Document qgbGXwdE0VDvO5968N6M1XM5
FILE NAME Brakes BRK
DATE 1976
DOC BRK066
DOCUMENT DESCRIPTION Journal Article - Asbestos Exposure of Brake Repair
Workers in the US
THE MOUNT SUAI JOURNAL OF MEDICINE Vol 43. No. 3. June 1976 Printed in U.S.A.
Asbestos Exposuroef Brake Repair Workers in the
United States
WILLIAM V. LORIMER M.D. ARTHUR N. ROHL PH.D. ALBERT MILLER M.D. WILLIAM J. NICHOLSON PH.D. AND IRVING J. SELIKOFF M.D.
Introduction
At least 900,000 people in the United States are employed as auto mechanics
or garage workers 1 An unknown but large percentage of these workers regularly service brake linings Brake linings pose a potential hazard for asbestos exposure because they contain 33-73 asbestos 2-4 Jacko and Ducharme 2 have estimated that 70 million pounds of asbestos 32 million
Kg are worn away from brake linings each year in the United States Much of the asbestos worn away around -90 drops to the road or is emitted into
the atmosphere The wearing of asbestos linings is complex and for brief periods of time local
areas in the lining surface have temperatures exceeding 630 the tempera-
ture at which chrysotile asbestos loses the major portion of its water of hy- pe nt
See droxylation and loses its characteristic morphology The bulk temperature
OR
Ore
cannot exceed 350-400 for any length of time without decomposition of the Er
:
organic polymer binder material
PegS$ at)
Several investigators 2-4 have analyzed bulk brake dust for
Pag
chrysotile and have found weight percentages of between 0.3 2 to at most % 3 Lynch 4 reported percentages of 10 and 15 free fiber in two of
fifteen samples Most of the rest were below % Personal and background sampling of workers engaged in brake mainte-
nance work at the job site gives a more direct estimate of exposure
During brake servicing the wheel is removed and all loose dust is
RE removed from the drums and backplates Compressed air jets are usually used
Fig 1 In a city survey in the USA Castleman et al 5 found that 175 out of 220 establishments used this procedure Alternates include vacuuming
and wet brushing The brake lining itself may require grinding to remove irregularities or removal and replacement The new lining may require
OTE considerable manipulation to fit the brake beveling edges and punching
holes in the material for example As an alternative the brake shoe and lining
IESE From the Department of Community Medicine and the Department of Medicine Mount Sinai
School of Medicine of The City University of New York N. Y. 10029
* Presented at the XVIII International Congress on Occupational Health Brighton England
Ua
SaHee September 16 1975
This work was supported by New York City Health Research Council 2329 NIEHS Grant
oe
ES 00928 and NIH Research Training Fellowship National Heart and Lung Institute Grant HL
doe
sphomengs 03591 Dr. Lorimer and by The Ford Motor Company
peal
Requests for reprints should be sent to Dr. Willian Lorimer Environmental Sciences
ae Laboratory Mount Sinai School of Medicine of The City University of New York N. 10029 =
207
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208
WILLIAM V. LORIMER ET AL
2 etaronies nalts
FIG 1. Amuants.o worker cleaning brake drum with compressed air jet Note personal sampler on the right side of worker's chest
5,000,000 may be replaced as a unit
A number of studies have measured exposure in summarized in Table I.
such work and fiber counts reported are
of
In addition Boillat and Lob 8 reported values for various manipulations
the lining material including punching holes for rivets and grinding
Sampling interval is not given Fiber counts ranged from 0.3 to 29.2 fibers
four of the nine values were over 5 fibers
disease Asbestosis in brake liners has been recognized and
Asbestos
for
9 and instances of mesotheli-
compensated in Great Britain
many years
Boillat and Lob 8
in
workers have also been identified 10-12
oma
garage
who had performed lining
examined 39 vehicular maintenance workers
for about 2-2 hours a day for a mean of 8+ years They found two men
service
however provided no
who may have had mild cases of asbestosis The study
information as to the risk with longer exposures
Present Investigation
additional information on this subject we have in-
In order to provide
workers in
vestigated asbestos exposure among brake repair maintenance
in
New York City and have initiated a clinical survey of workers employed
the workshops studied
ASBESTOS EXPOSURE
Materials and methods Personal air samples were taken during lining maintenance work both
on automobiles and trucks These were peak samples taken over 2-10 minutes
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ASBESTOS EXPOSURE OF BRAKE REPAIR WORKERS
209
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Asbestos
Operation duLnp WA XIOA TON Saynig Asbestos
AUOP
Su np
auoz
FIOM
Auryeorg durnd snoy TABLE
Measuremnts TABLE ur
Measurements Measuremnts Brake Brake
py
Sampling
he
and
Knight and blowing dust VAL
side
90
blowing
mechanic mechanic employed employed 800 806 personal cpelrsoounadl sampling dsaumrpilinngg sampling 2
eun/szaqt 2
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GEg 450 60g gto 450 L8
mornigafternon
Re derBCP
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we s
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adjacent bay WOIS O17e}5
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210
WILLIAM V. LORIMER ET AL
during which the workers were performing certain tasks such as blowing dust
from drum brakes renewing used linings by grinding and beveling new
linings Background samples were also taken at varying distances and times
The standard techniques for filter processing and fiber counting which have
been adopted by the Occupational Safety and Health Administration of the
US Department of Labor were used 13 Samples of dust collected in
standard manner
the
were examined both by standard optical techniques fi-
bers > 5 and by electron microscopy to give m of air and the results
compared Bulk samples of brake dust were collected and analyzed by
electron microscopy One hundred fibers were sized in each
tive morphologic comparisons of the fibers with
sample Qualita-
ogy were made
standard chrysotile morphol-
Results
Fiber concentrations for personal and background samples during blowing
dust from drum brakes on automobiles are
show extensive
presented in Table II The values
variation but the values at 3-5 feet are by far the highest with
a mean of 15.9 fibers
Fiber concentrations for personal and background samples during renewing used linings by grinding truck brakes are presented in Table III The
mean
concentration for the personal sampler was 3.8 fibers Fiber concentrations
TABLE II
Personal Automobile Brake Service
Operation
Distance
Blowing dust out of drum brakes Blowing dust out of drum brakes Blowing dust out of drum brakes Blowing dust out of drum brakes Blowing dust out of drum brakes Blowing dust out of drum brakes Blowing dust out of drum brakes Blowing dust out of drum brakes Blowing dust out of drum brakes
3-5 ft 3-5 ft 3-5 ft 3-5 ft 5-10 5-10 5-10 10-20 ft 10-20 ft
Background Automobile Brake Service
Distance
Blowing dust out of drum brakes Blowing dust out of drum brakes Blowing dust out of drum brakes Blowing dust out of drum brakes Blowing dust out of drum brakes Blowing dust out of drum brakes
10 ft 20 ft 12 ft 50 ft 65 ft 75 ft
0 min 0 min 5 min 5 min 7 min 14 min
*
Only fibers longer than 5 ...were counted by phase microscopy at 400
ConcentrationConcentration
13.8 29.4
6.6 13.6 -
3.8 2.0 4.2 0.4 4.8
Concetraion
0.3 0.8 0.2 0.1 0.1 0.1
for persc
are giver
To de
chrysotil
contrast
are given determin
A mean 20 of
diffractio was giver alteratior
granular
~ technique
alteration silicate co
CLINICA
Materials
104 me examined
City All ;
and envir
ASBESTOS EXPOSURE OF BRAKE REPAIR WORKERS
TABLE III
Personal Samples Brake Service
Operation
Concentration fibers
Renewing used linings by grinding
2.7
Renewing used linings by grinding
7.0
Renewing used linings by grinding
2.2
Renewing used linings by grinding
4.1
Renewing used linings by grinding
5.0
Renewing used linings by grinding
4.7
Renewing used linings by grinding
5.6
Renewing used linings by grinding
1.7
Renewing used linings by grinding
2.5
Renewing used linings by grinding
2.0
Background Samples Brake Service
211
Operation
Background to grinding used linings Background to grinding used linings Background to grinding used linings Background to grinding used linings Background to grinding used linings
Distance
10 ft 10 ft 25 ft 25 ft 60 ft
Concentration
1.2 1.7 1.0 0.6 0.2
for personal and background samples during beveling new linings for trucks are given in Table IV The mean concentrations were 37.5 fibers
To determine the correlation between optical fiber counts and mass of chrysotile sections of filters collected as above were analyzed both by phase contrast optical microscopy and transmission electron microscopy The results are given in Table V. Ten samples of bulk brake dust were analyzed to
determine the percentage of short fibrils defined as 250-500 ^ ^ 750-3750 ^ A mean of 83 of all chrysotile fibers were in this category A mean of about 20 of the total mass of the ten samples was chrysotile by electron diffraction Throughout the examination by electron microscopy attention was given to the morphology of the fibers A majority of fibers showed little alteration in the typical chrysotile fiber see Figure 2 Some fibrous and granular particles when analyzed by electron microscope microprobe techniques had structural and chemical characteristics of fosterite a thermal ~ alteration product of chrysotile Fig 3 Amorphous material with magnesium silicate composition was also found along with the fibrous particles Fig 4
CLINICAL STUDY
Materials and methods
104 men members of a union of vehicular maintenance workers were examined in a preliminary study of maintenance workers in New York City All were volunteers The examination included a detailed occupational and environmental history medical history physical examination chest
F
er
TEPRos
Avies
om
s?hert
he Reh
ARTE
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Ly
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Sean
=
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autor^5 autor^5
Cprenrens makabukas
t sewmeager makabukas
212
WILLIAM V. LORIMER ET AL
TABLE IV
Personal Samples Brake Service
Operation
Concentration fibers
Beveling new linings Beveling new linings Beveling new linings Beveling new linings Beveling new linings
31.7 23.7 32.7 72.0 26.3-
Background Samples Brake Service
Operation
Background to beveling linings Background to beveling linings Background to beveling linings Background to beveling linings
Distance
8 ft
:
12 ft 12 ft 30 ft
Concentration
0.6 0.5 0.3 0.3
TABLE V
Automobile Lining Service
. Operation /
Light grinding of new linings before installation Grinding new linings before installation Blowing dust off drum with air jet Cleaning brake drum with hand brush Background to blowing out brake drum 10 feet away Background to blowing out brake drum 20 feet away
Background to blowing out brake drum 65 feet away
Comparison of Optical and
E. M. Fiber Counts
Optical Microscopy
fibers
4.8 2.7 0.4 3.6 0.3 0.8
.1
Electron
Microscopy
g
.
53.0
66.0
1.1
6.5
0.2
0.1
0.2
ray and pulmonary studies Three men were excluded from analysis because they had worked in a shop for less than 10 years Also excluded from analysis were nine men whose occupational history raised the possibility of
other asbestos exposure Two men were excluded because of known chest
disease The remaining 90 believed themselves to be healthy all either were currently working 84 or had retired because age 6
Occupational Categories
General mechanics
67
Body workers
7
Undercoaters
5
Lubrication
42
Painters
42
Miscellaneous other crafts
8/0
8/0
ERIN
ASBESTOSASBESTAOSSBESTOASBSESTOS EXPOSURE EXPOSUREEXPOSUERXEPOSURO E F OF BRAKE BRAKE BRAKE BRAKREPAIRREPAIR REPAIR
WORKERWSORKERS WORKERS WORKERSWORKERS
edrim
i eis
Arshuviiyt
LN
aaa
ee
her
yeh
Chrysotile
FIGFIG . 2. Chrysotile
1
Chrysotile Chrysotile Chrysotile fibers fibers fibers frofmrom
brakebrakberake
drum drum dust
aSTite
gt
ve
Abele
A
Aevtend
Aapiers pape
neipiomae
iecapineod FORE
SmRikiep Fab
pe
025 025025
Hen
FIG FIG 3. A foster foster te fiber fiber fiber from from brake brake brake
drum dust
i:
:
an a OS 2 PT RTI
VTE
LITT
EIT Te ee
i
re
eR
Rai ra
:
e fot
214
WILLIAM V. LORIMER ET AL
0.5 p
FIG 4. Amorphous material mixed with chrysotile fibers from brake dust
Sixty of the seven general mechanics did brake lining more than
once a week for ten years or more The workers had a mean age of 48 -12
with 28 -8 years on the job
years
Results
Clinical examination Findings on pulmonary examination were minimal
There were five cases of clubbing and four instances in which fine rales were
heard
Pulmonary function Standard spirometry was performed on a Systems Research Laboratory screener The measurements used were FVC predicted FEV1 and as a more sensitive measure of obstruction in
airways the FEF25 ratio FEF25 is the forced expiratory flow rateswmiatlhl
25 of the vital capacity remaining to be expired The results were classified into either restrictive obstructive combined or normal according to the schema given in Table VI the results are detailed in Table VII 29 had decreased vital capacity the percentage increasing with age and most markedly after 20 years from onset on auto work Table VIII The differences are statistically significant .05 > p > .02
Effect of smoking Significantly more smokers and smokers than
smokers were obstructed Table IX X= 8.48.01 8.48.01 > p > .001 See note
at end of the Table There was no significant difference however
smokers smokers and smokers with
among
not significant
respect to restriction X= .01
FVC FVC FVC
*
Note
Pulmor
Restri
/
restr
and cor N
For be
Relati
No Ob Re Co. Tc For res For obs Those ;
ASBESTOS EXPOSURE OF BRAKE REPAIR WORKERS
215 215 215
TABLE VI
Classification of Pulmonary in Function Vehicular Maintenance Workers
FEV1 75
FEF
FVC .30
FEF
FVC < .30
.59 < FVC
FVC pred .80 FVC pred = .79 FVC pred ./69
Normal Restrictive Restrictive
Obstructive
Combined
Combined
Obstructive
Combined
Combined
Obstructive Obstructive
Combined
* Note all those with FEV1 < .75 also had FEF2 < .30
TABLE VII
Pulmonary Function Abnormalities in 87 Vehicular Maintenance Workers with over 10 Years
Experience
Number
Percent
Restrictive Obstructive Combined
Any abnormalities
14
165
32
375
11
13
57
66
TABLE VIII
Restriction of Pulmonary Function by Year of Onset of Work in 90 Vehicular Maintenance
Workers
.
Abnormal
Total
Before 1946
i
restrictive
1956-65
1946-55
and combined Yes No Yes No Yes No
25
1
15
14
28
10
19
%
33
34
For before 1956 compared with 1956 and after X = 4.84 .05 > p > .02
TABLE IX
Relationship between Obstruction or Restriction and Smoking in Vehicular Maintenance
Workers
Normal
Normal
Obstructive
Restrictive
Combined
Total
Subjects
31 31 14 11 87
Smokers
7
25353 25353
25353 25353 25353
Never Smoked 13 5
25
Smokers
8 11
5
5
29
For restriction X=== .01 N.S. smokers and smokers compared with never smoked
For obstruction X= 8.28 .01 > p > .001
Those in the combined group counted as being both obstructive and restrictive
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216
WILLIAM V. LORIMER ET AL
The relationship between pulmonary function signs of restriction and abnormal rays was investigated No significant association was found Table
X
Chest ray The chest rays were read twice by consensus reading using at least three experienced readers and categorized according to the ILO
classification An ray was read as abnormal if fine or moderately thin irregular linear opacities were present s or t t 1/0 and pleural thickening was present a or more The prevalence of abnormal readings is given in Table XI Parenchymal abnormalities were present in 19 instances nine 1/0 six 1/1 two 1/2 and two 2/2 ray findings consistent with asbestosis
increased with time such a trend is evident in Table XII This trend is
statistically significant
o
cane
TABLE X
Relationship between Ray Reading and Pulmonary Function Tests in 87 Vehicular
Maintenance Workers
Pulmonary function
Number of Subjects
ray reading
Percent
Restriction
25
Abnormal 5
20
Pery Obstruction
Normal
20
80
43
Abnormal 15
35
Normal
Normal
28
65
30
Abnormal 8
27
Normal
22
73
*
parenchymal fibrosis and pleural thickening
For overall pattern X= 1.78 .50 > > .30
For restriction alone X== 1.21 .30 > > .20 For obstruction alone X= 1.50 .30 > p > .20 For obstruction and restriction compared to normal X= .08
.80 > p > .70
TABLE XI
tk Ray Changes in 90 Vehicular Maintenance Workers with over 10 Years Experience
Number
Percent
Parenchymal fibrosis
Pleural thickening or calcification Both parenchymal and pleural changes Any changes
18
20
5
:
%
1
%
24
27
kgoetr,
TABLE XII
te
Ray of Vehicular Maintenance Workers by Year of Onset of Work
Abnormal
1956-65
Yes
No
1946-55
Yes
No
Before 1946
Yes
No
3 14 10 33 14 16
%
23
47
*
Parenchymal fibrosis ILO s t 1/0 and pleural thickening Xfor before 1956 compared with 1956 and after X= 5.95 .02 > > .01
The an and eve hundreds in brake these ope
weighted peak val
Much
granular
Detailed
reported optical f
intact ch exposure
Many
asbestosi results w
expected
Measu
brake re
averages fifths of
0.4 in 1
group of of ray restrictiv limited i therefore United S among su instituted
We are i Automobile cooperation
We wish son and D wish to exp Warshaw in Mrs. Diane
ASBESTOS EXPOSURE OF BRAKE REPAIR WORKERS
217 217 217
Discussion
The amount of asbestos brake material worn away each year is enormous
and even if only a small percentage is morphologically unaltered then hundreds of thousands of kilograms remain Fiber counts in various operations in brake maintenance work show wide variations Certainly they indicate that these operations need more systematic evaluation both as to peak and timeweighted values Peak values frequently exceed the 10 fiber legal limit for peak values in the United States
Much of the chrysotile is altered to other phases which may be fibrous or granular The biologic activity of these materials has not been studied Detailed classification and quantification of these changes has not been reported However even the incomplete correlations presented above between optical fiber counts and electron microscopic volumes of morphologically intact chrysotile is evidence that fiber counts are useful measures of asbestos
exposure in brake repair work Many of the vehicular maintenance workers examined showed signs of
asbestosis The prevalence both of chest ray changes and restrictive function results was significantly higher after 20 years of exposure than before a result expected after occupational exposure to asbestos 14 15
Summary and Conclusion
Measurements were made by optical microscopy of asbestos levels during brake repair and maintenance work in New York City Both weighted averages and peak levels showed significant asbestos exposure Over fourfifths of the total number of chrysotile fibers in brake dust were below 0.4 in length and not visible by optical microscopy Over quarter of a group of experienced vehicular maintenance workers examined had evidence of ray abnormalities consistent with asbestosis quarter also had restrictive pulmonary function test findings While this preliminary study was limited in scope and was restricted to volunteers and its results cannot therefore readily be generalized to all brake maintenance workers in the United States the findings suggest that asbestos disease will be present among such workers and that appropriate control measures should be urgently
instituted
Acknowledgments
We are indebted to the United Automobile Workers Local 259 New York City and to the Automobile Dealers Industrial Relations Association of New York City for their valuable
cooperation in the conduct of the field studies in this research
We wish to acknowledge the assistance of Dr. Ruth Lilis Dr. Susan Daum Dr. Henry Anderson and Dr. S. Alf Fischbein for their cooperation in the clinical and radiologic studies We also wish to express our appreciation for the valuable assistance of Ann Teitelbaum and Raphael Warshaw in cur laboratory studies and to Mrs. Frances Perez Mrs. Marcia Lorimer R.N. and Mrs. Diane Monahan in our field investigations
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218
WILLIAM V. LORIMER ET AL
References
1. Department of Commerce Bureau of Census 1972 Census of Manufacturers 1972 County Business Patterns Census of Population 1970 Occupation by Industry adapted by J. William Lloyd
2. Jacko M. G. and DuCharme R. T Brake Emissions Emission Measurements from Brake
and Clutch Linings from Selected Mobile Sources EPA Report 68-04-0020 1973 3. Hickish D. E. and Knight K. L Exposure to Asbestos during Brake Maintenance Ann
Occup Hyg 17-21 1970
4. Lynch J. R Brake Lining Decomposition Products J Air Pollution Cont Ass 824-826
1968
5. Castleman B. Camarota L. A. Fritsch A. J. Mazzocchi S. and Crawley R. G The Hazards of Asbestos for Brake Mechanics Public Health Reports Vol 90 No. 254-256 1975
6. Hatch D Possible Alternatives to Asbestos as a Friction Material Ann Occup Hyg 35-29
1970
7. Knight K. L. and Hickish D. E Investigations and Alternative Forms of Control for Dust
Generated during the Cleaning of Brake Assemblies and Drums Ann Occup Hyg 36-39 1970
8. Boillat M. A. and Lob M Risk of Asbestosis in Workers Employed in Replacing Automobile Brake Linings Schweiz Med Wschr 103 1354-1359 1973
9. McVittie J. C Asbestosis in Great Britain Ann NY Acad Sci 128-138 1965 10. Newhouse M. L. and Thompson H Mesothelioma of Pleura and Peritoneum following
Exposure to Asbestos in the London Area Brit J Ind Med 261-269 1965
11. McDonald A. D. Harper A. El Attar O. A. and McDonald J. C Epidemiology of Primary
Malignant Mesothelial Tumors in Canada Cancer 914-19 1970 12. Greenberg M. and Lloyd Davies T. A Mesothelioma Register 1967-1968 Brit J Ind Med
91-104 1974
Asbestos 13. National Institute for Occupational Ocupational Safety and Health Occupational Exposure to .
1972
:
14. Bader M. E. Bader R. A. Teirstein A. S. Miller A. and Selikoff I. .: Pulmonary
Function and Radiographic Changes in 598 Workers with Varying Duration of
Exposure to Asbestos Mount Sinai J Med 492-500 1970
15. Selikoff I. J. Churg J. and Hammond E. .: The Occurrence of Asbestosis among
Insulation Workers in the United States Ann NY Acad Sci 139
1515985
Received for publication January 23 1976
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