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v . The Hazards o? Asbestos for Brake Mechanics
BARRV CASTLEMAN. LUCILLE A. CAMAROTA, ALBERT J. SUSAN MA2ZOCCHI, and ROBERT G. CRAWLEY
AsnESTOS is the generic name of a group of hydrated
magnesium silicate mineral fibcrj. There arc two
groups of these minerals--serpentine (chrysotile) and
amphibole (amositc, crocidolitc, anthophyllitc,
trcmblitc, and actinolitc).. Ninety-five percent of the
world's asbestos production is chrysotile.
Reports of epidemiologic and pathological studies
(1--4) reveal that occupational exposure to commercial
asbestos minerals enhances the likelihood of a number
of diseases--asbestosis and cancers of the lung, pleura,
peritoneum, larynx, and gastrointestinal tract. The
time from onset of exposure to the lime of clinically ap
parent disease is usually more than 20 years. Cancer
from asbestos is not limited to workers who handle the
material. There arc also reports of pleural and
peritoneal mesothelioma (tumors rarely seen in the
general population) in persons with family, or
neighborhood, or indirect occupational exposure to
asbestos (4--7).
.
Mesothelioma was the cause of death of a man who
had regularly sanded vinyl asbestos floor tile (S). Under
simulated conditions of this man's work, a maximum
asbestos dust concentration of 1.3 fibers per ml (fibers
longer than 5 microns) was found in air samples passed
through membrane filters worn by a person sanding
vinyl asbestos (S). The type of asbestos now used in
domestic floor tile is chrysotile--the same as that used
in brake friction 'materials, according to (lie Asbestos
Information Association. A ease of mesothelioma in a
brake mechanic has been reported (9). Ciommuieial fflcilun ntftief'liiU uwd In ih* United
States for braking passenger cars and trucks contain an
average composition of 50 percent chrysotile by weight
(10). Asbestos has been used for brake drum linings,
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disk pads, and clutch facings fob the past 50 years. Jacko and DuCharme (11) estimated that the United Stales annually uses 103 million pounds of asbestos for brake friction materials and 4.5 million pounds in automotive clutch friction materials.
In 1968 Lynch reported that because of the heat of friction caused by braking, almost all of the asbestos in brake linings is transformed to a nonfibrous mineral, and a small fraction of asbestos escapes as free fiber (12). Jacko and co-workers.determined that vehicles in this country emit 158,000 pounds of asbestos per year, of which 11.2 percent is retailed in the brake and dis posed of during service (13).
Brake mechanics have low and intermittent exposure to asbestos. This exposure has been reported to be 0.79 Tiber per ml time-weighted average (fibers longer than 5 microns), with peaks up to 7 fibers per ml when brake parts arc being cleaned (14). The standard method for removing dust from brake parts is to blow it out with a
CAfr. Castlcman, an environmental engineer, was with the Center for Science in the l\iblic Interest when this paper was prepared; he is now with the Maryland Public Interest Research Group. Dr. Frilsch is director of the Center fur Science in the Public Interest. Ms. Camarota is an occupational health nurse. District of Columbia Department of llumun Resources. Ms. Ma^'titihi was a research associate, Environmental Cancer Research Project, Environmental Sciences Laboratory, Mount Sinai Schno{ of Medicine, /lew Tork City. Mr. Crawley is a sanitarian, Italtimore County Department of Health.
Ttnnheet ui/u*ni to Parry Cattleman, Maryland Public Interest Research Group, Jl 10 New Main Dining Halt, University of Maryland, College Park, Aid. 20742.
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' comptfvsscd air hose. In 1970 several reports (//-- l{i) cirxcrihrd (lie levels of exposure of brake mechanics to asfjcxtox; alternative fiiclion materials, aiut specific changes in brake repair practices which would reduce the levels of exposure.
Baltimore and Washington Studies
In December 1972, the Baltimore County Department
of Health mailed a 1-pagc mimeographed circular to
about 130 establishments which provide brake repair
service. These businesses included new car and truck
dealerships, certified motor vehicle inspection stations,
and other concerns advertising brake repair as a
specialty. Some of the establishments initially con
. (acted had either gone out of business or replied that
. they do not do brake repairs. The circular warned that
inhalation of the dust from brake cleaning could cause
serious diseases, including cancer, and advised
vacuuming brakes of accumulated dust. Additional
measures suggested were improved ventilation and the
use of face masks (19). Two student volunteers went to
100 of the places on the'mailing list 4 months later to
ask shop managers what methods they were using in
brake repair.
A similar study was started in Washington, D.C., in
August 1973. This work was conducted by the Center
for Science in the Public Interest and the District of
Columbia Department of Human Resources. Of 186
brake service establishments initially contacted, 120
were followed up. Several new methods were tried in
order to improve the effectiveness of the warning. The
warning leaflet was more eye-catching and readable
than the paragraph-form sheet used in Baltimore; the
leaflets were handed out by an occupational health
' muse to the mechanics themselves--none were mailed;
and followup to ascertain the degree of effectiveness
was conducted by the same nurse who interviewed
the repair shop managers. The Washington study was
also featured in a local television program at the time
the leaflets were first handed out.
To assure that students trained in brake repair by
public vocational schools would learn proper methods,
health officials met with appropriate school officials in
both locations. At the time they were contacted, school officials in Baltimore and Washington reported that the
schools were teaching the'"blow out" method of brake
dust removal to the trainees.
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The standard method of cleaning brakbs is "blowing
out" with a compressed air hose. In Baltimore* 63 per
cent (65 per 100) of the brake repair establishments
contacted were using this method at the time they
received the warning circulars. In Washington, the
figure was 91 percent (110 of 120). Most'of the
managers and workers interviewed had never heard
/about the hazardous potential of brake dust. Predict
ably, the responses ranged from annoyance to apprecia
tion.
Of the 65 places in Baltimore initially blowing out
brakes, 11 were using either vacuum or wet brushing
methods at the time of followup. Four others were still
blowing out brakes, but had improved ventilation or
provided dust masks,, or both, to reduce workers' ex
posures.
In Washington, only two establishments had
changed to wet brushing, but none were vacuuming
brakes. Four others provided face masks. I-ntcrcsfingly,
two others decided to change brake shoes in all brake
repairs, thereby simplifying the problem of dust
removal and reducing the mechanics' exposures.
The degree of improvement, indexed by the percent-,
age of establishments converting from blowing out
brakes to safer techniques after a single warning, was
23 percent in Baltimore County and 7 percent in
Washington. This disparity probably arises more from
differences in the methods of the studies than from
differences in the study groups.
............
It may be critically important to approach manage
ment at the outset in order to enlist the cooperation
needed to implement any changes in practice. A
mechanic who is approached directly with a warning
may simply disregard it. The mechanic might reason
that if the dust were really dangerous, there would be a
law requiring the use of preferred methods in brake
repair. And the employer, if not asked to participate
from the beginning, may well conclude that he need not
be concerned with the matter. The failure to involve management may be the main reason why the Washington study produced less gratifying results than
the Baltimore study.
Brake warning programs consisting merely of mailed
warning notices require little manpower, compared to
other health programs. Also, the effort to implement
safe techniques in public vocational schools is time well
spent.
Conclusion
.*
Over a 7-ycar period ending in 1976 ( 20,31.1, the ITS.
standard for lime-averaged exposure to asbestos will
have been reduced from 5 million particles-pee-cubic
May-Jurw tors, VoL SO, No. 3 3SS
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foot of nir 10 ?. fibres ju'r ml {filn-ii l<m;;rr than S , yiicrfrtlis), I-\>r ifthcsios textile jil.wtis, (his mluitioii is ' ivl^ljit IfT-fold (22). ['resent twul scheduled standards
claim only to protect workers ni;nirist nshestosis, the I disease for which the dose-response relationship is most
quantitatively known. The British standards for chrysolite and nmositc asbestos, which tire comparable to the asbestos standard scheduled to take effect in the United States in 1976, do not purport to provide protec tion against increased risk of cancer (25,2!).
Previously studied cohorts of asbestos workers svere | exposed to time-averaged concentrations greater than 2
fibers per ml (fibers longer titan 5 microns). Current studies of cohorts with time-averaged exposure on the order of 1 fiber per ml (greater than 5 microns in length) may provide evidence of hazard at that level. In view of alarming preliminary findings of pulmonary fibrosis in such a cohort, the National Institute of Oc cupational Safety and Health has suggested to the j Department of Labor that consideration be given to / further lowering of the-asbestos standard (25).
The average brake mechanic is not aware of the potential hazard of ai; borne brake dust. Nor is he quick to change time-hardened habits when warned of dangers if he cannot feel their effects. Nonetheless, sub stantial reduction in asbestos exposures during brake repair can be achieved by simple ciianges in technique, with the use of equipment already -available in most brake service establishments.
In view of the tendency of the accumulating literature to reveal cancer induction from asbestos at progressive ly lower levels of exposure, mechanics should be ad vised not to blow out brake parts and to use instead methods which create less airborne dust. The manufac turers of automotive friction materials could easily at tach a clear hazard warning to every item sold.
The limited success of both the Baltimore and Washington studies shows the limited efficacy of volun tary compliance with health warnings--the shop managers and the mechanics simply do not have the same regard for a warning that they have for a rcgulalion. The margin of safety, if any, provided by the current asbestos standards has been sharply criticized as insufficient (26). While it is advisable that brake mechanics at least be warned of the potential hazard of their work, it is also apparent that blowing out.brakes will be a common practice so long as health regulations permit it.
Rtjttrnecs
; 7. Cooper, \V. C., cl At.: Asbestos--the need for nod feasibility of air
. pollution controls. National Academy of Sciences, Washington,
O.C., 1971. |
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2- SclikofT, l, J., Hammond, K. C., amt Clung, J.: Mortality ex* pericncci of asbestos insulation worker*. /* IVuercdinj;* of the Imernatimwil Conference on rneomocnninti.s, Johannesburg, 196V, edited by II. A. Shapiro. Oxford University iVess, Capetown, South Africa, J97u, pp. 180--186.
J. StelJ, l*. M., and McGill, *0: Asbestos and laryngeal carcinoma.
I .am el 2: -Ilf. - 117. ,\tn{ \l\ 19/3.
,
/. NewhooM', M. 1.., amt \ lininpson, II : Mronhehtmia ui the
pleura anti pit it mien in follow im exp* mii e to .isI^mos in the I .on*
don area, tor J 1ml Med 11, 261 -269 (196*).
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posufe. Arch Environ JJe.iIlh 1*1: 359-363 (1967).
(i. Warner, J. 0., Stn;i;s, A. and M.t/eh.uul, I*.: Diffuse pleural
mesothelioma and asbestos exposure m the North Western Cape
,
Province. UrJ Ind Med 17: 250-271 (196(1/., '
7. l).iUpirn, l\, Uabherl, A. K., and Hut/, 1.: Epidemiologic drr
Pkur.imesoihelium.v Vorlauligcr Herirht uber 11V Falle aus clem
Hamburger. Kaum I'rax l'ticuiimt 23; 347--53K (1900)
3*. Murphy, R. L., ct al.: floor tile installation as a source of
asLcxto* exposure. Am Uev Kespir Hi.* 101*. 576--580, October
1V71.
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9. Sullivan, R. J., and Athan.iydadis, V. C.: Preliminary air pollu-
a bon survey of asbestos. National Air Pollution Control Ad*
ministration, AI*TD 69--27. RMcighrN.G., 1769, p. .12.
10, Harwood, C.: A.sbesios air pollution from the wear of brake
lining*. Illinois Institute of Technology Research Institute.
Chicago, April 1972.
77. Jaeko. M.G., and DuC.harrnc, R.T.: llrakc emission** emission
measurements from brake and clutch lining* from selected mobile
source*. Environmental Protection Agency Report 68*04-0020.
Ann Arbor, 1773.
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12. Lynch, J.r [hake lining decomposition products. J Air Pollut
Control Assoc 18: 824-526 (1965).
7J. Jnrko, M. G., DuCharmc, R. T., and joiners, J. H.: Drake and
. clutch emissions during vehicle operation. Paper presented at `
Society of Automotive Engineers Meeting, Detroit, May-1973.
//. Uickish, D. E., and Knight, K. 1..: Exposure to asbestos during
brake maintenance. Ann Occup Hyg 13: 17--21 (1970).
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75. 7 latch, D.: Possible alternatives to asbestos as a friction materia). Ann Occup Hyg 13: 25--29 (1970).
16. Knight, K. L. and Hickish, U. i: investigations into alternative forms of control for dust generated during the cleaning of brake assemblies and drums. Ann Occup Hyg 13: 37--39 (1970).
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77. Lee, G. L.: Removing dusts from brake assemblies during vehicle
servicing--alternative cleaning methods. Ann Occup Hyg 13;
33-36 (1970).
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IS. Bentley, M. L.: Control of the uscuf asbestos-containing friction
materials. Ann'Occup! Hyg 13: 31--32 (1970).
19. U.S. Senate, Committee on Commerce: Toxic Substances Con-
irol Act of 1973. Hearings before the Environment Subcom-
miuee. Statement of U. Castlrman. 93d Cong. U-S. Government
Priming Office, Washington, U.C., 1973, pp. 1-17, 349--350.
20. Guenther, G. C.: Emergency standard for exposure to asbestos dust. Federal Register, vol. 36, No. 234, Dec. 7, 1971, pp.
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23207-23208. 21. Guenther, G. O.: Standard for exposure to asbestos dust. Federal
Register, vol. 37, No. Ilf), June 7, 1972, pp. 11318 -- 11322. 22. Lynch, J. R.t Ayer, H. E., and Johnson, D.*L.: The in-
" terrelationship of selected asbestos exposure indices. Am Ind Hyg Assoc J 12: 598-601 (1970).
21. Hygiene standard for dirysmile aslsesios dust. Ann Occup Hyg .11: 47-49 (1968).
21. Hygiene standards for airborne amositc asbestos dust. Ann Oc* cup Hyg 16: 1--5 (197.1).
25. Key, M. M.t Reopening of asbestos standard. Memorandum to J. Stentlcr, Assistant Secretary of Labor, Oecup.uiuua! Safety and Uealib Administration.Office of Tcchnieul Publications, National Institute for Occupational Safety ami Health, Rockville, Md., March 2H, 1974. ;
2fi Gcr, H.t and Boulmys, A-: Action on asl^cxtu*. N EnglJ Med 28S; 1317-1318, Dec. 2, 1971.
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