Document nN98kDgkxqpRz0o2p6VKE4d08
FILE NAME Brakes BRK
DATE 1973 Feb
DOC BRK042
DOCUMENT DESCRIPTION EPA Report - Control Techniques for Asbestos Air
Pollutants
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ENVIRONMENTAL PROTECTION AGENCY
Office of Air and Water Programs
Office of Air Quality Planning and Standards
:
Research Triangle Park North Carolina 27711
February 1973
of Documents U.S. Government Printing Office Washington D.C. 20402
For sale by the Superintendent
average of 3 pounds of asbestos per set.35 The yearly number of sets of replacement brake linings can be gauged by considering
that | trillion vehicle were traveled in
1968 in the United States and that an average lifetime for brake linings is 27.500 miles Further it is estimated that between one and two sets of containing clutch
facings are consumed during
the average vehicle equipped
clutch
the lifetime of with a manual
Figure 3-29 Dust capture device fitted to portable drill.33 Courtesy of Manville
readily supplied by an industrial vacuum cleaning system The prompt cleanup of trimmed wastes broken material fragments and spillage from containers minimizes further disintegration airborne entrainment and creation of secondary emission sources such as dispersion from workers clothing Tightly sealing waste containers should be conveniently accessible vacuum cleaning
devices are recommended for the removal of
The principal types of asbestos containing
friction products are molded woven or
extruded Chrysotile asbestos 30 to 60
percent of product is mixed or asbestos
cloth is impregnated with asphalt drying oil
synthetic resin or rubber Chrysotile is
preferred over crocidolite because of better
resistance and heat metal surfaces
less severe wear against
Friction materials materials containing asbestos are
also used in the pads of disk brakes for clutch
facings in automatic transmissions and for
small particles and dust In the absence of
brake blocks for heavy trucks
Se
vacuum cleaners the watering of wastes prior
moving equipment elevators and other
mn
to sweeping and shoveling can be an effective
industrial applications The percentage of
gn control measure The disposal of
domestically produced motor vehicles
tiem
rte
containing wastes is discussed in
equipped with disk brakes has increased from
Ramee
weber
Section 3.5
2.9 percent in 1966 to 11.2 percent in
In an effort to control emissions from the
1968. Additional increases in the fraction
epntram opening and dumping of bags of asbestos
of vehicles equipped with disk brakes will
insulating cement or loose dry insulating
affect the types of operations carried out
materials and also from the subsequent
during replacement of motor vehicle brake
mixing of those materials with water to form
linings
a
a slurry it has been proposed that mixing
3.4.3.1 Emissions
take place within the shipping bag.34 Water is
injected into a polyethylene bag through a narrow sleeve and the contents are kneaded into a wet mixture prior to removal from the
During the
brake linings on
and trimming
replacement of drum motor vehicles the grinding
operations required for
container
3.4.3 Friction Products The automotive and heavy equipment
industries are the major users of asbestos
friction products.19 In 1968 new passenger
and commercial motor vehicles manufactured
individual fitting are potential emission
sources
assumed asbestos
of asbestos loss of 0.05 content to
fibers Based on an
percent of brake lining the atmosphere during
grinding and fitting asbestos emissions from
the fitting of brake linings were estimated to
total 190 tons in 1968.23 The analogous
in the United States accounted for 9,913,000
grinding operations that are performed in
sets of brake linings which contained an
friction product manufacturing plants are
3-48
known to yield asbestos physical form to those
associated with adverse
fibers of similar that have been
health effects.36
Since disk brake pads are not contour ground
as drum brake linings are the current trend to
disk brakes should reduce asbestos emissions
As brake linings and clutch facings rub against their mating bearing surfaces in the course of usage particles of the lining material are abraded These particles can be partially trapped in the housings of manual clutches and in brake drums the remainder
can be emitted directly into the atmosphere
The latter emissions are treated as a problem in mobile source air pollution control and are
outside the scope of this study
Because extremely high temperatures can
result from the sliding of brake linings and
clutch facings against the corresponding
mating surfaces the question arises as to
whether the asbestos that would otherwise be
contained in the particles released from the
friction materials has been thermally
degraded One set of tests of automobile bus
and truck drum brakes and clutches has
shown that except under conditions ofvery severe usage the majority of the freed
asbestos has been thermally degraded.36degrade.36 For
example most of these samples of released
material from automotive brakes contained
less than 1 percent asbestos as compared with
50 percent in formulation 36.
the This
original lining
residual amount
however is not inconsequential relative to air pollution control Further tests are needed to
evaluate emissions from type brakes
In the course of servicing and overhauling motor vehicle brakes and manual clutches the accumulated containing dust is frequently dislodged from drums and
housings by directing a compressed air jet against the deposits.37 Depending upon the
servicing location this results in airborne asbestos emissions either to the work space or
directly to the atmosphere
3.4.3.2 Control Techniques
Asbestos emissions accompanying the
grinding and trimming of replacement brake
installation linings at the site of
and fitting are
presently uncontrolled at most sites The
incorporation of volume velocity
capture hoods see Section 3.3.2 into
grinding equipment is feasible and can provide
an effective method for controlling these
emisions.18
emissions.18
The removal of asbestos dust from
brake drums and from housings of manual
clutches by the compressed method produces uncontrolled emissions The
dislodging and collection of this waste
material at the source by operating a brush
connected to an industrial vacuum cleaner as-
a volume velocity dust capturing and collecting device has been evaluated.37 evaluated.37
This control technique reduced personal exposure to fibers larger than 1 micrometer in
diameter by approximately 75 percent
3.5 DISPOSAL OF ASBESTOS WASTE MATERIALS
Potential waste materials containing
asbestos are produced during the mining and
milling of asbestos ores and in the
manufacture and use of containing
products The wastes ranges
form of asbestos in these from asbestos bound in
relatively large rock masses or in such manufactured products as asbestos
pipe and reinforced plastics to diameter readily dispersed asbestos fibers that are
removed by cleaning devices or are
produced in the milling of asbestos ores
In mining operations large quantities of asbestos ore are sometimes rejected at the
mine site because either the concentration or the form of dispersal of the asbestos renders
recovery uneconomical The lower limit for profitable recovery of chrysotile asbestos
from massive deposits of serpentine rock is a
concentration of approximately 3 percent
3-49