and accidental loss of askarel to the en
j vironment.
After removal from equipment, capacitors j
I should be disposed in accordance with the pro
3.5.4.2 Containers should be labeled as to con tents and precautions relative to loss to the
cedures for production rejects (3.5.1.1).
environment per 3.3.2.
Where removal of aakarel-containing capacitors
3.5.4.3 Containers for this purpose cannot be
fro* equipment is not practical, that equip
used for any other materials or they should be
ment should be disposed of only in approved
retired from service until they are completely
landfill sites.
cleaned. Any solvents used in cleaning these
3.5.2 Disposal of Liquid Wastes. All vasts
containers will be contaminated with askarel
as karel or liquid wastes containing aek&rsl
and should be disposed of according to the same
should be disposed of in accordance with one
procedures described in 3.5.2.
Of the procedures given in 3.5.2.1 or
3.6 Labeling. Capacitor units vary greatly in
3.S.2.2. However, preference should be given
size and in end use or application. Small capac
incineration, 3.5.2.1.
itor units are frequently applied as a component
3.5.2.1 Incineration. Proper incineration
of another piece of equipment, such as a fluores
must involve a suitable balance between dwell
cent lighting ballast,a roadway of area lighting
time and temperature in the incinerator plus
luminaire, a motor, etc. In such applications a
oxygen availability, and finally, suitable
label on the capacitor unit referencing approved
scrubbers to remove the HCL that will be
disposal procedure would not normally be visible
formed; for example, 2-second dwell time at
when the piece of equipment is disposed of.
2000P and 31 excess oxygen in stack gas, or
Tor the foregoing reasons the methods of label
1.5 second dwell time et 2700F and 21 excess
ing for small capacitors and large capacitors are
oxygen in stack gas.
treated separately in 3.6.1 and 3.6.2, respectively.
These facilities should meet the appli
3.6.1 Small Units. Small capacitors are defined as
cable state requirements end should control
those that contain askarel in quantities up to
effluents within the limits set forth in
about 2 pounds each and in which the free liquid
this standard.
does not exceed 0.4 pounds. They are hermetically
3.5.2.2 Chemical Waste Disposal. Where in cineration is not feasible, sites which have
sealed in metalic cases. It is recommended that shipping containers from capacitor manufacturers
been classified by state agencies as suitable
should be labeled as to contents and that trans
for disposal of chemical waste liquids should
porters be given instructions, in accordance with
be used (Sea Appendix A).
3.5.3 Disposal of Solid Wastes (See 3.5.1 for scrap capacitors). All solid wastes which have been saturated with askarel should bo placed in leak proof containers and preferably trans ported for disposal by incineration. A less
paragraph 6.12 as to procedures in the event of a spill.
If, however, a label of the capacitor is required by statute or by specific manufacturers, the follow ing is suggested;
Contains PCBs. Dae care in disposal.
.
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The shipping container label, yellow on
or spillage that may have occurred in shipping.
black, should contain the following informations If leakage is evident, the cause should be
"CAUTION* Contains PCBs (Polychlorinated
BiDhenvls) that are environmen-
.
tal contaminants* In case of
leaks or soills. restrain dis-
charoe and consult manufacturer.
In transportation emergencies,
call National Response Center
(800-424-8802) and Chemtrec
(800-424-9300), Avoid pro
longed breathing of vapors or
mists, contact with eyes or
skin. Disposal should be in
accordance with ANSI C-107
- - -- Guidelines or applicable state and Federal statutes."
corrected and the spillage soaked up with ab sorbent materials such as sawdust, followed by a cleanup of the affected area with kerosene or other approved solvent such as perchloroethylene. All materials used should be collect ed for proper disposition as described in 3.5. 3.7.3 Installation and Periodic Inspection. Large capacitors should be installed in new
Small unit capacitors are applied as a
facilities such that if a leak should develop,
component of a large piece of equipment.
aakarels can be restrained from reaching the
Manufacturers utilizing askarel-filled capac
environment. Depending upon the type of in
itors should affix a label referencing this
stallation, consideration may be given to pans,
standard or describing disposal procedures consistent with it.
dams, traps, standpipes, dry wells, absorbing agents, etc.
3.6.2 Large Units. Large capacitor units are
Following installation, the unit should
defined as those which contain more than 2
again be inspected for any damage or leakage.
pounds of askarel. The manufacturer should
It is recommended that periodic in-service in
affix a label in a conspicous place on the
spections be made for leaks.
capacitor, referencing this standard or des cribing disposal procedures consistent with it. As a minimum, the label should contain informmation listed in 3.6.1. 3.7 Information for Users of Large Capacitors 3.7.1 General. Large Askarel-filled capacitors contain more than 2 pounds of askarel and de livered to customers as sealed units from which there is no escape of askarel under normal operation. Although certain types of equip ment failures can permit loss of some askarel to the environment, such cases are extremely rare. 3.7.2 Transportation and Receiving. Immediately upon receipt of a shipment and following any transportation or handling accident that could ffact the integrity of the capacitor enclo sure, the transportation vehicle, enclosure, and fittings should be examined for any leakage
4. Transformer Guidllnea. 4,1 General. 4.X.1 Askarels of various compositional types are currently in use (for the general proper ties and types, see ASTM D2283-73a(20)). The trademark designations used by manufacturers for liquids containing PCBs are given in Appendix C.
Under arcing conditions, the gases produced, though predominantly consisting of noncombust ible hydrogen chloride, can contain varying amounts of combustible gases depending upon the askarel type. 4.1.2 Safety Precautions. Based on about 40 years of safe industrial usage, askarels have been considered as relatively harmless mater ials to humans There has been no known instance of human injury when askarels are used under the normally prescribed conditions of pre
caution and handling. _ a
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Although it has been generally thoughtthat
in case of accident. If the odor of
exposure to askarels is not hazardous pro
askarel or its arced products is detected
vided that simple precautions are taken, ex
posure should still be avoided or minimized.
.4 1.2.1 Vapors. The odor of askarel is
.
noticeable well below the maximum safe air
by the person wearing protective equipment, he should immediately go into fresh air. All gas masks, respirators, and replacement parts should have U.S. Bureau of Mines approval
concentrations. Depending upon the composi
and be maintained on a regular schedule in
tion of the askarel used, from 0.5 to 1.0
accordance with the manufacturer's recommen
milligram per cubic metre of air has been determined to be the upper safe level of
dation.
.4 1.2.2 Liquid.
In contrast to the situa
exposure during an 8-hour workday. (See re
tion in which mineral insulating oils are han
ference (19)).
dled, there is no fire hazard in handling
The procedure for performing the neces
askarels. A limited solvent action (similar
sary analysis is contained in ASTM Method
to that' for paint thinner) on the fats and
D3304 (See Appendix B).
oils of the skin with prolonged contact may
Breathing vapor or fumes from heated
lead to drying and chapping of the skin. As
askarels should be avoided. High concen
with insulating oil, some people are allergic
trations of vapors can cause irritation of
to askarel, and continued exposure may result
the eyes, nose, throat, and upper respira
in skin irritation. Both the liquid and vapor
tory tract. Provisions shall be made for
are moderately irritating to eye tissue.
adequate ventilation to avoid open exposure of hot askarels (55C or higher). The gases
Operating procedures should require avoid ance of contact with any askarels. The use of
produced when askarel is decomposed by very
porous gloves that can absorb and retain
high temperatures (such as that of an elelc-
askarels is to be avoided. Resistant gloves
tric arc) in the presence of air or organic
and aprons such as the polyethylene or
insulating materials contain a high percen
fluoro elastomer type should be used if contact
tage of hydrogen chloride which is highly
is unavoidable. For some operations, it has
toxic, and small percentages of other gases.
been found advantageous to use non-porous, dis
Minute concentrations of this combination of
posable aprons and gloves. In case of spill
gases are very unpleasant and irritating,
age on clothing, the clothing should be re
thus giving ample warning of their presence.
moved as soon as practical, the skin cleaned
Zf exposure to high concentrations of askarels with waterless cleaners or solvents such as
or its arced products is necessary under em-
kerosene, and wiped dry with disposable towels.
rgoncy conditions, an approved gas mask of the organic canister type, or self-contained
These towels should be disposed of as PCB con
. taminated solid wastes. See Section 4 1.6.2.2.
breathing apparatus, must be worn. Such ex
Clothing and shoes saturated with askarel
posure should be under the surveillance of
should be discarded (burnable waste). Con
other personnel capable of effecting rescue
taminated clothing may be reused providing that
For example "VITON"
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it has been thoroughly cleaned using segre
4.1.3.2 Spill Procedures - Bulk liquid shipments.
gated solvents or a segregated degreaser, then followed by normal laundering. (Launder ing alone is not sufficient.)
Medicinal washes or mild detergents
See Section 6. 4.1.4 Receiving, Handling, and Storage of Askarels.
Askarels are shipped in tank cars, tank
followed by the application of cold cream *
trucks, steel drums, metal cans, and test-
will reduce the irritation resulting from
sample containers. When received, all con
the contact of an open cut or abrasion with
tainers should be inspected for leaks.
askarel.
4.1.4.1 Storage Tanka. Storage tanks should
Safety glasses with side shields or a
be erected so that inspection can be made for
face shield should be worn when handling
leaks or spills. Construction should be such
askarels. Eyes that have been exposed to
that inadvertent leakage or spills are pre
liquid askarel should be irrigated iasnedi-*
vented from reaching streams and sanitary or
ately with large quantities of running water
storm sewers.
for approximately 15 minutes and then exam
4.1.4.2 Tank Cars and Tank Trucks. All bulk
ined by a physician. (A drop of (U.S.P.)cas
shipment equipment should be inspected for
tor oil has been found to reduce irritation.) Ingestion or swallowing of askarels is
leaks immediately upon receipt. Drain pans should be provided to prevent spillage from un
not generally regarded as a problem of the
loading hoses and connections. Askarel liquid
industry; however, should accidental inges
collected in drain pans should be placed in
tion occur, a physician should be consulted.
drums labeled "Scrap Askarel* for disposition
Hands should be cleaned as noted above
in accordance with 4.1.6.2.1.
.
before eating, drinking, smoking or using
4.1.4.3 Steel Drums, Can3, and Test Sample Con
toilet facilities.
tainers. On delivery, all such shipments should
be carefully inspected for leaks. The contain
4.1.3 Liquid Transport Containers.
ers should be stored indoors in an area expe-
4.1.3.1 Transport Container Marking. Any con cially selected for this purpose. A curb
tainer, such as tank cars, tank trucks, drums, should enclose the area to provide a basin for
cans, etc., used to transport transformer
containing the askarel from one or more con
askarels, new or used, should be labeled
tainers should the containers be damaged. The
with the following(yellow on black)*
area should not have a drain that is connected
CAUTION" Contains PCBs(Polychlorinated Biphenyls) that are environmental contaminants. In case of leaks or spills, restrain discharge and consult manufacturer. In transpor tation emergencies, call National Response Center (800-424-8802) and Chcmtrec (800-424-9300). Avoid pro longed breathing of vapors or mists, contact with eyes or skin. Disposal should be in accordance with ANSI C-107 Guidelines or applicable state and Federal sta tutes."
to a sanitary or storm sewer. If an indoor storage area is not possible,
the containers should be stored under a leanto with similar containment capabilities.
0269243
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PCB-ARCH0745461
4.1.5 Control of Water Effluents. The Indus try goal is to eliminate askarel in water effluent streams. However, it is recognized that existing drain systems from manufactur ing plants, repair shops, and installation sites may be contaminated as a result of past practices. Other sections of this standard provide that no askarel wastes of any kind be disposed of in any water effluent streams and that accidental spills be prevented from getting into such streams. 4.1.5.1 Concentration limits. The EPA has proposed water quality criteria to maintain PCB concentration in rivers and lakes below detection level. Requirements under Sections 307(a), 307(b), and 311 of the 1972 Amend ments to the Federal Water Pollution Control Act are under review (1976-77) and the latest revisions will apply. State and municipal requirements must elso be met.
Further information may be obtained from the Environmental Protection Agency Regional Office. A listing of these offices is con tained in Appendix D. 4.1.5.2 Monitoring Streams. All plant effluent streams should be monitored on a regular basis. The procedure for performing the necessary analysis is contained in ASTM Method D3304 (See Appendix B). 4.1.5.3 Methods for Minimizing Effluent Stream Contamination. The ideal approach is to totally isolate all effluents that could be contaminated with askarels during manufac turing processes and prevent them from being discharged from the plant.
4.1.6 Disposal procedures and Services.
4.1.$.1 Sources of Materials Requiring Special
Handling and Disposal Procedures. Liquids con
taining PCBs and solids containing or con
taminated with PCBs may come from many
sources including transport containers, trans
former manufacturing processes, in-test failures,
liquids contaminated beyond reclamation, in
service transformer leaks and failures, askarel-
filled transformers scrapped for any reason,
sample containers and handling equipment.
4.1.6.2 Classification for Disposal of Mater
ials Containing PCBs.
In general, there are
four types of materials requiring disposali
burnable liquids contaminated with PCBs; non-
burnable liquids contaminated with PCBs; burn
able solids contaminated with PCBs; and non-
bumable .solids contaminated with PCBs.
4.1.6.2.1 Burnable Liquids. Liquids containing
PCBs , requiring disposal by high-temperature
incineration may consist of the following;
(1) PCBs contaminated with mineral oil.
(2) Mineral oil contaminated with PCBs.
(3) Nonreclaimable contaminated trans
former askarels, arced askarels,
askarels from manufacturing spills,
sump accumulation, askarels from
holding basins, drip and drain pans,
washings, sample jars and containers,
etc.
4.1.6.2.2 Honburnable Liquids (Water) Con
taminated with PCBh. Water contaminated with
PCBs may be treated by such means as activated
carbon filtration or by a reductive dechlorina
tion process, providing that the effluent meets
Federal and State water effluent standards.
Such liquids may also be disposed of, packed in
suitable containers, in approved landfills. See
Appendix A.
026924*
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PCB-ARCH0745462
4.1.6.2.3 Burnable Solid Waste Materials Contaminated with PCBs. These materials cam be disposed of by high-temperature incineration and consist of cellulosic materials, rags, proaaboard, wood, sawdust, fuller's earth in bulk or in cloth bags, blotter papers, nitrile or cork gaskets, etc. 4.1.6.2.4 Nonburnable Solid Waste Materials Containing or Contaminated with PCBs. These materials may consist of steel, cooper, aluminum, filter units of the steel mesh con struction type, askarel drums, cans, etc.
Materials of this nature should be allow ed to drain with liquids collected in drip pans, etc. Further removal of adhering PCBs should be accomplished by vapor degreasing, washing or solvent extraction with kerosene or other approved washing liquids such as perchloroethylene. Accumulated liquids should be disposed of as indicated in 4.1.6.2.1. Solid materials as cleaned above may be handled as normal scrap.
Coil structures may be dismantled with burnable material removed. Metals should be treated as noted above, and burnable solids disposed of in accordance with Section 4.1.6. 2.3. An alternative but less desirable pro cedure for disposal of coils, cores, burnable waste, etc., is to suitably package and bury in an approved landfill site. See Appendix A. 4.1.6.3 Shipment of Scrap Liquids For Dis posal. All liquid scrap material should be placed in appropriate metal transport con tainers, properly labeled (Section 4.1.3.1) for shipment to a company offering an accept able disposal service (Appendix A).
4.1.6.4 Shipment of Burnable Solid Wa3te Material Containing PCBs for Disposal. Material of this type should be placed in a liquid-tight container meeting Federal and State transportation requirements, and acceptable to the disposal organization. The container should be properly labeled (Section 4.1.3.1) for shipment to a company offering an acceptable disposal service (Appendix A). 4.1.6.5 Liquid and Solid Waste Disposal Ser vice Organizations. These facilities should meet the applicable requirements of the state in which they are located and should control effluents within the limits referred to in Section 4.1.5.1. 4.2 Guidelines for Original Manufacture, Ser vice and Repair Shops. 4.2.1 Plant Housekeeping It is necessary to assume that in filling equipment with askarel, and during further handling of this equipment, an askarel spill may occur. Therefore, it is ncessary to provide facilities and a procedure for cleanup to prevent contamination. 4.2.1.1 Askarel Filling Area. 4.2.1.1.1 It is desirable that the askarel filling area be adjacent to the test area and final shipping area to minimize the danger of damage to units during handling. 4.2.1.1.2 The main manufacturing area for filling equipment with askarel should be pro vided with impervious surface floors or suit able basins so constructed that any inadvertent leakage or spills are prevented from reaching streams, sanitary sewers, or storm sewers. All askarel-handling equipment, such as pumps, hoses, etc., shall be of the askarel-resistent type.
0269M5
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PCB-ARCH0745463
4.2.1.1.3 Drip pans shall be provided for
for disposition. Cloth bags filled with fuller's
hose connections and filling valves.
earth should be placed in the "SCRAP BURNABLE
4.2.1.2 Special Containers for Scrap Mater ASKAREL WASTE" container for disposition.
ials.
4.2.X.4' Teardown of Units for Repair or Scrap.
4.2.1.2.1 Drums labeled "SCRAP ASKAREL"
4.2.1.4.1 Drain all askarel from the unit either
should be available for handling all spilled into a holding tank for reuse or into the drum
and waste askarel from sumps, failed units,
labeled "SCRAP ASKAREL" for disposition, allow
drip pans, sample jars, etc.
ing sufficient time for all of the askarel to
4.2.1.2.2 Open-head drums with suitable
drain from the core and coils.
closures and labeled "SCRAP BURNABLE ASKAREL 4.2.1.4.2 Remove the core and coil assembly
WASTE" should be available for handling con from the transformer tank and place over a suit
taminated cellulose insulation, rags, paper, able drip pan.
pressboard, wood, gaskets, sawdust, etc.
4.2.1.4.3 Place all materials in the appropriate
4.2.1.2.3 Separate containers for handling
salvage containers during dismantling for later
steel, copper, and aluminum, each adequately disposition.
marked, shall be provided for the components 4.2.1.4.4 All used materials,.including rags,
of contaminated core and coil assemblies.
sawdust, tape, etc., regardless of quantity,
These containers are required for the various shall be put into the appropriate containers for
materials when repairing or scrapping
disposition.
-
assemblies.
4.2.2 Transformer Labeling and Shipment
4.2.1.2.4 Containers for supplies of mater 4.2.2.1 New and Rebuilt Transformers. All new
ials for absorbing small askarel spills or
and rebuilt transformers that contain PCBa shall
cleanup of larger spills should be provided. have a label of adequate durability, permanently
4.2.1.3 Conditioning of Aakarels.
and prominently attached to the tank by the manu
4.2.1.3.1 Askarel Conditioning Equipment.
facturer, giving adequate warning and instruc
The conditioning unit should be located
tions. A suggested label, yellow on black, in
either in the storage tank area or in the
cludes the following:
main transformer manufacturing area for " filling with askarel.
4.2.1.3.2 Fuller's Earth. Conditioning of new askarel or recycled askarel requires fuller's earth treatment. The spent fuller's earth in cartridges or bags, when replaced, should be allowed to drain thoroughly over drip pans to remove as much liquid askarel
CAUTION" Contains PCBs (Polychlorinated Biphenyls) that are environmen tal contaminants. In case of leaks or spills, restrain dis charge and consult manufacturer. In transportation emergencies, call National Response Center (800-424-8802) and Chemtrec (800-424-9300). Avoid prolonged breathing of vapors or mists, contact with eyes or skin. Dis posal should be in accordance with ANSI C-107 Guidelines or applicable state and Federal ata-
tutea."
as possible. The cartridge units of steel
4.2.2.2 In-Service Transformers. The Transformer
mesh construction should be placed in the
manufacturer should make available suitable labels
"STEEL CONTAMINATED WITH ASKAREL" container
with similar warning as shown in 4.2.2.1 for use
on existing transformers.
4.2.2.3 Shipping papers should contain the warning
statements given in 6.3.2.
02fc92<6
PCB-ARCH0745464
4.2.3 Information for Transformer Users 4.2;3.1 General. Askaral-filled transformers are delivered to customers as sealed units from which there is no escape of askarel under normal operation. Although certain types of equipment failures can permit loss of some askarel to the environment# such cases are extremely rare. 4.2.3.2 Transportation and Receiving. Im mediately upon receipt of the equipment and following any transportation or handling accident that could affect the integrity of the tank# bushings# or radiators, the trans portation vehicle# tank# and fittings should be examined for any leakage or spillage that may have occurred in shipping. If leakage is evident, the cause should be corrected and the spillage soaked up with absorbent mater ials such as sawdust, followed by a cleanup of the affected area with rags soaked with kerosene or other approved solvent such as perchloroethylene. All materials used should be collected for proper disposition as des cribed in 4.1.6. 4.2.3.3 Installation and Periodic Inspection. Transformers should be installed so that if a leak should develop, askarels can be re strained from reaching the environment. De pending upon the type of installation, con sideration may be given to pans# dams# traps# standpipes, dry wells# absorbing agents, etc.
Following installation, the unit should again be inspected for any damage or leakage. It is recommended that periodic in-service in spections be made for any leaks.
4.2.3.4 'Filling'# Filtering#' or Drying Askarel.
Most askarel units are shipped with the proper
amount of askarel, but if it becomes necessary
to top off a unit, the manufacturers's in
structions should be followed.
If it is necessary to dry an askarel unit
or to treat an askarel unit with fuller's
earth, instructions should be followed. When
filtering or conditioning askarel, all of the
precautions previously described for drip pans,
proper disposal of filter media, etc. apply.
4.2.3.5 Sampling. It is common practice to
sample askarel from a transformer for periodic
maintenance testing. As previously described,
such samples should be taken in a manner to
avoid any contamination of the environment.
Washings should be collected for proper dis
posal. Field and laboratory test samples,
washings, etc., should also be collected for
proper disposal.{See Section 5).
4.2.3.6 Transformers Installed in Moving
Vehicles. In the event of a leak or accidental
spill, the procedures outlined in Section 6
should be followed.
.
4.3 Retrofilling Apparatus Containing Askarel3.
It is not recommended that apparatus containing
PCB liquids be changed to other liquids. It is
recognized that the best possible change-out
procedures will still leave appreciable PCBs
in the apparatus. Apparatus that has contained
PCBs which has been replaced with another
fluid should be labeled as indicated below, and
the disposal ultimately should follow the same
disposal procedures as those recommended for
PCB liquids and PCB-filled apparatus.
02692*7 -15-
PCB-ARCH0745465
Label (yellow on black)
CAUTION* Contains liquid con taminated with PCBs an environmental con taminant. Changed to (describe liquid) on (give date).
4.4 Transformer Disposal.
The ultimate disposal of a PCB-containr-
ing transformer may be accomplished by the
following procedures*
1. Contract with a qualified organiza tion for disposal of the complete transformer.
2. Where acceptable facilities are available, the following alterna tive procedures are recommended*
(a) Always drain the liquid and dispose of it by approved incineration.
(b) For the solid components or for the entire structure, either of the following procedures are recommended *
i. Dismantle, wash and dispose in accordance with Section 4.1.6.
6. Spill Notification and Control Plan
Polychlorinated Biphenyl(PCBs)
The immediate actions needed are to contain or restrain liquid spills with the best means available and to notify "CHEMTREC" and "The National Response Center."
"The basis for this spill notifica tion and control plan relies on Chemtrec to advise on the immediate actions needed to contain or restrain the liquid spill with the best means available based on listed instructions. The National Response Center will notify all interested parties, i.e. Federal and State authorities and the manufacturers involved, as well as give guidance on action to be taken."
FAILURE TO REPORT SPILLS TO PROPER AUTHORITIES MAY RESULT IN CRIMINAL PENALTIES.
6.1 Chemtrec
6.1.1 What is it. - Chemtrec stands for
Chemical Transportation Emergency Center, a
public service of the Manufacturing Chemists
Association at its offices in Washington, D.C.
Chemtrec provides immediate advice for
ii.
Ship entire solid struc ture to acceptable organization for disposal.
those at the scene of emergencies, then prompt ly contacts the shipper of the chemicals in
iii. Ship to acceptable land fill disposal site. (See Appendix A).
volved for more detailed assistance and appro priate follow-up.
5. Disposal of Laboratory Samples Contain ing PCBs.
The disposal of laboratory samples and materials used for testing and experimental purposes which contain, are impregnated with, or contaminated by PCBs (askarels) must be carefully controlled. Their disposition should be made in a manner consistent with procedures in 3.5.2 and 3.5.3 (Capacitors)
Chemtrec operates around the clock - 24 hours a day, seven days a week - to receive direct-dial toll-free calls from any point in the continental United States through a wide area telephone service (WATS) number, 800-424-9300 (483-7616 for calls originating within the District of Columbia; 202-483-7616 for calls originating outside the continental D.S.).
and 4.1.6 (Transformers).
0269248
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PCB-ARCH0745466
6.J..2 It is recommended that all past and
6.4
Installed Equipment
present manufacturersof PCBs and PCB-con-
It is recommended that all users should have an
taining equipment be listed with Chemtrec.
on-site spill prevention counter-measure and
Contact "CHEMTREC" at.the manufacturing
control plan which should be followed in the
Chemists Association, 1825 Connecticut Ave., event of an accident.
N.W., Washington, D.C. 20009.
6.4.1 Capacitors
6.2 National Response Center. 6.2.1 What is it Location! U.S. Coast Guard Headquarters, Nassif Building, 400 7th Street, S.W. Washington, D.C. 20590. Function* To coordinate pollution emergen cies when national involvement is required. Nationwide Reporting Network for receiving pollution reports. The basis of this net work is a well publicized toll-free tele
Capacitors should be installed in accordance ' with 3.7.3.
6.4.2 Transformers Transformers should be installed in accordance with Section 4.2.3.3. 6.4.3 Spills In case of liquid spills due to leaks or equipment failures, the procedures outlined in sections 3.7.2 for capacitors and 4.2.3.2 for transformers should be followed.
phone number (800-424-8802) which anyone
may use to call the National Response Cen
ter reporting pollution incidents or acci
dents which may result in pollution.
Relay of Pollution Reports to the local
representatives of the Federal Agency re
sponsible for action when a pollution dis
charge has ^occurred. When necessary, other
specific local, regional, or national rep
resentatives for the various agencies will
also be notified.
6.3 Shipment of Liquids and Equipment Con
taining PCBs.
t
6.3.1 Labeling All containers and equip
ment containing PCBs shall be labeled in
accordance with sections 3.6, 4.1.3, 4.2.2.1
and 4.3.
6.3.2 Shipping Papers. Shipping papers
should contain the following warning state
ment t
CAUTION: Contains PCBs(askarel) that are environmental contaminants. In case of leaks, or spills, restrain discharge, DO
NOT FLUSH. For further instructions call Chemtrec (800-424-9300) and the manufac turer. Also notify* National response Center (800-424-8802).
7. REFERENCES
7.1 References to Text
(1) Standard Method of Test for Rapid Gas Chromatographic Estimation of High Boiling Homologues of Chlorinated Biphenyls for Capa citor Askarels,(ASTM D3303-74].
(2) American National Standard Method of Test for Specific Gravity of Askarels, C59.1965 (R1973) (ASTM D 1810-63 (1973)].
(3) American National Standard Method of Test for Neutralization Number by Color-Indicator Titration, 211,131-1964 (R1974) (ASTM D 976-64 (1973), IP 139/65).
(4) American National Standard Method of Test for Neutralization Number by Potentioraetrie Titration, Zll.59-1958 (R1971) (ASTM D664-58 (1968), IP 177/641 .
(5) Standard Method of Test for Density of Rubber Chemicals,[ASTM D 1817-66 (1972)].
(6) American National Standard Method of Test for Inorganic Chlorides in Askarels, C59.55-1963 (R1973)( ASTM D 1821-63 (1973)).
(7) American National Standard Method of Test for Pour Point of Petroleum Oils, 211.5-1966 (R1972) (ASTM D 97-66 (1971), IP 15/67)].
(8) American National Standard Method of Test for Power Factor and Dielectric Constant of Electrical Insulating Liquids, C59.22-1967 (R1973)( ASTM D 924-65 (1973)].
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PCB-ARCH0745467
(9) American National Standard Method of Teat for Specific Resistance (resistivity) of Electrical Insulating Liquids, C59.51-1965 (R1973) l ASTM D 1169-64 (1973)1 .
(10) American National Standard Method of Teat for Hydrolyzable Chlorine Compounds in Chlorinated Aromatic Hydrocarbons (Askarel) C59.106-1970(ASTM D 1820-65 (1971)).
(11) American National Standard Method of Test for Thermal Stability of Chlorinated Aromatic Hydrocarbons (Askarels), C59.1111970 [.ASTM D 1936-64 (1971)1.
(12) American National Standard Method of Test for Distillation of Road Tars, A37.91974 [ ASTM D20-721.
(13) American National Standard Methods of Testing Electrical Insulating Oils, C59.21974 ASTM D 117-71 (1973)
(14) American National Standard Method of Teat for Dielectric Breakdown Voltage of Insulating Liquids Using Disk Electrodes, C59.19-1968 (R1973) ( ASTM D 877-67 (1971)).
(15) American National Standard Method of Test for Plash and Pire Points by Cleveland Open Cup, Xll.6-1973 (ASTM D 92-74, IP 36/67).
(16) American National Standard Method of Test for Saybolt Viscosity, 211.2-1956 (R1971) l ASTM D 88-56 (1973)1 .
(17) American National Standard Method of Test for Coefficient of Thermal Expansion of Electrical Insulating Liquids of Petroleum Origin, and Askarels, C59. 57-1963 (1973) (ASTM D 1903-63 (1973)).
(18) MUNCH, R.H. Measuring the dissipation
factor, dielectric constant, and resistivity
of liquids. Insulation/Circuits, vol 16, Mar.
1970, pp 46-4?:
`
(19) Chlorodiphenyls. Hygienic Guide Series. Westmont, New Jersey: American Industrial Hygiene Association, Jan-Feb 1965.
(20) Standard Specification for Chlorinated Aromatic Hydrocarbons (Askarels) for Transformars.l ASTM D 2283-73.1
7.2 General References
Polychlorinated Biphenyls and the Environment, Interdepartmental Task Force on PCBs, Wash ington, D.C., May 1972. (National Technical Information Service, U.S. Dept, of Commerce, Springfield, Va. 22151.) (COM-72-10419).
DRINKER, C.K. Further observations on the
possible systemic toxity of certain of the
chlorinated hydrocarbons. Journal of Indus-.
trail Hygiene and Toxicology, vol il, 1939,
* pp isr-Tl'9.
---------------
DRINKER, C.K.) WARREN, M.F.f AND BENNET, G.A.
The problem of possible systemtfc. effects from chlorinated hydrocarbons, Journal of Industrial Hyqiene and Toxicoloqy, vol' 19, 1937, pp ill-328.
ELKINS, H.B. The Chemistry of Industrial Toxicology. New York: John Wiley 6 Sons, Inc., 1959.
GREENBURG, L.; MAYERS, M.R.; AND SMITH, A.R. The systemic effects resulting from exposure to certain chlorinated hydrocarbons. Journal of Industrial Hyqiene and Toxicology, vol. 2i, 1939, pp 29-38.
Threshold Limit Values for Chemical Sub stances and Physical Agents" in the Work room Environment. Cincinnati: American Conference of Govermental Industrial Hygienists, 1973.
TREON, J.F.) CLEVELAND, F.P.fCAPPEL, J;
and ATCHLEY, R.W. The toxicity of the vapors
of Aroclor 1242 and Aroclor 1254. American
Industrial Hygiene Association Quarterly,
vol. 17, 1956, pp 104-211
*
8. REVISION OF AMERICAN NATIONAL STANDARDS RE FERRED TO IN THIS DOCUMENT. When the American National Standards referred to in this document are superseded by a revision approved by the American National Standards In stitute, Inc., the revision shall apply.
0269250
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PCB-ARCH0745468
APPENDIXES (These Appendixes are not a part of American National Standard Guidelines for Handling and Disposal of Capacitor - and Trans former-Grade Askarels Containing Polychlorinated Biphenyls, C107.1 -197__, but are included for information purposes only.
APPENDIX A Disposal Services
(g) Richmond Sanitary Service Richmond, California (415-234-3304) All forms.
In addition to the supervised dry land fill sites that may be used for the disposal of askarel-containing scrap, the following additional known facilities and services have been established. For other facilities, call your regional Environmental Protection Agency Office. (See Appendix D).
2. Chemical Waste Disposal Co. Elizabeth, N.J. (201-351-5460) Disposal by incineration
3. Chem-Trol Pollution Services, Inc. P.O. Box 200 1550 Balroer Road Model City, N.Y. 14107 Phoner 716-754-8231
Can handle solids and liquids by incinera
tion or land disposal.
The firms listed below (not all-inclusive) will accept PCBs for treatment or disposal, as noted. The Environmental Protection Agency does not endorse any of these firms and cannot vouch for the environmental adequacy of their operations. Each-of' these firms has been' contacted and reports
having the required technical characteris tics to adequately handle PCBs, in accord ance with Recommended Procedures for the Disposal of PCB-Containing Waste (Indus trial Facilities) as published by EPA in the Federal Register. The appropriate State or EPA Regional Office should be consulted for environmental suitability of the firm/site.
This organization has facilities and ser
vices capable of handling:
(1) Liquids. solvents or oils. incineration.
Askarels alone or mixed with Disposal by High-temperature
(2) Solids (software). Askarel-soaked com pounds, rags, cartons, absorbing earths, etc. Disposal by incineration or scientific landfill.
(3) Solids (hardware). Capacitors, trans former tanks, cores, askarel-soaked metals. Disposal by scientiric landfill. Has solvent extraction capability.
1. California Class I Landfills
4. Hyon Waste Management Services, Inc.
Chicago, 111. (312-646-0016)
(a) Casmalia Disposal Site
Santa Barbara, California (800-969-4703)
Can handle solids and liquids by Incinera
Bulk Liquids and drummed materials.
tion.
(b) BKK Corporation
Wilmington, California (213-775-3607)
5. Monsanto Company
All forms.
800 North Lindbergh Boulevard
St. Louis, Missouri 63166
(c) Environmental Protection Corporation
Phone: 314-694-3352
Bakersfield, California
All forms.
Handles only liquid askarels manufactured
(d) County of Los Angeles Whittier, California (213-699-7411) Facilities: Palos Verdes Calsbasas All forms.
(a) San Diego County San Diego, California (714-565-5703) All forms
(f) Ventura County Dept, of Public Works Ventura, California (805-648-2717) All forms.
by Monsanto. Disposal is by incineration. This organization has facilities and ser
vices capable of handling askarel liquids alone or mixed with other oils or solvents by hightemperature incineration. Liquid is pumped through a gun with atomizing steam into incinera tor.
0^69251
PCB-ARCH0745469
Temperatures are maintained at 2000F with
auxiliary natural gaa. Exit gases are quen ched to 180F by contact with water. Gas is
then passed through a high-energy venturi ,
scrubber for removal of particulates. Before o
exhausting to air (110 F, gases are passed
through a packed column scrubber to remove
BC1. Askarel liquids containing more than
II water, or any phosphate esters cannot be
accepted.
6. Nuclear Engineering Co., Inc. Lousiville, KY. (502-426-7160)
Facilities: Sheffield, 111. Beatty, Nev.
Disposal by landfill? Can handle drummed
liquids and solids.
Nuclear Engineering Company Eastern Division P.O. Box 146 Morehead, Ky. 40351 Phone: 606-784-6611
Nuclear Engineering Company Disposal Division Sheffield, 111. 61341 Phone: 815-454-2624
The organization provides containerization,
transporation, and disposal services of all
liquids and solids (including hardware). Dis
posal is in controlled chemical and scientific
landfill area. Licensed by Atomic Energy
Commission for radioactive waste disposal.
The organization also has two West Coast loca
tions, in the states of California and Washin-
ton.
7. Rollins Environmental Services, Inc. P.O. Box 2349 Wilmingtoft, Delaware 19899 Phone: 340-658-8541
This organization has facilities and ser
vices capable of handling;
(1) Liquids. Askarel alone or mixed with solvents or oils. Disposal is by high-tamperatuxe incineration.
(2) Solids (software). Askarel-soaked com pounds, rags, cartons, absorbing earths, etc. Disposal is by incigeration at combustion teapeatures up to 2500 F. Incineration gases axe scrubbed, and entrained solids are removed be fore exhausting to air.
Rollins Environmental Services maintains dis
posal facilities in the following areas:
Philadelphia/Camden: Rollins Environmental Services, Route 322 Logan Township Bridgeport, New Jersey 08014
Inc.
Baton Rouge: Rollins Environmental Services, Inc. Scenic Highway f, West Cheatham Lane Scotlandville East Baton Rouge Parish, La. 70807
Houston: Rollins Environmental Services, Tidal Road & Highway 134 Deer Park,Texas 77536
Inc.
8. Texas Ecologists, Inc. Robstown, Texas Phone: 512-387-3518
Disposal by landfill..
9. Wes Con, Inc. Twin Falls, Idaho (208-733-0897)
Receive packaged materials for disposal
in missile silos.
10. Gedcor Environmental Protection Corp. 1313 Newburgh Rd. Westland, Michigan 48185 Phone: 313-326-0600
Will accept transformers, capacitors and
PCBs solidified in Imbiber* beads,
APPENDIX B
ANALYTICAL PROCEDURES AND LABORATORY SERVICE
ORGANIZATIONS.
Bl. General
Analysis for PCB in environmental samples
is a tedious process due to the very low levels
(ppb or ppt) which are of interest and due to
the high sensitivity of the electron capture
chromatographic procedure. It cannot be over
emphasized that extreme care must be taken to
ensure first that the sample is representative
and second that sufficient numbers of blanks,
Dow Chemical Corp.
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and sample replicates are tested to define detectability limits and precision of the particular equipment and procedure being used. Cleanliness of sampling devices and contain*era and their extraction is also important. Analytical procedures for the determination of PCB# in air, water and sediments are given in section B3. B2. Laboratories
Por a listing of laboratories offering services for PCB analysis refer to Directory of Testing Laboratories publication STP333A available from the American Society for Test ing and Materials (ASTM) 1916 Race Street, Philadelphia, Pa. 19103. If an outside laboratory is used, a verification of capabil ity is recommended. B3. Analytical Procedures
DOMESTIC
NAME
MANUFACTURER
Askarel* Chlorextol Qorinol Clorphen Diaclor Dykanol Eleraex Eucarel Hyvol Xnerteen No-Flaraol Pyranol
Saf-T-Kuhl
Universal Mfg. Company Allis-Chalmers Sprague Electric JARD Company, Inc. Sangamo Electric Cornell Dubilier McGraw Edison
Electric Utilities Corp. Aerovox Westinghouse Electric Wagner Electric General Electric Kuhlman Electric
OFFSHORE
Clophen Fenclor Kennechlor Phenoclor DK Pyralene Pyroclor Solvol
Bayer (Germany) Caffaro (Italy) Kenneclor (Japan) Prodelec (France) Caffaro (Italy) Prodelec (Franca) Monsanto (UK) USSR
"World-Wide generic name used for insulating liquids in capacitors and tramsformers that usually contain PCB'a.
See ASTM D3304-74, "Analysis of Environ
APPENDIX D
mental Materials for Polychlorinated Biphenyls".
ENVIRONMENTAL PROTECTION AGENCY REGIONAL
OFFICES.
APPENDIX C TRADEMARK DESIGNATIONS USED BY MANUFACTUR
ERS FOR LIQUIDS CONTAINING PCBS. Capacitors or transformers in service and
liquid shipments showing the following trade mark designations contain PCBs. These have been or are in use and usually the designa tion appears on the nameplate or the warning label.
NAME
Aroclor Aroclor B Asbestol Askarel* Askarel*
DOMESTIC
MANUFACTURER
Monsanto Mallory American Corporation Hevi-Duty Corporation Ferranti-Packard Ltd.
Environmental Protection Agency Region I, Room 2303 John F. Kennedy Federal Building Boston, Massachusetts 02203 Telephone: 617-223-7265
Environmental Protection Agency Region II, Room 909 26 Federal Plaza New York, New York 10007 Telephone: 201-548-8730
Environmental Protection Agency Region II Curtis Bldg., 6th 6 Walnut Sts. Philadelphia, Pa. 19106 Telephone: 215-597-9898
Environmental Protection Agency Region IV 1421 Peachtree Street, N.E. Atlanta, Georgia 30909 Telephone: 404-526-5062
Environmental Protection Agency Region V 230 South Dearborn Street Chicago, Illinois 60604 Telephone: 312-896-7591
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Environmental Protection Agency Region VI, Suite 1000 160C Patterson Street Dallas, Texas 75201 Environmental Protection Agency Region VII 1705 Baltimore Avenue Kansas City, Missouri 64108 Telephone: 816-374-3778 Environmental Protection Agency Region VIII, Suite 900 1860 Lincoln Street Denver, Colorado 80208 Telepnonei 303-837-3880 Environmental Protection Agency Region IX 100 California Street San Francisco, California 94111 Environmental Protection Agency Region X 1200 Sixth Avenue Seattle, Washington 98101 Telephone: 206-442-1263
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