Document 2R9EQqmZq2BQJJ4xGBJ0D9aRg
1 July, 1969
Mx' } It Lyneh
Department of Hoalth, Kdocation and Wolfarc
Public Health Servieo 10.X4 Broadway
Cincinnati Ohio 45208
Doav Mv Lynch,
Thank you for your letter of June 13,J969, and for tho oopy of your Paper entitlod 'Drake Lining Decomposition Products',
Tho last aontenco in my summary of your oonoluslcmo was taken from the draft report which yon coni no in January,
1968, hut 1 aeo that your views have now ohangod, : X BUggost, therofore, that tho final part of my roferonoo
to your work should road as followot "At lower hulk lining teirQ>oratures within tho normal operating rango, tho hinder bohind tho surfioe remains intaot, However, tho epot temperature at tho point of oontaot botween tho
.lining and tho drum may bo hlghor than tho decotnpofcltion temporature of aoboatoa* Tho decomposition product, thereforo, inoludoa not free asbestos flbros but a different
minoral, resulting from thermal metamorphosis#*
X hope that this roforonco to your work is now aoooptablo to yon and unless 1 hoax* from yon to tho oontrary 1 will publish it in this foia
Tours sinoerely,
D K Hloklsh .Tndustx'lal Hygiene 8pseiall/t
8850
1/16# B006 1200
. PRODUCED BY FORD SCF-FORD-0600
li tI
BRAKE LINING DECCiPOSITION PRODUCTS
BY Jeremiah R. Lynch
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-Occupational Health Program ' 1014 Brri.adv.-ay
Cincinnati, Ohio 45202
U. S. DEPARTMENT' OF HEALTH, EDUCATION-, AND WELTARE
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Public Health Service
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National Center for Urban and. Industrial.Health
Occupational Health Prograta
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Presented at the Engineers Round Table Thirtieth Anpual"KefctJ.ns^T ~
American Conference of <j>vifrnmentP.l Industrial Kygffcnists
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St. Louis, Missouri, May 12-, 1968
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. . . ' brake liniks decomposition- products
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ABSTRACT ' `
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. A number of Investigates have found asbestos bodies In the lungs
of urban residents who were not occupationally exposed to asbestos. A
relationship between the carcinogenic properties of asbestos and the urban
excess of lung cancer has been suggested. The decomposition products of
brake linings have been described as a possible source of these fibers.
Brake testing laboratory methods were used to test fiber emission from
a variety of friction products. Only a very small fraction of the asbestos
escaped as free fiber while,the remainder was transformed Into some other,
non-fibrous, mineral. A significant release of free fiber occurred only
under conditions extreme enough,to produce b^ak^ failure.
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BRAKE LINING DECOMPOSITION PRODUCTS
^ Jeremiah R. Lynch*
Introduction
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" The-occurrence of coated fibers referred to as "asbestos bodies"
In the lungs of urban populations not occupationally exposed to asbestos
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has been noted by several Investigators. The results of several autopsy
series, as sunnnarlzed by Cooper, ^ are shown In Table i.
Thomson, ^
in suggesting possible modes of exposure that could account for these
bodies, stated "The average private'EStor vehicle wears out three or
four sets of brake linings and one or two clutch linings In Its lifetime,
and commercial and public transport vehicles wear out many more. These
linings consist largely of csbestos which Is ground to dust as the ling9.
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wear, and most wear occurs in built-up areas. This alone in most cities
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would Involve the discharge of many tons of asbestos dust and fibers in
the streets each year." Since asbestos has been Implicated as a carcinogen^and lung cancer has a higher incidenceamong urban populations, the fate of the asbestos v?6rn from brake linings becomes significant.
*0. S. Department of Health, Education, and Welfare .
Public Health Service
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Bureau of-Disease Prevention and Environmental Control
/National Center for Urban and Industrial Health
Occupational Health Program
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1014 Broadway, Cincinnati, Ohio 45202
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JHK0Q7911
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' . Table 1
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. Asbestos Bodies in Human Lunes'
*
' Location
Cape Tovn (2)
Miami (2).
Pittsburgh (3)
Johannesburg (A)
Finland (5)
Montreal (6)
.
San Francisco (1)
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1963 1965 1965 1965 1966 1966 1966
X Positive 26 27 41 39 58 48 42
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Brake Lining Composition
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The average coraposicion of typical brake linings of the type
tested IS-shown In Table 2. Individual nixes may vary considerably
from these averages.
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Table 2
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Brake Lining Composition
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Ingredient
Asbestos Resins and Polymers Oxides and pigments Metals Carbon, graphite, etc.
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Automobile
55 28
9 3 5 1007.
Truck
. 33 48 16 2 1
1007.
Each of these ingredients performs a'particular' function. The
asbestos provides strength, heat resistance and selective decomposition
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under stress. The resins and polymers hold the other Ingredients together.
Various oxides are added as pigments and to improve the grip of the lining
on the drum. Soft metals such as lead and brass improve wear while carbon
and graphite serve as friction modifiers.
Brake lining quality depends to a large extent on the type of binder
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used. . Linseed oil, which begins to-decompose at about 450 F-, Is used for.
light service brakes. More 'demanding service requires brakes made from
ca'shew' type resins or oil modified, phenolic resin's 1 ;Thesc ingred!ents'- are _
mixed, either dry or with a solvent added,' formed, into- shape and cured'
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in an oven. The hardened lining Is chen cut, ground and sanded to the
precise dimensions of the finished linings. ' The dust produced by the
abrading operations in asbestos friction product factories (Figure 1)
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contains free asbestos fibers thap are similar to Chose In industries
`< where cancer is known to be in excess (10). The question to be resolved,
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therefore, is whether the dust produced by the normal wear of brake
linings contains this same type of free asbestos fiber.
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Test Methods
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In an initial exploratory survey, the dust obtained from Inside automobile brake drums removed for brake relining was examined by electron
micrograph. Figure 2, which is typical of the series, does not reveal
any free fibers. However, this finding did not eliminate the possibility
that free asbestos fibers were released and that they had escaped into
the atmosphere. To examine this hypothesis a series of experiments as
devised to permit sampling decomposition products of the .lining undjr
simulated operating conditions. The tests (Table 3).were performed with
the. brake testing machines in the laboratory of a major brake lining
manufacturer. Most of the tests were performed on a friction-tcstir.g
machine which used one-inch-square samples of the test lining. Heating
and cooling apparatus permitted control of drum temperature from those..
encountered with Intermittent brake use to the maximum temperature which .
.occurred only in'extremely rapid or.Vpariic" stops from high spee<f. ; .
Other tests were performed on a brake-testing dynamometer which subjected
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a complete brake assembly to'a.series o stops and starts from different
speeds and at different deceleration rates to simulate actual driving
conditions. In these tests the drum temperatures varied according to the
driving condition simulated. During each run at a test condition, a
-sample was 'collected on an 0.8 ji pore size membrane filter. Electron
- micrographs of these' filters were examined to determine the presence
of free asbestos fibers and to quantify these fibers when more than a
few occurred.
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* . Table 3
Teat Results by Electron Micrograph
Produc t
Brand
1. Automobile
A
drum brakes
2. n
B
3. tf
C
4. * ifi
C
5. . D French
Test ' Method Friction
Friction Friction Friction Friction
No. of Samples
1 6
1 1,6
Conditions Presence of of Test-F Free Fibers
300-800
Few
250-800
None
5 300-700
Few
1
700-900
Numerous
5 300-800
Few
I Free Fiber*
<1
6 <1 '---10 <1
6.
E
Friction '
5
300-700
Few
7.
F Friction
5 300-800
Few
German
8.
C Fricticn
2 . 100-500
Few
9. * 10.
M ft
C Friction H Friction
1
600-700
Numerous
2 100-600
Few
<1 <1
<1 w-15
<1
11. Automobile clutch
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12. Automobile ' disk brake
K
13. Bus drum breke
L
14. M
15. Truck drum ; f' brake (light)
Dynamometer
Dynamometer
- Dynamometer
Friction Friction" '
1 1 1 2 ' io'
norasl driving
normal driving
city driving
450-550
; ;-300-80CV ]
None
0
Few
<5
None
0
None - FetT
0 : .y
^Height estimated from fiber volume. -
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Results
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The object of the tests vij to determine what proportion of the
asbestos known to be present In the lining appeared as free fiber In the
decomposition product.* No attempt was made at a mass balance between the
material worn from the lining andjthe decomposition product since It was not possible to collect all of tile decomposition product. However, the
percentages obtained in the fraction of decomposition product examined
are applicable to the total material worn from the brake and may be
compared to the percentage of esbestos originally present. In all but a few tests the automobile drum brake linings showed
less than IT-free. fiber In the decomposition product as compared to about
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50% in the lining. An election micrograph of the decomposition product
obtained from a typical test In this group Is shown In Figure 3. In those
tests where e significant mass of free fiber was released (Flgure*4), the
temperature was in an extremely high range for the lining in question as evidenced by rapid drop in the coefficient of friction. Had these linings
been subjected to like conditions in a vehicle, the brakes would'have
failed.
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Similar rcsults'werc obtained In the bus and truck drum braka tests
and in the clutch test. The experimental model disk brake tested did
releese some 0>57.) free fibers, but no conclusion can;be dpawn freti.s -
single sample. . ' " ~\
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Discussion ---------------- --
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Except In all but the most extreme driving conditions, only a
very small fraction of the 30 to 50% asbestos present .in a brake lining
escapes into the atmosphere as free fiber. The question remains: What happened to the asbestos? A prevalent theory of brake operation holds
that wear occurs not by abrasion of1 the ling by the drum but by the
production of minute areas of intense heat at the points of contact
between the di-uro and the lining. Decomposition, not only of the binder
but of the asbestos as well, occurs at these locations since the break
down temperature of asbestos-, about 90(1 F. is exceeded.. The decomposition
products will thus include not free asbestos fibers,- but a different
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mineral resulting from the thermal metamorphosis of the' asbestos.
Some .independent experiments done at a brake lining- research
laboratory^*^ have shown that all of the magnesium present in the .
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chrysotile asbestos orgir.ally in the lining can be accounted for in the
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decomposition products. However, the characteristic X-ray diffraction
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pattern of chrysotile asbestos had vanished. Thus, it is apparent- that
under conditions in which asbestos is worn from the lining of a brake,
the asbestos is destroyed.'
Conclusion
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Only a very smell proportion of the asbestos worn from breke
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-. linings is released as free.fiber; the'remainder is converted into"so'me.-
other mineral as a result of the extreme temperatures generated at small ...
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spots on the lining surface. Thus, although urban aJLr-. contains a-few
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free fibers as a result of brake lining wear, they represent a very '
small, proportion of . the total asbestos used in the manufacture of
brakes. Hany sources of respirable fibers not associated with
asbestos products have been Identified,
and the free fibers
from brake lining wear appear to be an inconsequential health facto' . I.
in urban air pollution.
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' References
1. Cooper, W. C.: Asbestos as a Hazard to Health. Arch, of Env. Health.
15:285 (19671.
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2. Thomson, J. G., R. 0. C. Kaschula and R. R. McDonald: Asbestos Is as a Modern Urban Hazard. S. Afr. Med. J. 37:77 (1963).
3. Cauna, D. R. S. Totten and P. Cross: Asbestos Bodies In Human
bungs at Autopsy. JAMA 192:37 (1965).
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4. Web6ter, I., In discussion of Thompson, S. F. : Physiological Effects
of D20 In Mammals, Ann. N. Y. Acad. Scl. 84:736 (I960).
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5. Meurman, L.: Asbestos Bodies end Pleural Plaques In a Finnish series of Autopsy Cases,.Acta Path Microbiol Scand Suppl 181:107 (1966).
6. Aryllrel, L. and V. Thiirlbeck: The Incidence of Asbestos Bodies In the
Lungs of Random Autopsies In Montreal, Canada. Med. Assoc. J. 95:1179
(1956).
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,7. Thomson, J. G.: Asbestos and the Urban Dweller. Ann. N. Y. Acad.
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..Scl. 132:196 (1965).
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8. Sellkoff, I. J., J. Churg and E. C. Hammond: Asbestos Exposure and
Neoplasia. JAMA 188:22 (1964).
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9. Buell, P. and J. E. Dunn: Relative Impact of Smoking and Air Pollution
on Lung Cancer. Arch, of Env. Health 15:291 (1967).
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10. Enterlinc, P. E. and M. A. Kendrick': Asbestos Dust Exposures at Various Levels and Mortality. Arch. Env. Health 15:181 (1967).
11. Sinclair, D.: Study of Wear Dust from Brake lining. Johns-Manvllie Research and Engineering Center, personal communication (1967).
12. Cralley, L. J., R. C. Keenan, J. R. Lynch and W. S. Lalnhart, M.D. :
Sources.' and Identification of Respirable Fibers'. Am. Indust. Hyg.
Assoc. J.'29:2 (1968).
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Figure l. Brake lining factory dust .
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Figure 2. Dust removed from brake drum:
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Figure 3. Decomposition product from normal yvear -
. of brake lining .
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. . Figure 4. Decomposition product from brake lining c at failure .
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COPY
Public Health Service - BSS
TO:
Asst, to Chief for Epidemiology and Field Studies, DOH
FROM: Engineering Section
SU3J: Report bn Brake Decomposition Tests
At the New-York Academy of Sciences Conference on the Bio logical Effects of Asbestos" It was stated: ll) "The average private motor vehicle' wears out three or four sets of brake linings and one or two clutch linings In Its lifetime, and
commercial and public transport vehicles wear out many more. These linings consist largely of asbestos which Is ground to
dust as the linings wear, and most wear occurs In built-up areas. This alone In most cities would Involve the discharge of many tons of asbestos dust and fibers in the streets each
year." This statement was meant to explain, In part, the presence of "asbestos bodies" observed In the lungs of non-
occupatlonally exposed residents of Cape Town, South Africa, and Miami, Florida.
To Investigate this possibility, a study of the mode of dis
integration of brake shoes under simulated operating conditions
was undertaken by using test facilities made available by the
American Brake Shoe Company laboratory at Kahwah, New Jersey.
These tests were made as part of the Division of Occupational
Health's overall epidemiological study of the asbestos
processing Industry.
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Automobile brakes are composed of from 30"50X asbestos (usu ally chrysotlle) held together with various resins and con taining such other Ingredients as carbon, brass filings and rubber. Theoretically, a brake wears by abrasion of the sur- . face by the drum and by thermal decomposition of the binder.
The question to be resolved was: What fraction, If any, of the asbestos Is liberated a3 free fiber In the wearing process undezj^yarlois operating conditions.
(1) Thomson, J.G.: Asbestos and the Urban Dweller, Annals of the New York Acad, of Science, VI32, Art. 1 (196-214),
Dec. 1965
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Asst, to Chief for Epidemiology and Pi eld Studies, DOH -- 4/8/66
At the Kahwah laboratory a number' of brake testing dynamom eters were available which could simulate various operating conditions. These machines were set to test a variety of typical brakes and air samplea of the decomposition products were taken on membrane filters. Electron micrographs were made of the deposits thus collected and a number of fields were scanned for the presence of fibers. Where significant numbers of fibers were found an estimate of the fraction of the decomposition product which was fiber was made by sizing all of the particles and fibers seen. The results of these tests are as follows:
Decomposition of Brake Linings
No. Type of Brake
Condition of Presence % Fiber
Test
of Fibers
(mass)
1 Disk Brake
Normal' driving Few
<5
2 Bus Brake
City driving
None
0
3 Automobile
100-200 P drum Few temperature
4 Automobile Brake 300-500 F drum temperature
*0 . <1
5 Automobile Brake 600-700 F drum Numerous temperature
15
6 Automobile Clutch Normal driving None
0
7 Bus Brake
**50-550 P drum None temperature
0
8 Automobile Brake 100-300 P drum None temperature
0
9
A.-Vu*Ttom.. -obile B' rake
400-600 P drum Few temperature
r'O
10 Bus- Brake
**50-550 F drum None temperature
0
One clump of fibers still largely coated with binder and having a roughly rectangular shape.
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-3Asst, to Chief for Epidemiology
and Field Studies, DOH -- 4/8/66 In only one case (No. 5) did the percentage of fiber approach the percentage of asbestos in the brake; and that was at a temperature of 600-700 F as compared with normal meiziDua operating temperatures for automobile brakes In the range of 550-600 F. It appears that when the design temperatuxe of a brake is exceeded., the binder decomposes and releases part of the asbestos as free fiber. At lower operating tempera tures the asbestos worn off the lining remains encapsulated In the binder and few free fibers occur. Thus, although urban air would undoubtedly-contain a few-free asbestos fibers as a resuit of disintegrating brake shoes, they would represent an extremely small percentage of the total asbestos used In the manufacture of brakes.
Jeremiah R. Lynch Senior Sanitary Engineer Engineering Section Research and Technical
Services Branch
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