Document Z40gxKdMbO7NVz0kpQDJ0N6p8
FILE NAME Brakes BRK
DATE 1984
DOC BRK256
DOCUMENT DESCRIPTION US Gov Report - Investigations of Health Hazards in Brake Workers Exposed to Asbestos
AOU ETAL
PB83-220897
Information is our business
INVESTIGATION OF HEALTH HAZARDS IN BRAKE LINING REPAIR AND MAINTENANCE WORKERS OCCUPATIONALLY EXPOSED TO ASBESTOS
NIOSH
CINCINNATI OH
AUG 84
U.S. DEPARTMENT OF COMMERCE National Technical Information Service
PB83-220897
_
Investigation of Health Hazards in Brake Lining Repair and Maintenance Workers
Occupationally Exposed to Asbestos
NIOSH Contract 210-77-0119
Principal Investigator William J. Nicholson Ph.D.
S
(
ENVIRONMENTAL SCIENCES LABORATORY
MOUNT SINAI SCHOOL OF MEDICINE OF THE CITY UNIVERSITY OF NEW YORK
>
OOOO
REPRODUCED BY
U.S. DEPARTMENT OF COMMERCE
NATIONAL TECHNICAL INFORMATION SERVICE SPRINGFIELD VA 22161
Investigation of Health Hazards in Brake Lining
Repair and Maintenance Workers
Occupationally Exposed to Asbestos
Authors
William J. Nicholson Ph.D. Susan M. Daum M.D. William V. Lorimer M.D. Henry Velez M.D. Ruth Lilis M.D. Irving J. Selikoff M.D. Albert Miller M.D. Henry A. Anderson M.D. S. Alf Fischbein M.D. Edwin C. Holstein M.D. William N. Rom M.D. M.P.H. Kenneth D. Rosenman M.D. James D. Todaro M.D. Wei Cheng M.D. Veetai Li B.S. Diane Tarr B.A.
\
ENVIRONMENTAL SCIENCES LABORATORY
MOUNT SINAI SCHOOL OF MEDICINE OF THE CITY UNIVERSITY OF NEW YORK
/
=
PLerTsat ol REPORT DOCUMENTATION 1.
PAGE 4. Title and Subtitle
NO.
2
NA
Investigation of Health Hazards in Brake Lining Repair and Maintenance Workers Occupationally Exposed to Asbestos
7. Author
W.J. Nicholson
9. Performing Organization
Address
Name and
Mt. Sinai School of Medicine of the City University of New York
Sponsoring
12.
Sponsoring Organization
NIOSH
Name and
4676 Columbia Parkway Cincinnati Ohio 45226
15. SupplementNaorteys
1.
Recipient's
PB8 3
5. Report Date
No. 220897
6
NA
& Performing Organization Rept No.
10. Project Work Unit No.
NA
11. or No. Contr Gra anc t t
C
210-77-0119
G
13. Reop f o Repr ortt& Period Covered
14
NA
16. AbsLt imir t 2a 00 c wort ds
There are several sources of asbestos exposure to garage mechanics automobile repairmen First of course is that the asbestos exposure from the debris of brake or clutch lining wear particularly when the brake or clutch housing are cleaned using a high pressure air hose Second garage mechanics may be at risk from exposures during the use of autobody filler and finally asbestos dust can be disseminated during mixing and application of undercoating materials each of which has contained the fiber in previous years
In order to determine the extent of the asbestos risk from garage maintenance work NIOSH has contracted with the Environmental Sciences Laboratory to conduct a clinical
examination of garage mechanics The examination was to focus specifically upon those manifestations of asbestos disease such as ray abnormalities and pulmonary function deficits that would elucidate the possible effects from exposure to asbestos in garage employment
7. Decument Analysis a Descriptors asbestos brakes automotive respiratory
a identif Eni dedeTr ers ms
c COSATI Group
Availability Statement
AVAILABLE TO THE PUBLIC
239.18
18. Security Class This Report
UNCLASSIFIED
28. UNCLASSIFIED Page
Sae instructions on Reverse UNCLASSIFIE_D_
t
21. He of Pages
130 130
22. Price
OPTIONAL Formerly FORM 272 6-77
Deportment of Commerce
ACKNOWLEDGEMENTS
This study involved the cooperative effort of a large number of indivi-
duals of the Environmental Sciences Laboratory The clinical examina-
tions were under the direction of Susan M. Daun M.D. William V.
Lorimer M.D. and Henry Velez M.D Other examining physicians inclu-
ded Drs Henry A. Anderson Alf Fischbein Edwin C. Holstein Ruth
Lilis William V. Rom Kenneth D. Rosenman Irving J. Selikoff and
James D. Todaro
The pulmonary function laboratory was under the
direction of Dr. Albert Miller with assistance from Raphael Warshaw
Mark Geiger and Joann Haas Frances Perez Diane Monahan and Blanca Solano were the capable laboratory technicians rays were read by
Drs Daum Lilis Selikoff and nan Cheng The organization of the
data files and the preparation of the various analyses were performed
by Veetai Li and Diane Tarr Mary Bell Valerie Josephson Shirley Levine Veelai Li Amy Manowitz and Diane Tarr conducted the occupational history interviews Scheduling was the responsibility of Ernest Dobbs Selma Annenberg and Sidney Sibel typed this manuscript Without the close cooperation of all of the above this study would not
have been possible
uw
TABLE OF CONTENTS
Intro cccd ccu c cet eei eeo e en ee e wee ees eeeaene ane
n wwe eree
Materials and Methods A
a
re
Study population aes ecee ete e rene be eaeeee
Examination locations and protocols ea nc eens cheese
Results
2... ccc
cece
cee
nae ee eaee cane ce eneecutenreseecenees
;
Occupational histories aren see
eee
tween wenn
ray abnormalities ... ees. ceaen ren eee
Age standardization of ray readings
Smoking standardization of ray abnormalities
Standardized ray abnormalities by work activity
Autobody repair and undercoating ..... oe
Effect of previous shipyard employment
Evidence of malig cccn ccca reneen ernec st eny eees
Pulmonary function tests eee eeee Cee ee eee cee
Principal spirometric tests
cc
reece ee
eee ene nene
Measures of small airway flow ... cece ewer eee enn eens
Possible effects from mechanic garage equipment
Autobody repair ect ....... oeteerereeres sees
Correlations between ray abnormalities and
pulmonary function tests e ee Dar eesen re t ce
Comparison with other populations ee eeee
Physical examination result ees ccm eee en enc nee e ee
Laboratory findings ee cetee ee
Nickel concentration in welders er pace e ce r ns ts cecee
Asbestos exposure data
ccc
eee
ee
ere tere reese sees
Review of published res 0. ceu ce ceel ce eeet n eee es nonce
Measurements in New York City facilities
Estimates of study population exposure o-
Summary eee ete ences wee
e neces rr
are rr ar
References ee enerc cere rert e e eres ate
e
eee e eres
Appendix ... ccc ... ac near cette t ee estes e esse eeeeeees yee eee eee tee
1 2 2 5 12 12 17 26 28 29 36 38 41 41 41 46 52 59
33 33 65 74 74 86 86 90 93 93 97 100
ii
INTRODUCTION
Several investigations have indicated that significant asbestos exposure may occur during brake maintenance and repair work Nicholson 1979 Rohl et al 1976 Hickish and Knight 1970 Limited studies have suggested that exposure may be associated with the risk of asbesinduced disease including both pulmonary asbestosis and asbes associated cancer Lorimer et al 1976 Greenberg and Davies 1974 These limited reports do not however indicate whether the risk of associated disease is common or uncommon The question is
of importance because over one million workers are regularly or inter-
mittently engaged in vehicle maintenance work in the United States at this time Bureau of Labor Statistics 1979 Additionally a large number of other workers were formally engaged in such work in the past and now are either retired or employed otherwise It is estimated that
4,940,000 individuals are currently alive with such current or past
employment Nicholson et al 1982
There are several sources of asbestos exposure to garage mechanics and
automobile repairmen First of course is that the asbestos exposure from the debris of brake or clutch lining wear particularly when the
brake or clutch housing are cleaned using a high pressure air hose
Second garage mechanics may be at risk from exposures during the use of autobody filler and finally asbestos dust can be disseminated during mixing and application of undercoating materials each of which has contained the fiber in previous years
In order to determine the extent of the asbestos risk from garage maintenance work NIOSH has contracted with the Environmental
Sciences Laboratory to conduct a clinical examination of garage mechanics The examination was to focus specifically upon those manifestations of asbestos disease such as ray abnormalities and pulmonary function deficits that would elucidate the possible effects from
exposure to asbestos in garage employment
MATERIALS AND METHODS
STUDY POPULATION
The study population for this project consisted of members of the
following union groups who routinely performed brake maintenance repair
work
1.
*
Local 259 of
were employed
the United Automobile in commercial garages
Workers UAW whose members in New York New Jersey and
Connnecticut
Also included were all pensioners maintaining
vested rights in a program administered by the Local
2
Local 246 of the Service Employees International Union SEIU
employed in New York City municipal garages
The unexposed control population for the above brake workers consisted
of
1
Local 259 members and pensioners employed currently or previously
in parts warehouses New York City and amphibious vehicle con-
struction in Stamford Connecticut and Schenectady New York
2
District Council 37 DC 37 Municipal State and Federal Employees
Union members employed in New York City as motor vehicle operators
or traffic device repairmen
The above groups were selected prior to the beginning of the project as
the study and control groups for determining the effects of possible
asbestos exposure on workers engaged in brake maintenance and repair work The control groups were chosen because of membership in the same union and similar employment circumstances but without brake maintenance work As the study progressed it was found that many of the control population had had exposure to asbestos in other circumstances such as shipyard work and that fewer DC 37 members were participating in the examination than was initially expected Thus in consultation
with the project officer it was decided to add to the control groups the rays to be taken in examinations of Local 595 UAW members em-
ployed in production maintenance jobs in an automobile body
construction facility in Linden New Jersey These workers were to be
examined for effects of lead exposure associated with their work in an
examination April 7-10 1980. An analysis of their work activities had
indicated that their current employment provided only limited opportu-
nity for asbestos exposure
The decision to include this group was
made prior to the April examination
In order to reflect the effects of asbestos exposure only those in-
dividuals with ten years of employment in a particular trade were
considered for examination
In the case of the UAW members this con-
sisted of all individuals with ten years of union membership For SEIU members who were classified as mechanics in the New York City Civil Service Employees categorization five years of prior automobile maintenance work were required in order to obtain such a status Thus the criteria of five years of union membership identified individuals who had at least ten years of employment in garage work as a mechanic or
apprentice Table 1 lists the distribution by seniority date and union affiliation of all individuals who were invited and who participated in
the examinations
The response was limited by several circumstances
One was the dis-
tance many individuals had to travel in order to reach an examination
site For example both Local 259 and DC 37 Headquarters at which most
examinations were held are located in lower Manhattan whereas most
study participants lived in Brooklyn or Queens Many lived at even
greater distances in Westchester or Nassau County N.Y. or in New
Jersey Examination sites were arranged to accomodate as many of the
study population as possible but many individuals still lived at
considerable distance from a site Another factor was that most shops
organized by these unions are relatively small 79 of the population
workers in shops employing fewer than 30 members only sixth of
whom would have been employed for longer than ten years
259 9Tt < <zt
gee
garge garge invted 97
construction
invited invited invted LS Ste z
28
particpated maintenace invited particpated uy
sxzeak seay]
OZ
Ajpouas 315zauoT 20.0-29.9
197
197 pojyedia ATens 48ze
od 5
30.-9 pajypauy pazTWT Total 676 676
Total
sopueyom Percentage
Percntage T Retires 395
395 43. AQFOUS quowkTda @TauL Aq MVN
Percntage YUewoTds STOPFYSA- 15.9 jo
U7 ES
S
O<
26% ve
z6
(282)
97
T
82 69 ral
<
S SIT ey
15
ST
(9
(7S) T)
907
9<
UBY (
Od
SBT
02 OU vsoy
sem 10x
AQFZO 892
sem BY se AQZO YIP
NIGS |yQ-4q qof Jo 20 years
Becausof
particng years azoqun reflected
employedin syy
particpang Vsvays poypAury Ce" (6*ST) Jusao1 particpating Vo
employment
distributions distributions job
employment
for
|
7)
S
94 L6T 84
949
G6e
seniority seniority
syq
UP
sit s1z9M YQ
sTenpa,uy SUOTICPLRXS 6T-0OL 62-02 asequieg Ay
peqfyot Jo ct
SOAFI savozuoyunfiopuas >
6 viow
ase
6<-00<
120 YY
Teo]
qued.194
DY
Jo UE
osnvray joUoyQ air
The contact with individuals in these shops was by mail with letters from the Union President and Dr. Irving J. Selikoff of Mount Sinai
School of Medicine followed by a phone call from Mount Sinai personnel In the larger shops where the program was also described by the Union health and safety representative and attendance encouraged
greater participation resulted Finally only one examination was held
at each of the sites outside of Manhattan and those unable to attend on
a given day could only be accomodated at a clinic in New York City These factors led to a particularly low response of the 264 individuals
invited
cipated
to the examination versus 53.4 at the
site in Long Island where large shops of Condec
only
23.8 parti-
Information was obtained by phone and from the return mailer of the
reasons for participation
These are tabulated in Table 2.
It
also was found that of those sent invitations 2.1-5.3 were unde-
liverable by the post office
EXAMINATION LOCATIONS AND PROTOCOL
Examinations were held at approximately monthly intervals from May 1978
through February 1980 at a variety of sites chosen for their conven-
ience These
to the residence or employment included the union headquarters
location of Local
of the participants 259 UAW in New York
City and Schenectady New York the Community Center Stamford Con-
necticut the headquarters of DC 37 State County and Municipal Em-
ployees Union in New York City the Paterson Clinic Paterson New
Jersey the
Mount Sinai
Multiphasic Medical School of Medicine
Center Hempstead Long Island and
New York City
For those locations
without ray facilities portable units were obtained In each lo-
cation spirometry stations were established ment of the Pulmonary Function Laboratory
using field survey equip-
of Mount Sinai School of
Medicine Laboratory examining and interview stations
established in the available space in all facilities
were
easily
Appendix 1 is the form used for all examinations
The examinations
consisted of a complete occupational history with detailed descriptions
Table 2 .
Reasons given for participation
in examinations
Do not wish to participate
Not interested
Too busy at this time
Inconvenient time
Recent examination
Current illness injury or incapacitation
Illness or death in family
Too far to come or moved away
Miscellaneous health
reasons
:
Telephone
response
20
-
20 20
Mail response
175
5
of work activities that could affect the health of the individual descriptions of work practices during brake maintenance and repair work and the use of personal protection devices Special care was taken to elicit information on previous exposures to asbestos and other dusts that might be pneumoconiotic
The clinical examination tests and procedures consisted of
1.
complete medical history
2
current and past uses of medications
3.
o
4
5
current and past symptoms physical examination complete blood count including a
differential
count on
individ-
uals with an abnormal white cell count
6
20 channel blood chemistry analysis
7
pulmonary function tests including determination of complete
volume characteristics
8
14 17 inch full size anterior chest ray
All chest rays laboratory results and examination findings were reviewed immediately for conditions that might require urgent attention If such conditions were found the patient was notified and if
he wished his personal physician was called The radiographs were
subsequently interpreted using the ILO C International Classification
of Pneumoconioses
Parenchymal changes of 1/0 or greater were con-
sidered abnormal as were pleural thickening pleural plaques and pleu-
ral calcification Additionally other abnormal disease conditions were
noted See Appendix 2.
Predicted values for spirometry were based upon the revised analysis by
Miller et al 1980 of data of Morris Koski and Johnson 1971 The criteria for individual spirometric abnormalities are listed in Table
3 After interpretation of the rays and review of all laboratory and
clinical findings a report and letter were prepared and sent to each
participant
The two most important parameters for the assessment of
health effects from asbestos exposure are the manifestation of small
irregular opacities on an interpretable ray and restrictive pulmonary
Table 3
Criteria for normality of spirometry
FVC
FEV1
MMF
FEV1 FVC
> 80 of predicted
> 80 of predicted > 75 of predicted
age age age
29
30-59
60
.75 2.70 .65
FVC predicted
0.147 x Height in
0.025 x Age yr - 4.241
FEV predicted
0.094 x Height in
0.032 x Age yr - 1.426
For Blacks the predicted values were 89 of the above
MMF predicted 0.044 x Height in - 0.046 x Age yr + 2.806
For Blacks the same values were observed
From
Miller Thornton Smith and Morris Am J. Ind Med 55-68 1980
function deficits Of the 916 individuals from the four groups listed
above who participated in the examinations readable rays were available on 860 individuals and interpretable pulmonary function tests on 883. The 6.1 unsatisfactory rays stemmed from the use of portable
ray facilities that did not have processing facilities immediately available In one examination a light leak developed in the ray cassette holder that rendered 30 rays unreadable 24 from SEIU members and 6 from DC 37 members Because of the extensive travel in-
volved few with unreadable rays from the examination took advantage
of the availability of another ray at a later examination
The
distributions by union affiliation and work activity of participants
with valid rays and pulmonary function tests are shown below in
Tables 6 and 7
ray developing facilities were not available for films taken by the portable units and by two of the fixed installations used in this survey The unavailability of a film for review at the time it was taken led to a less than desired quality for the readable rays Both overand -penetrated films present difficulties in the interpretation of the minimal changes seen with low level asbestos exposure Thus a greater degree of inter- and observer variability exists with the interpretation of the films of this survey by the physicians reading
the rays than with films taken by the same technician with the same equipment and continuously monitored for quality
Following the completion of the examinations all rays from all
examinations were intermixed masked and identified with a coded
number
If multiple films of the same individual were taken these
were labeled with a single number and designated as A B C etc.
These films were read as group individually by three experienced
readers who were free to utilize the best P film for the determi-
nation of an ray reading
Results for the three readers and that of
the individual who read the rays following each examination were entered on a code sheet for each participant The results of the four
readings were then averaged using the following criteria
10
1 All parenchymal readings within given categories rounded irreg-
ular and combined were averaged utilizing the ILO U twelve
point scale
If the average came exactly half between two
values as is possible with an even number of readers the values
of the three readers who read the entire group of rays at one
time determined whether one averaged up or down
2
If the reading of one individual differed by three units from that
of the average of the others all readers read that particular
film The readers were told that a disagreement existed on par-
enchymal readings but no other information was provided If the
subsequent reading brought the outlying interpretation into closer
agreement the average of the second readings was utilized If a
disagreement of the same magnitude still persisted the ray was
interpreted by the entire group of readers and a consensus ob-
tained This occurred for fewer than five rays
3
If a disagreement existed among the readers as to whether or not
pleural changes existed such films were also read with the
specification that a disagreement existed with respect to in-
terpretation of the pleura Following a second interpretation a
determination was based upon the average of the second reading If
an ray was interpreted as normal by two individuals and abnormal
by two others the interpretations of the same three readers as
before determined the overall classification
Approximately 110 rays read early in the sequence were reintroduced into the group at a later time to provide information on reproducibility of the individual readers For this analysis no second readings
as described above were used Table 4 shows the distribution of dif-
ferences of parenchymal and pleural readings of each of the four read-
ers along with the average score of the parenchymal readings for each|
individual based on a 12 point scale As can be seen both the interobserver reproducibility and observer comparability of readers is well within similar variations determined by other interpretation groups Rossiter 1972 Glover Bevan Cotes et al 1980 See Table 12 for the results of individual and averaged readings by job category
11
Table 4
The variability and reproducibility of three
ray readers participating in this study
4 *
Reader 1.
2
3
Subcategory difference
Second reading - first reading
-3
-2
-1
0
1
2
3
0
4
13
93
1
82
1
0
Standard deviation 0.77
Average score First reading 2.40 Second reading 2.241
0
5
20
66
10
4
0
56
Average
Standard deviation 0.83
score First reading 2.67
Second
reading
2.55
3
8
13
63
14
5
0
57
Standard deviation 1.01
Average score First reading 2.51 Second reading 2.38
( ) = Number of films read as 0/0 both times
1
/ = 1 = etc.
12
OCCUPATIONAL HISTORIES
RESULTS
A careful review of all jobs each person held revealed that many examinations participants had previously been employed in a job with potential for significant asbestos exposure This is shown in Table 5 for each union group that participated in the examination or whose rays were utilized for analysis Overall 21.5 of the study participants
had an identified or highly probable exposure to asbestos in previous employment or military service The percentages were particularly high
in the groups that included men with skills as welders vehicle construction and city maintenance mechanics Here asbestos exposure in shipyards or during the welding and cutting of high temperature equipment insulated with asbestos was identified Of the 234 with identi-
fied or possible asbestos exposure and readable rays 87
rays were of men previously employed in shipyards
8.9 of all
In order to
eliminate any confounding exposure in the analysis of brake work the
health effects of individuals with identified and possible exposures to
asbestos and other dusts were analyzed separately according to the
four broad exposure categories of Table 5 direct occupational asbestos
exposure shipyard and heating trades possible asbestos exposure and
exposure to other dusts
In the direct occupational category were
those individuals that insulated pipes worked in asbestos manufactur-
ing operations or had similar exposures Among those classified in
shipyard or heating trades were those with any shipyard employment or
work that involved the repair installation or maintenance of boiler
room equipment or equivalent exposures
Also included in this cate-
gory were a group of men 12 that insulated mufflers with asbestos or
installed brake linings on continuous basis during the construction
of amphibious vehicles
An individual was classified in the category with the highest potential
asbestos exposure as ordered above irrespective of the total employ-
ment time in that category
It should be noted that while every care
was utilized in attempting to elicit a past asbestos exposure this may
13
Table 5
The distribution by union affiliation and
type of work activity,, of study participants
Type of work activity
No identified asbestos
exposure or garage work Garage employment
but no brake work
Brake work
Union affiliation
UAW 259
Maint
Const UAW 595
DC 37
14 3.9
70 55.6
85 69.1
28
28.9
82
2
-
23.0
1.6
18
18.6
217
2
-
61.0 1.6
18
18.6
Other dust exposure
7
2.0
3
2.4
18
14.6
1
1.0
Possible asbestos exposure
Shipyard heating trades
14
3.9
23
18.3
22
6.2
262 20.6
11
8.9
5
4.1
13
13.4
17
17.5
Direct asbestos exposure
-
insulation factory work
-
4
2
3.3
2.1
Totals
356
126
123
97
Totals with other possible asbestos exposure
36
10.1
372 29.4
20
16.3
32
33.0
SEIU 246 Totals
8
)2.4
22
6.5
205
124
213
63.2
450
7
2.1
22
6.5
61
18.1
4
1.2
36 83 131 10
337
1039
7
25.8
224
21.5
( ) = Percentage of union members in job category
1 Four men had missing occupational histories and These were excluded from further analysis
2 Ten of these 26 individuals insulated mufflers and 2 continuously
installed brakes during amphibious vehicle construction Their other asbestos exposure occurred as part of the job under study These were not included in totals other possible asbestos exposure In subsequent analysis however they were included in the category of shipyard heating trades
14
not have been successful in every instance due to inadequate recall of
the worker or because an asbestos exposure may have occurred without
his knowledge The large number of workers with identified exposures suggests the possible scope of the problem Such unidentified exposures would however contribute proportionately to the abnormalities found in both the exposed brake workers and unexposed groups under study In the analysis that follows workers will be classified according to their asbestos exposure irrespective of their union affiliation or job classification at recruitment
a
It is striking that 8.9 of all participants had previous employment in
the shipbuilding and ship repair industry As approximately 45 of the
study participants were over age 55 many had opportunity for employ-
ment in one of the several New York area shipyards that operated during
and after World War II Brooklyn Navy Yard the Hoboken yards of Todd
and Bethlehem Steel Approximately 4,500,000 men and women were
employed in ship construction and repair during World War II Nicholson Perkel and Selikoff 1982 This constituted 9.4 of the agricultural national male work force in 1943 but a much smaller percentage
was employed tics 1979
after World War II -0.5 Bureau of Labor StatisThus the finding of such a large number with shipyard
employment in this study is understandable and provides an opportunity to evaluate the effects of past short shipyard work as well as
that of garage employment
Tables 6 and 7 display the distributions by work activity of those for whom interpretable rays are available and for whom valid pulmonary function tests were obtained As can be seen lower percentages of readable rays were available for DC 37 and SEIU 246 members be-
cause of the previously mentioned loss of 30 rays The individuals
involved however were randomly scattered among the different exposure categories The percentage of individuals with valid pulmonary function tests 96.4 compares favorably with other surveys Again those
with missing tests are randomly distributed among all occupational
categories
15
Table 6
The distributions and percentages of readable rays by union affiliations and type of work activity
Type of work activity
Union affiliation
UAW 259
Maint
Const
UAW 595
DC 37
No identified asbestos exposure or garage work
14
100.0
67
95.7
85
100.0
25
100.0
Garage employment
but no brake work
81
2
98.8 100.0
-
14
77.8
Brake work
214
2
98.6 100.0
-
18
100.0
Other dust exposure
7
3
100.0 100.0
18
100.0
0
0.0
Possible asbestos exposure
14
100.0
21
91.3
11
9
100.0
81.8
Shipyard heating trades
22
26
100.0 100.0
5
100.0
13
76.5
Direct asbestos exposure
-
insulation factory work
-
4
100.0
1
50.0
Totals
352
98.8
121
96.0
123
100.0
80
87.0
SEIU 246
Totals
8
100.0
202
98.5
19
86.4
116
93.5
187
87.8
421
93.6
7
100.0
35
97.2
20
90.9
57
93.4
77
92.8
123
94.0
4
100.0
302
89.6
9
90.0
983
94.6
( ) = Percentage of category with readable ray
16
Table 7
The distribution of valid pulmonary function tests
by union affiliation and type of work activity,,
Type of work activity
Union
UAW 259
Maint
Const
affiliation
DC 37
SEIU
246
No identified asbestos exposure or garage work
Garage employment
but no brake work
13
92.9
80
97.6
69 98.6
2
100.0
25
89.2
18
100.0
8
100.0
22
100.0
Brake work
211
97.2
2
00.0
17
94.4
206
96.7
Other dust exposure
7
100.0
67.3
67.3
100.0
100.0
7
100.0
Possible asbestos exposure
14
100.0
23
100.0
11
100.0
20
90.9
Shipyard heating trades
21
95.5
262 100.0
17
100.0
56
91.8
Direct asbestos exposure
-
insulation factory work
-
J
4
50.0
100.0
Totals
346
97.2
124
98.4
89
96.7
323
95.8
Totals
115 95.8
122
98.4
436 96.9
17
94.4
68
97.1
120
95.2
5
83.3
883 96.4
( ) = Percentage of category with valid pulmonary function test
1 Two men with valid pulmonary function tests had missing occupational histories
2 No pulmonary function tests were performed at the Linden New Jersey examination of UAW 595 members
17
RAY ABNORMALITIES
Tables Sa and 8b list the averaged readings for the parenchymal ray
abnormalities according to the ILO C International Classification of
Pneumoconioses for the various asbestos groups established in
this survey Seven hundred and ninety of 983 readable rays were
classified as having 0/0 or 0/1 readings for parenchymal fibrosis One
hundred and seventy were classified in category 1 0-1 and
seven were classified as having 1-2 abnormalities
Of those with
normal pleura 735 of 871 84.5 were also normal for parenchymal
changes For those with abnormal pleura the percentage with normal
parenchyma was much less Only 64 of 113 56.6 of the readings were
categorized as 0/0 or 0/1
Tables 9a and 9b list the pleural abnormalities according to the se-
verity extent and thickness of pleural thickening and whether or not
calcification or pleural plaques were seen The greatest proportion of pleural abnormalities consisted of pleural thickening 89 of 113
Pleural calcification was seen only infrequently being identified on
only 12 rays including eight for which pleural thickening was also
noted Fleural plaques were seen on 38 rays including 16 for which
pleural thickening was also identified and one with pleural calci-
fication The degree of pleural abnormalities was relatively minor
Of those with and thickness
pleural A
thickening 42 had the lowest category of extent
Twenty were categorized as either A or
1
The more severe examples of pleural thickening were largely
confined to individuals who had either direct asbestos exposure or had
previously been employed in shipyards
Tables 10 and 11 list the percentages in the different occupational categories according to the type of ray abnormality As can be seen from Table 11 the percentage with any abnormality among those with garage employment is 24.2 compared to 18.8 among individuals with no stated asbestos exposure or garage employment Corresponding percentages for parenchymal abnormalities are 19.0 vs. 15.3 and for pleural abnormalities 8.4 vs. 8.9 respectively for those with garage
18
number
AVFaTIOfi z/e
YI0M
BUA
Type 02 work t/z g
Suipazosae
Z/t
exposure identfied
garage
Soya[eurq Garage work No
eg Baineld
Other STqeL Avz-x [ewaoN dustexposure [eukysred asbetos heating Fo
420385 ,
pue
categorization
Joqum
no
oul
categories
4)
)
0
0 fa) re)
0
I
to 0
if
9
T
() 0
Normal
Normal
c
0
0
0
activty i
9 0
9
9
L
l
ay. -x2
0
t
opacitesopacitesUQ daey
0
<
Parenchyma
Parenchyma oste *yz0m
0 9 UeF P& arenchyma 2/2 2/2 ayeig
work 107 9 ras z 0
oO 3 atqz3sOASaqse 4
8
1 il 19 eT 84
00 oTqey .
1) cz Zz 66
Ao
f*a t
3"sse
yons
use OF
Sq
1 UF 343
2
UF
is 30 Z^' OIt LU <Z LZ
=
trades 52 27 702 Ot O < 2G
0 z08a,e>A9MOCT
) ' sy IsyWO 0 xay2zy
S$
897
0
00
&
satTroFaqed ansodx work
0 factory ansodxs 0 ainsodxe soyeqsy o8er3 267
exposure activty asbetos e.g clasifed of atno indvual in work
such
activty in
other lower
categories
shipyard
_~ Ss
(q2z0m
Bapexy
YK Jo 0 MOT,
0 0 uy
indvidual AzoqBy ou TayxIOK
person category clasifed category OF
e.g.
also
have
On
have
the
ex-
19
</Z
AZTAT
RIS
Z/Z
YAO
0Ff
Type workwork
YuTproa.8 exposure identfied identified employment
SofjptTewrug No Jo o/1
98 Bainatd
Other 9TqeL Aer-y [Tewmouqy Posibleasbestos
TewAqsuzed Shipyard heating
Fo
AroZa
eS Totals
pue categorization
Aoqun worker
ayy
asbestos
fe) 0 6) ) Abnormal 0 4)
0)
0
ag
0
) Profusion
)
0
I
6) ra
aqt X39
0
0/0
0 0/1
0
1/0
ra)
asbestos r4 T
t
0)
0
1
opacitesopacites UH oaeq
1/2 re) 2/1 Parenchyma Parenchyma "Yx0%
0 | < UBT ueosad ASYIO p[noa ayeIq
t
9
z 17
0
0
t
0 sOySqse szayrzom 6
6
<9
)
<
oT!
AO
-a'y
3'ase
0 ras
yous
fatqey
aTqez 0 03
T
ze
a9
0 UT 0
VaNnsSOdxa pzed tys exposure
exposure
z
Zz m
2
tl
0 AaeMoy 0
s) Se sy ADO a7[qe0
0 ArOBaqzeo trades
Ol
< 11
0
10
Z
Tt
67
3q3
saFY UT
e
0 (720m 0 Jo JOU MOY
1 work
sopeay
FO P[NOK uy
factory such ansodxa ansodx category work activty
that category exposure
is
a indvual category exposure
categoris dust the table
would shipyard workes e.g in categories shipyard
indvidual AzroQeZ given category
or other clasifed clasifed clasifed clasified
such e.g.
work
also
have
Se
have
ex-
yeantg anbeytd
AYTaJoe categorycategory 7
FIOM
AyT[eurog pleura activity
10
asbestos work 164 rat work
Fo
employnt (1/0-/0)
lq
SoUyItTq, wz
trades dust exposure
PUT
Posible
heating
ZUIXY Vv
factory factory
Ayogaqes [Tewsouqy eanstd
calcifcation
with pleural
pleural
categorization
clasifed
yon
Fo
adA^'yT
S
t (EET t ( <)zt (1)1 z (7)S
(8)
0 2z
[z} {zle ) 0 0 9 ) 0
0
of 0 Extent Extent and thickness thickness
pleural thickening
t
860
60
0
0
9
2
9
.
<
el 3Z 0
0
e
T
0
0
Tt {i}
r(t]9 0
11
0
3< 0
( ) a ' e ft)
0 (t)lot
0
9
4 4 Zz ( <}6 0 y 1 2 3
L
Ss
L@
Zz 8
<@
aL
t
99
Sc
thickening thickening 8 Oze LZ <s 6L
SEL
present
uoTPENSU) that
table
pleural
given
thickenig
category
also
shipyard
shipyard20
shipyard Ason workes e.g. , could
syerg Zenp aT
paTsZuUpT anscdxa o8vze9 ON Syuzg 19430 qtsog paedryg 4I5TG
STEROL
ON
f708a3e2 s3SNpsatrogyea
@ 19430 UT
activity ZO
vansodxsojseq soyaqse oF
ou o%
dATY Pleural sanodxa
califcation califcation
califcation oste
AzoZaye2d SAVY ptnoa
*Zurayot WaTSJou
TernayTd UeT& prRom '3'a
qypa ASYION Sszaqiom
[eaptuTquaszd
2
ayexrq
e
paed
tys
2 (sjanbe,d0
atqey TT
))
paTj{seo 2 pur
SB
egy
2
st oq}
Ut
voTyetzI[Zo ofAQTZYOE ypA Teqy}O uoszed oT"YOM
WITH
ewe
quesad YIOM exposure SyBIq
no exposure
a
exposureexposureexposure asbestosasbestosin
y30q eyz AvYyIO faTqey
asbetos= = =
UT
[ ({ ] )} x,5
TeHoT ByQ ay4
ayy UO vi
NS 4
Sap~rAoFjeAxto8a3> [RaNdsTegnbeyd Ct4 (Z) (Zz z re) (1)z (9)s (it (6)91
*Ss3np
& 3q30 ut
Jo tO
according
to
categorycategory So3seq pleural parenchyma parenchyma abnormalites 0-2 abnormalites acording ) to
AQTSRQOF ainsodxaS0Rsqe Abnormal
03 ou 0}
Z2
WIOM Ay}
OF [emouge Normal sae)
activty TeanyTg pleura rac
20
gare work
1c:
85 rAd
exposure Brake exposure
6
dust
heating
9 L
efxapcostuorrey exposure [ewurogy Bad nal
0
Oo
o
o
0
0.
600
0
69
60
60
0
2
abnormality
thickenig 2
(1)
e{T3t 0 ie) ) 0 {tle (12
1 2 z 0 o 1
0 C1
0 00
3
)
T4
0
0
o
6)
00
s4eq sinodxs sinodxs
Pleural aey califcation califcation
2 califcaton2 2aey pynos usazTs you e prnoa -B-a ot
FAC
3 ARES: (Ze {tis o
00
00
3< 0 0
1 Aayiom szayr0om
1 Te(ENPaAtpu syee@xq predrys
1) SUOTAPS 0 ) 0 LT 9 It fe) 0 0
T
0
1 pue
2s
e
eya
Yons atqeq
( aq}
UF
Ayrayou pue
pleural pleural
07
$8
St
9
9
6
<l z
SEL
y3t4 ASsYIO
vosxzad MoT YAOm
califcation
YAM
w
wotqesz1p of given ywasdno pleural
an
given thickenig
SyeIq ofyrom
exposure
se
clasifed that categoryalso asbetos shipyard workers
asbestosasbestos in
shipyard exposureexposure would e.g. could YIOA paTzT Ao YAM
could SyeIq Jsnp aT
Fo
asbeto S[eq0y opr
ON ayxTIag
uotzernsuy) oasnodza parsdyg sSerey qtsog za01g adfkt cy
2430
y30q
= ==
[ ({ ] j}
ze
ou zsyQo atqeq
ut
ayy, 243
auqL roMer 10 Lr
22
aqQuay AS20ZazeD rar Les Parenchymal Parenchymal Reading Ll cer 6 86
UT
sotq[ewru AQTR9"
Aci~-y
OT yo YA0OM
P14RL OF
osequazodOther
pue
zsquny
Z
asbestos
garage
work 0 garge
Tt
Brake work work I
asbetos asbestos
factory factory
T %S 0 0 -
0-
.0 -
fa) -
6) -
t
48 70)
0-
z category
0
work 81.2 % %Z E % Ges 30 29 2 3.4 %
5.0 %
0.5 %
i
202
LY 06%8'y
=
|
|
|
L 75.8
% 15.1
15.1 8=4E'9
0.7 %
5.0 %
17
%
1 Z9PT
L
537
#9 YG"9
0 75.0
% 14.7
%
%6 0
0.9 %
4.3 %
5.2 %
1 4B" fh) -
%S O
076.0
6
1g 15.2
LI 41 91 0.7 %
9% 2
6
%
et%8 6
Z
35
oct %e et
17.1
exposure exposure Loy RBS 8%0 SL 0 %092 81@
<4s3 89
6L %z9
77
Ged 28 9
983 yazom
9.1 1 ainsodxe(410M
exposure 64.2 yAon 55.6
%
10
14.6
9.8
0.8
123
soyaqse
0.2 work % % 5 1.1
on 74.8 % 130 6.5 4.8 43971G STEROL
Ae)
Url
xraqumy Ai08a 6
ZO0Z ces SIt tty Sse ^'d <Z1
86
ze9
parenchymlorZaqei3to/pue
20
T/T] 1/0change 20
asbestos
asbestos
asbestos
workasbetos Teinstd Avi-X
:pue Aue24
IT work x0
[euAyoal jo O/Ted10/pue
AWTtq.e work
exposure [eanstd exposure
17.1 of
asbestos
Auy
heating asbetos
TewAyousredtradesexposure 21.1
work
pleural parenchymal LET 47
greater 8 Any
%6 parenchymal
pleural 21 and or
parenchymal parenchymal
pleural
6
eI S1 pleural
and thickening thickening thickening
4381 11 40 92 252 40 g 46 %2 %8
42
ge
Ott
62 Sz
TOT
ZA
by
252
ZZ
TE
SE
8x2 SZ
46 93 ZL S 5.7 45
1
-1
2S" 42 -1 45
ST
SY 5.7 Il 6 oe 8
ci 61
te SZ
-1
-1
Ell iT
EST LZ 42 81 25.2 %L %S -1 43
I<
zol 61
97 02
BL
81
9
LT
gL 07
97
KE EE 2ST
ainsodxa
dinsodxa
sapezy
(Y20H t
Binsodxe
AZTATI
sojaqse YIOM yom
YIOM
aXeAQG
Yroa
eansodxa
soyeqs
3urqvoy
AroqIe;
soy se uot
paediug STISsog 3e{nsur) Oe payzeqs a8er3 asers oY syeag ysnp
SL
YIM oN 306 pry
29430
yosaTG UqoL
24
employment compared to those with no such employment or no stated
asbestos exposure
The minimal overall differences between these two
groups are more manifest in parenchymal abnormalities there being
little difference in the percentages of pleural abnormalities On the
other hand significant differences exist in the percentages of pleural
abnormalities among those employed in work having direct asbestos
exposure or shipyard employment and those only employed in garage work
or having no asbestos exposure We will thus utilize both parenchymal
and pleural abnormalities to characterize the various exposed groups
3
Other criteria could have been utilized for the determination of an
abnormal ray For example we could have required that all four
readers read an ray as abnormal before it would be so categorized or
that an averaged reading of 1/1 be required for the establishment of
parenchymal fibrosis or that pleural plaques not constitute an abnor-
mality To
ities would
investigate whether more stringent criteria for abnormal-
have altered the analysis the overall results were cal-
culated with the criteria for abnormality being an ray categorized as
1/1 or greater and the presence of pleural thickening of calcifica-
tion plaques were not considered abnormal These data are shown in
the last column of Table 11 and demonstrate the identical trends that
were present in the data with less stringent criteria for abnormal-
ities
Table 12 shows the distribution of abnormal rays for each reader according to work category While different percentages of abnormal rays were obtained by the various readers the trends according to work activity were highly consistent Those engaged in brake work had a higher percentage of abnormalities compared to those who did not and those with other asbestos exposures had the greatest percentage of abnormalities according to all four readers Thus the overall ray results are relatively independent of the individual readers and independent of the criteria for abnormality established
25
Zz
Sl 8 92 $'IZ Le $ 9% 6 7Z
ROL Table (186/Z1z) (186/59) (186/097) (186/497)
Percentage 3snp 62ZX 982abnormalites ets abnormalites teal (S </9) L&%(S </6)
so category
PTqtsog Ysqse job job ez category 89Ecategory gee(11/9@) geE(14/92)
*saepax ,
Heavy
exposure
no brake (eet exposure Shipyard Shipyard Posible
paeAdrys exposure Shipyard Posible Posible /4)
jo
exposure 4203985 18.8Azo3aye. ( 101/421
)
et
Aavoy ) (6/9) 4/9 ) 4/123 4/123 yoy ( 24/7 )
16.8
STQeL 34/202 got
31.7 &q Savzeg(( ) (9L1/6Z) 4/9 5.6 42/12 542//1122 912( 17/76 36.8
64/20 of
19.3
(12/01) ( ) 47/123 ) 27.6 4/9 47/123 eSZ 3.8
aywag (
8
<
8t 8 91 Lcre 61 < S.
anamnsodxs (207/8<) (Z0/#E) (Z0%/9) (Z0/6) (Z02/L<)
rapesay
pogezaySutprsa I
z
4
26
Age standarization of ray readings
Inasmuch as the prevalence of ray abnormalities reflects various
assaults to the lung separate from that under study that accrue
overtime it is necessary to consider age in comparisons of groups
exposed to asbestos in different circumstances Any age effect can in
part be due to unknown exposures to various dusts including asbestos
the opportunities for which increase with time Additionally any
related changes progress with time and the manifestation of rela-
tively minor exposures early in life can be significant in later years
As discussed previously a selection criteria for the exposed and
control groups resulted in study populations that had similar age
distributions However to more accurately take into account any age
effect
ized to
the the
overall percentages
age distribution of
of ray abnormalities were standard-
all 983 individuals for whom readable
rays were available using equation 1
A standardized percentage stdstd was calculated
N,,
1
Pstd
= =
PN,,9 83
Where P. is the percentage of abnormal rays in the ith age category
of the group of interest and NT the number of all 983 individuals in
the ith age group For a group having an age cell with no data
insulation other standardization was based on those cells
with with with
data data
std
NT
=
NT 1/983
avail i
/
yt yT
i N
all i
avail i
2
Where P. again equals the percentage of abnormal rays in the ith age
category of the group of interest and N. the number of all 983 individuals in the ith age category P is the percentage of abnormal
rays among all 983 individuals in the ith age category These over all standardized percentages are shown in Table 13 The difference between the individuals performing brake work and those with no identi-
fied asbestos exposure remains while the percentage of abnormalities
in those employed in a garage but not engaged in brake repair work
27
PpazieuysPercntage 2O0l SC 1O l y Table
c'24 S$ 9 9 9
o 1
69%
$
#
F
+
-
a8y Percentage - abnormalites abnormalites acording work activity by 9 72 2 Sz 9TQeT
standardized
40 40-49 50-59 Totals percntage (6/12) 60-69 (2/92) activity (S </8) work
<
oe
40-49
'4
50-59
9 OF
6 22
70
Totals
Se
4
by(6/4) percentage
929M
Aq
t
Sher
7/47
~X
oremployment
Qi<
11.9 11.9
8 7/47 0 </E4)
15.7 (2/2)
26.7 26.7
0'0 34.4
<
34.4 ( </T)
OO 30.8
0 09 24.2
oot (1/1)
24.3
- STQ#pes2 YOM
( brake
25.0
9
i (2/8 9E 0.0 (s/8) 9/389/38 7Td8/35 ) (6/ <) 2/7 ) ( 21/9 <'ce( </T) 18.6
wous
705
24.5 19/107
worket
19/107 10.7 Body 38y 6S-0S 6/54 0.0 ( 0.0(86/6) 38/15 83/8/1154 TL( 71.4 (21/2) 0.0 0.0 9613/32 30.6 (S/2) 38.6
38.6 <g6
6
work exposure 1(i9/L) Lst 2/11(1/0) ( 0 0( )(1/2) 1/3 1/3 0028/35 a 20.3 IIE
( 2/12 32.0 asbestos
JO
exposure
,
woTyngtzisp 0.0 ( 39.6 60.0 ,
trades
e'y
6 TT
20.0 20.0 Tit
0 017/42 40.5
60.0
0"0 4/123 35.8
30.8
30.8 30.8
/9T)
asbetos YA0M
:
(z04
aBe
Sopeiq
943
factory BOYSIQe 34.9 ) quawioy10.4 16.9
12/9 248/93 YIOM 14/134 dua 36/213 104/372 ya0om 4ysnp
14/34the
all indviduals indivduals
rays avilabe paztreuys distrbuion readble readble the oy distribution
whom
( Az03e3 1.6
were avilabe
t
28
decreases to somewhat below the level of those unexposed otherwise The percentages of abnormalities among those with other asbestos expo-
sure remain significantly different from those unexposed
If we consider the percentage of ray abnormalities a manifestation of a normal distribution with a variance reflected by the number of abuormal rays the respective standard deviations in the final column of Table 13 are calculated While the percentage of abnormal rays in each of the job categories of Table 13 has a large uncertainty associated with it because of the limited number of individuals in a work activity other than brake work the pattern of observed percentages yields a remarkable consistency The two groups with no identified asbestos exposure garage controls and garage workers with no brake or body work have the lowest percentages of abnormalities the various
activities with probable asbestos exposure have the highest percentages and brake workers are intermediate Individuals with other dust exposure appear to be unaffected by such materials This is probably the result of the relatively short exposure times or the marginal exposure circumstances The other dusts included coal 23 men silica 9 men and other dusts 3 men Five of the other dust exposures were for longer than ten years One of the five had an abnormal ray The average exposure of the other 30 was 3.2 years In subsequent analysis these 35 individuals will be characterized by their garage or garage employment One notable feature of Table 13 is the high
percentage of abnormal rays among the 32 individuals who worked for
some time in auto body repair See subsequent sections on auto body repair and undercoating work
Smoking standardization of ray abnormalities
Smoking has been identified as exacerbating the malignant effects
of asbestos
Death rates from asbestosis among 20+ cigarette
smokers are 2.8 times greater than among nonsmokers and Seidman 1979 and both parenchymal and pleural
Hammond Selikoff ray abnormalities
have been reported as more common among current and smokers than
nonsmokers Weiss 1971 Rossiter and Harries 1979 Weiss Levin and
29
Goodman 1981 An effect of smoking on the prevalence of ray abnormalities was also found in this study with both parenchymal and pleural
abnormalities found more among smokers than nonsmokers and more
frequently among current smokers than smokers The age standardized data for the overall ray readings are shown in Table 14a
Table 14b lists the percentage distribution of smoking histories ac-
cording to job category
As the unexposed group contains 25 more
current smokers than the other exposure groups the ray results
where possible should be standardized for cigarette smoking as well as
for age This can be done for major work categories but is unreliable
for most subcategories because of the absence of data in some smoking-
age cells The standardization procedure follows that of age standard-
ization and utilizes the overall smoking histories of the study group
31.6 were smokers 42.4 smokers and 26.0 nonsmokers
Standardized ray abnormalities by work activity
Table 15 lists the age and smoking standardized percentages of ray
abnormalities among those with no identified asbestos exposure those
engaged in brake maintenance and repair and those with probable asbestos exposure including auto body repair work The overall percentage of abnormal rays among individuals with probable asbestos exposure
differs significantly from those unexposed 0.005 two sided The differenc ies particularly significant 0.0002 for pleural abnor-
malities This occurs because pleural abnormalities often appear from relatively low asbestos exposures and can exceed parenchymal abnormalities in prevalence at long times from onset of exposure See Anderson et al 1976 e.g. As many of the individuals in this probably exposed category worked during World War II in shipyards we are observing
effects in this group after 35 years from onset of exposure
Table 16 lists the age and smoking standardized percentages of abnormalities according to garage activity and union There is relatively little difference between the percentages of abnormal ray for the auto workers of UAW Local 259 while a large and significant p < 0.05
30
Table 14a
Age standardized percentage of ray abnormalities according to smoking history
all exposure categories
Smoking History
Abnormality
Smokers
smokers
Nonsmokers
Smoking
standardized
Pleural
14.0
11.2
9.1
11.5
Parenchymal
26.3
16.0
13.9
18.8
Any
32.6
22.9
20.4
.
25.3
Table 14b
Percentages of distribution of smoking histories according to job category
Smokers
smokers
Nonsmokers
No exposure including
mechanic garage work
39.1
39.1
21.7
Brake work
Probable asbestos exposure
29.1 31.8
43.1 42.0
27.8 26.1
31
Table 15
The age and smoking standardized percentages of ray abnormalities according to exposure category
Exposure category
Pleural
No identified asbestos exposure
8.4 1.6
garage work
10.4 2.3
Garage work but no
brake work
6.6 2.2
Brake work
Probable asbestos exposure
including body work
7.2
19.8 2.7
Parenchymal 15.8 - 2.1
17.0 - 2.8
14.4 - 3.5
19.3
19.9
2.7
Any
20.1 2.5 21.9 -3.2 17.8 - 3.9
24.4 2.5
32.5 - 3.5
32
Table 16
Age and smoking smoking standardized percentages,,percentapergcentages,, es,, of ray abnormalities
for different groups of garage workers according to work activity
Work activity Brake work
UAW 259
19.8 - 3.0
No brake work
17.3
Percentage of participants
with other asbestos exposure 15.1
UAW 595
. Group
DC 37 SEIU
28.9 - 4.0
21.7 4.4
18.7 4.7
16.3
25.8
;
Overall 24.4 2.5 20.1 - 2.5
21.5
1
Standardized to age and smoking distribution of all 983 men for whom readable rays were available
No identified asbestos exposure
.
:
3 Does not include 12 individuals with asbestos
amphibious vehicle construction
exposure
during
33
difference exists between those employed in city garages and all other
groups combined This can be attributed to the greater grinding and
finishing of brake lining material that the city workers do The work
in commercial garages is virtually exclusively on automobiles in which
brake shoes are simply removed and replaced Asbestos exposures large-
ly occur through the air blowing of residual dust in the drum housing
Many of the city workers on the other hand repair truck brakes and
here machining of the lining may be required to obtain a proper fit
This additonal exposure can be significant Rohl Langer Wolff and
Weisman 1976 found
machining of new brake
short term asbestos concentrations during
linings to range from 24 ml to 72 ml
the
Tables 17a and 17b show the percentages of individuals with ray
abnormalities according to years of garage employment and years since
onset of garage work As can be seen there is an increasing percent-
age of rays according to either variable However to some extent this would be a reflection of the previously discussed age effect seen
in both the exposed and unexposed populations analyzed in this study In order to take into account age the standardized percentages of
abnormal rays were calculated for the age decades 40 through 69 years for those employed more than or less than 30 years and more than or
less than 30 years from onset of employment Individuals in each of
these three age decades were included in both the 30+ years and year
groups So difficulties with empty cells was avoided However the small numbers in each age cell prevented any smoking standardization The results show that those employed for more than 30 years or with 30
or more years from onset of exposure have the greater percentage of
abnormal rays
The differences between the age standardized abnor-
malities in the group with 30 or more years of employment and those
with no asbestos or garage exposure or those with less than 30 years of
garage employment achieve a sided level of significance of 0.05
An analysis by the estimated number of does not indicate any trend Table 18
brake jobs per week however The estimates are necessarily
uncertain because of poor recall and the analysis did not consider
either duration of work or time from onset of employment
34
Table 17a
Percentage of individuals with ray abnormalities according to years of garage work
Garage work
20
Years of garage employment
20-29
30-39
40+
Totals
Brake work
13.8
13/94
No brake work
27.0
3/48
Total
18.3
26/142
20.0
34/170
16.7
6/36
19.4
40/206
Age standardized
30
Brake work
19.4 - 3.0
28.8
34/18
16.7
2/12
27.7
36/130
45.2 14/31
0.0
0/3
41.2
14/34
30+
23.0
95/413
21.2
21/99
24.2
116/512
28.7 -4.2
Table 17b
Percentage of individuals with ray abnormalities according to years since onset of garage work
Years since onset
Garage work
20
20-29
30-39
40+
Totals
Brake work
13.2
10/76
No brake work
22.5
9/40
Totals
16.4
19/116
20.3
30/148
21.2
7/33
20.4
37/181
Age standardized
> 30
Brake work
21.2 - 3.6
24.4
33/135
11.1
2/18
22.9
35/153
40.7 22/54
37.5
3/8
40.3
25/62
30+
25.3 - 3.5
23.0
95/413
21.2
21/99
24.2
116/512
35
PpezTuyspesquaored $'9Z 0Ez 827 Age 98T y' <Z
of
Age
ase
SuypscoeAq STeVOL
ya10m
sAva-
+02
Bt axerq
sTqeL Temzrouge yo 1-4 times
FO Asvenbsry than
s
eQu
arzSg
3yQ
OF
work
O%>
Standardized
Standrized
readbleayeig
23.6 9E%17.8 Zz Cost/ov)> T <Czzat/zy) Ste 36.5 Z1z(6/TZ) D <Z percentage,,
SLENPTAU 19/107 19/107 ( 38/15 )( 31/85 35.7 2/5 ( 96/406 2.2
23.1 86S9e7/52 ) 14/60 ) Cxe/ot) 15/42 ) 1/3 0.0 23.1
<86 ITB
Fo
cy
1/1
9.1 (
35.3 (8z/et)
66.7 6 .7
100 100
31.8
31.8 31.8
DOFANGTS BLT
eTQyea 0/1
0.0( 25.6(y7/TI}
22.9
2 .9
0.0
0.0
21/9
21/9
TP
|a8e
whom sAer-y 24.9
ayy azam
( 19/18
) 47/192
47/192 (
)39/120
8
4/12 )
17/505 17/50
02
distribution distribution all Al indivduals
al
were available 9-7 x80m saqy yom ayeazq
yI0mM |
qupeax
Auy
on TEIOL z
36
Among those members of Local 259 of the UAW who were examined 27 had been examined previously Lorimer 1976 Table 19 shows the comparison of the two sets of readings for these individuals Of the 27 pairs of rays read ten received identical readings The 1979/1980 reading was one subcategory higher than that of 1974 in seven in six it was one subcategory less One reading was two subcategories higher in 1979-80 and three were two subcategories lower Thus the overall readings were very similar between the two periods of time and there was no evidence for any progression of fibrosis among the small group of individuals examined in two periods of time
Auto body repair and undercoating work
The highest percentage of ray abnormalities in any group observed in
this study was
riods of time
among men employed in auto body shops for varying 38.6 versus 24.5 for brake workers and 18.6
pefor
garage workers who did no brake work While relatively few men were in the category the percentage of abnormalities was significantly higher than garage workers who did no brake repair 0.05 sided
The average time of employment of the group in body shops was 13.3
years Of those employed more than 20 years 5 of 7 71 had abnormal
rays
In past years asbestos was commonly used as a reinforcing agent in
plastic auto body fillers used for dent patching
Extensive dust
exposure was common as the material was sanded smooth
The extent of
asbestos exposure is unknown because no fiber counts are available from
such operations Fortunately with the increased awareness of asbestos hazards and with the introduction of the occupational asbestos stand-
ard most manufacturers removed asbestos from their formulations In a current 1981 analysis of six compounds used in shops employing UAW
259 members no asbestos was identified However while current a bes-
tos risks no longer exist in these shops at least to our knowledge
persons exposed previously should be made aware of their asbestos
exposure the risk associated with it the synergistic effect of cigar-
ette smoking and the desirability of appropriate medical surveillance
37
Table 19
Comparison of ray readings of garage employees 1974-1979
1974
reading
0/0 0/1 1/0 1/1 1/2
0/1
1979/1980 Reading
0/1
1/0
1/1
6
2
0
0
5
4
4
1
0
0
0
0
0
3
0
0
0
0
0
1
1/2
0 0 0 1 0
38
Automobile undercoating materials also contained asbestos as
forcement fiber and disease had been suggested in individuals
a rein-
engaged
principally in undercoating work Thirteen men were identified in this
study with significant periods of undercoating work Of the group
three had abnormal rays but two of the three also work in body
shops
Thus we have insufficient data to evaluate a risk from this
activity in this population Parenthetically numerous other men re-
ported having occasionally one to two times per year applied under-
coating materials These individuals were not segregated in any analy-
sis In all cases where undercoating was done mixed compounds were utilized It would be expected that the spraying of such material
would not lead to the release of high concentrations of resirable
asbestos fibers However the grinding underfoot of dry sprayed material on shop floors could release the encapsulated fibers
Effect of previous shipyard employment
Of the 983 individuals with readable rays 87 had been previously employed for some period of time in a shipyard generally during World War II Overall 39.1 of the rays of this group were abnormal On an age standardized basis 28.6 were abnormal compared to 20.5 for all groups unexposed to asbestos control group garage workers with no brake or body work exposure and those exposed only to other dusts Because of the relatively small number of cases the difference between these percentages is not significant at 0.05 level Tables 20 and 21
show the number and percentages of abnormal rays according to years of shipyard employment and time since onset of shipyard work To the extent possible age standardized percentages have been calculated for each exposure category although with the small numbers in a given time
cell the procedure has large statistical uncertainties The average
time of employment of all 87 individuals in shipyard work was five years As few 15 worked longer than ten years the data in Table 20 on the trend according to shipyard employment are unstable because of the small numbers in longer term employment categories In Table 21 however a significant thand with years since onset of shipyard employment is seen On an age standardized basis 37.9 of those with more
39
Table 20
Number and percentage of ray abnormalities according to years of shipyard employment
Parenchymal reading
Years of shipyard employment
0-4.9
5-9.9
10-14.9
15-19.9
Totals
Normal pleura
0
31
14
4
4
53
1
3
4
0
2
9
2
1
0
0
0
-
Abnormal pleura
0
7
1
4
1
13
1
8
2
0
0
10
2
1
0
0
0
1
Any
abnormality
20
39.2
Age standardized percentage of abnormality
27.2
7
33.3
24.7
4
50.0
45.5
3
42.9
37.1
34 39.1
28.6
40
Table 21
The number and percentage of ray abnormalities according to years from onset of shipyard employment
Parenchymal abnormality
0
1 2
< 10
Years since onset of employment
10-19.9
20-29.9 20-29.9
30-39.9
Normal pleura
3
3
12
33
0
0
2
7
0
0
0
1
40+
Totals
2
53
0
9
0
1
Abnormal pleura
0
0
0
2
9
2
13
1
0
0
0
9
1
10
2
0
0
0
1
0
1
Any abnormality
Age
standardized percentage of
abnormality
0
0.0
-
0
0.0
-
4
25.0
19.2
27
45.0
3
60.0
34
39.1
36.6
47.6 37.9
28.6
* Age standardized percentage of those 30 or more years from onset of shipyard employment
41
than 30 years from onset of shipyard employment had abnormal rays This percentage is different from that of unexposed individuals at a 0.02 sided level of significance
It is possible to compare the results of the prevalence of abnormal rays among different shipyard populations 30 years or more from onset of employment The finding here of 17 more ray abnormalities
compared to controls among former shipyard workers employed for an
average of five years is in agreement with studies of the effects of
term shipyard employment In a study of ship repair workers
employed for more than 20 years 87 of the rays of those 30 or more years from onset of employment were abnormal Selikoff Nicholson and Lilis 1980 The percentages of abnormal rays in the two groups are approximately in the ratio of the periods of employment
Evidence of malignancy
In any ray screening of a population of this size it would not be unexpected that a chest malignancy would be identified Such was the case with one individual in this study He was referred to the chest service at Mount Sinai Hospital for follow diagnosis His bronchogenic carcinoma was not operable and while alive two years later was in poor condition Parenthetically at examination his CEA level was 1.3 nanogram and his sputum analysis showed moderate atypia but no malignant cells present
PULMONARY FUNCTION TESTS
Principal spirometric tests
Tables 22 23 24 and 25 show the mean values of forced vital capacity
as a percent of that predicted 100 x PFVC the forced expiratory
volume in
TVC the
1 second as a percent of forced expiratory volume
forced vital in 1 second
capacity 100 x FEV /
as a percent of that
predicted tween 25
100 x FEV PFEV
and 75 of forced
and vital
the maximal midexpiratory flow becapacity as a percent of that pre-
42
Pez;
Sutyowsprzepurys
Zed"
S6
Forced
work (62)
9
exposure employment
brakewith
body 97%96
withAvy including including work (29)
FO including including
employent AlcS
Al FTqeL &
6
2
posible 2FLpossible
asbetos se gof asbestos exposure oj heating
Aqtorde ZuTpr0s5 exposure [rapa asbetos exepxpoossuurere
psoig
mean
indivduals to
the smoking
; smoking 31.6 Ex smokers
categorization
activity
categorycategory lower exposure exposure asbestos
9 percent percent
acording
capacity
to
and that history
category
96
94.1 ( 94.7 1.9 ( < <} (Z)
99.2
7
2%
2
( 2.4 96.4 86.0 92.1
Ess
92.1
42
93.6 ( 98.5 1.2 181 (1)
4.6 15
93.0 (
92.8
FL96
2FE 96
6SIT
94.9 ( 94.7 2.2 26 99.8
(
93.0 ( 94.3 2.0 56 10.5
alqysod
sanodxs
gapeaz
(yzom
ansodx
distrbuionmeaningful of
distribution distributionsmokers
all
with
valid
pulmonary
KkzojaeF
pulmonary pulmonary
)
theother dsusutcshdust sOmokners person indvidual clasifed given given
Smoking ou Jou
aT
a ey Smoking
standrized,, standardized,, standardized,,
standrized,, UT
95.7 4804
UT
95.7
AzoZaqu 1.2 sye2q
uopzuNy 91.3
91.3wats SB
@
1.5- UF
Azeuow{nd 0.7
96.9 pTeA 92.9 TENpFAuy 2.4 YIFA (%o9z uoszadBy
we UQ 03
96.1
1.6- [Te
JO Aey. 96.1 Yone 3
srayou-n Ss} 95.8 -1.5
3 WoTANQIYS|p( AYTIOR%y"Zy 19.1 19.1 2
ay} FO
UF ostr
* SuTHYows02
ay}
JO
srayou-xqayy
YIOM AaMoT prtnos
JO OF S*a
STENPAUT AroJaqzed AroSa]eI x0179 *yzOM $%9 OF test function TE B
category ainsodxa szayo0m category test
Fo ayerg
would notwouldcategory
0 ray se
brake worker worker
low
categories
low
higher
_
table no Bart] pardAtys yans
~m
MOT UT
OU 82g
pPeZTazupeysSuTYOUS 6LLOF8 7O1F6' to category and smoking Smoking 4 =
(St) (6%) Curent smokers (2S) smokers smokers Non
work 6
8
quadizadSuTprode
e@
garge IFE'9L 76.5 1.4 o'Ts7'82 - ( 80.1
saBy
&
Se
SeTIOZa3eD
TSYsIY
p{nom
staSnmdorkiizendg,, standrized,,staundorsiizead,,asyYIOp0uvyusayrroFze2
0.9 e BYyQ soyaqse
se
Garage (JAg/ Axio3stypuodas Aga Garge x employment suo
SutTyous 75.7 0.8 <@ UT QOOT) pue
employment
=
1.3
body work 75.6 1.3
employment
L1EL including
work XY
92
3.3
ZL
74.7 74.7 43
( <8) - ( (i)
60FZ 94 79.074.7 (15 79.0
.
e uO
1.0 a+r o3
74.9 "SUNP
78.4 * aqtry
0.4 axrnsodxa 75.7 78.4 1.9 943 2A94G30 aaey UT
etqey oumtoa Ajtoeds>sz03aqe5
AzojeatdxTeqTA gol 03 poszoj
pasiog jo
SOjaqse identifed and posible 74.3 1.1
7
8
(19) 76.2 ( 78.4
6
[Te
Jo sToyus ey, aAamoT OSTe
76.2 0.6 prnod 04 1.0
) uotgnqraysip exposure 1.9 T'1LFE"yZ 1.7 76.4 18 1.0 Posible asbestos 75.4
0.7 aAnsodxa szayioa exposure
12.8 srayous-xg standr e1qIsodansodxs soy8q1se.6 sozaainqssoedxa 2 ansodx predtys indviduals offactory factory mean YI0% pur of
category meanigful function = few category in category to
Standardized
smoking
distrbution distrbution of valid pulmonary test UOTIZBaXeD 31.6 smokers with est Standrized Ex smokers % Smokers categorization
smokers
that
75.5 *8'a 75.7
1.2 ( ) 76.4 B@
)
0.7
(20H ayy
"HIOM
Suryous saperzq
12.8
YOM azqyQ0
72.7 12.8 9Y3 FO BART syeIq
UT FO OF
ou
se
Butqeay Aaj
S%OIE
JOU
sAPY yons
function function
PTNOK a_qeq function function
pulmonary p[Nnoa azgqrq ( ind af ) have category
ayy
would have no 313
Table
;
ZuT
yous
pesyotperd TGyarpgee employent work SS'IOFF9T"*6S0OTL 91.8 <316Fe8Z0OT L<F8LO 97.6 standrized,,Smoking yey)Aroysty
29 97.6 jO
Sutyous
AZO3STY
9
6
9
work 1F9L6
<F9
16
asbestos asbestos (GIL) 98.1
:
=
employment work (18T) 97.9
O'7FL Smoking history
TOL ot
(ZS) (81) (ZE) (2)
47
42
=
128 (92) 108.0 181
-
a ey
standrized,, standrized,,
smokers
VyeIg UT
102.6
102.6 SB 102.6 ( 1.6 WsAT3 97.6 1.9
e
0.8 UT |YA 105.2
including [eNPTALU quaoradpue SuTXoOUS
e&
<1F0'gOl Azosaqzvose
9%
) 9T92L pUodes
2.5 auc ogoyr
UT
Jutpz03s5e ( BUNTOA
56 ) (*higd/
UOTIeAdxa 10.3 Aas)
to smokingsmokers distrbuionactivty distrbuion 26.0 pulmonary functio test paoszog
EC
ebmpolodymeynt work
T 9
95.9 1TO2L eFE'6 96.9 1SE5I
Posible Posible asbestos exposure 98.8 exposure
24 (92) 99.3 (Z)
Shipyard 8Ship6yard heating 1tra6des 96.7 35 09F386 102.4 =
amsodxa 135.1 ( ( standard
sojaqse ButTqvoy ATOZICT few indivduals the category category
To meanigful valid Standrized Standardized the category be
all
T(he Sexmpookseurres categorizatn categorizationcatEegoxry work activty such such smokers indvidual
105.2 (
( ) e 97.6 3.4
TTe ue -atJaqZO osTe ( Jey 102.8 1.3
( YSNs 102.8
ST 101.7 2.0 *MIom
10.7 3.5 12.5 32 03 103.1 1.81.8 uvali UI
103.1 0}
TaMOT ce
101.3
5.1 2 * FO
Yom Yyons
Axo8azed pavdtys ayy Fo
OY
AsYyO SaTqeq
'%QLE atqey TOIT OF UT Jo function
e
FO
BAY ay3
pulmonary pulmonary function
===
YOU 343 UT
UT
category would given
classified
givengiven
classified
a
would worker worker have have
3
yPezt
9
8
8
Sutyougpreugs
SEF"
Ss
<FS
forced
expiratoy flow
A3r2ed> (61) (92) (06) (7)
work
$ 9
< 9 Curent smokers
Teqta
CIKW/SNH staed PFSIOTOF X Ai03stu Garge
LCLO01) Sutyows pus Due Garge
Se
including 2.9 Yor
asbestos 469 83.6 5.5
or work 78.0 5.9
employment < 9 78.9
employment zE'SL 82.3
peqatped91qeL
AsoSaqnowsozaq yeqy qol yo
MoT} 09
quazed
'
identifed and posible 76.2 4.1 asbestos exposure 81.5 7.1
Posible heating trades 72.8 5.3
AzrojZetdxs Burpadsese
Table 25 75
(9 <) Smoking Smoking
- 9 S
smokers
F6
FZ H0T 92.3 5.8
($9) 78.3 6.3
8'> 98.4 2.6
z68 71.3 9.4
(8S) 89.2 4.8
1 ) 82.6 8.6
FZ9/ 92.8 5.7
=
(1)
"3893
< <2I (
(
(
27.9 90
{Te
jo
(2)
1.5 6.536 69%F0L 10.1 12 23 104.9 UT -
OU
BABY 3ou *arqez oTqe2
PN ayy 942 p[nom ur
Smoking
standrized standardized
Arosazedsyerq standrized
e
95.1uaTs Se
Bw
95.1ut 80.5 Uy patysepo 93.6
TeNpATU 93.6uosad80.0
Ue 80.0 03
ev
89.0 Jey ortS{NP
yons
st atqeyAsyjJo 87.0
AJYTADE aqQ 20 ut 89.6
123. 1 soyeqs few @Tqtsodal soqeaanssoedx Butzeay pulmeoinnasryodxaAr0,De5 ( ArtoZazeDainsodx to PpecstoF
exposure ,
of mean
(Yt0m 123.3 03
Sapezy FO
YAomM AasoT PTROD
ayq Jo oy -2'a
of be ay] individuals category pue
10213 04
UI Fo
%qTE
YIOM
&
the meanigful sroyY40m Standrized Standardized Standardized
category smoking
activty Non smokers valid pulmonary functiotest Uorqetigsa with pulmonary , Smokers
31.6 smokers have no categorization categorization
smokers
ofwork activty
meaningful
activty such
function
pulmonary = fu=nction function
given given category category brake
Jo 94vIq Jayjo se
would have YOHs
46
dicted 100 x PMMF according to job category and smoking history
The prediction equations used were those of Miller et al 1980 See
Table 3 The distribution of these parameters is shown in Tables 26
27 28 29. With the exception of auto body workers and garage workers
who do not work with brakes there are no differences between the means
or in the distributions of the three principal spirometric test results
PFVC FEV PFEV
including those with
FEV1 )
possible past
for all exposure
other groups to asbestos
of workers
While there
are some differences between the various job categories in smoking
category subgroups these are largely the result of statistical varia-
tions The more stable smoking standardized data show virtually
identical results for the unexposed control population brake workers
and individuals exposed or possibly exposed to asbestos These data
are shown in Table 30. This might be anticipated as only marginal
differencweerse seen in the
individuals in different work
percentage of ray abnormalities among categories As forced vital capacity is
usually a less sensitive determination of asbestos changes than
the presence of ray abnormalities and forced expiratory volume in one
second relates to exposures other than asbestos the absence of a
definite trend among the groups with varying asbestos exposure is not
unexpected sec section on measures of small airway disease for a
discussion of PMMF
Measures of small airway disease
As was seen in Tables 22-24 with the exception of mechanic garage workers and those men engaged in auto body work no differences existed in the means of the spirometric test results between the three major occupational groups studied those unexposed to asbestos or to garage work those engaged in brake work and those with a probable asbestos exposure However in the case of PMMF Table 25 individuals with an identified asbestos exposure had a lower smoking standardized mean compared to those in the other two categories although not at a 0.05 level of significance The unexposed control group had the highest
mean values followed closely by mechanics engaged in brake work
Those with identified and possible exposure to asbestos had interme-
47
Table 26
The distribution of forced vital capacity as a percentage of that predicted 100 x PFVC
by job category and smoking history -
Job category
60
100 x FVCP
60-79.9 60-79.9
80-99.9 80-99.9
100+
No identified asbestos exposure or garage work
Garage employment
but no brake work Brake work
Body work
Smokers
0
0.0
2
5.6
5
11.1
7
19.4
1
0.8
20
15.6
0
0.0
0
0.0
29
64.4
23
63.9
67
52.3
11
91.7
11
24.4
4
11.1
40
31.3
1
8.3
No identified asbestos exposure or garage work
Garage employment
but no brake work Brake work
Body work
0
0.0
2
6.7
2
1.1
1
6.7
4
8.5
9
20.9
21
11.5
1
6.7
27
57.5
16
37.2
75
41.2
10
66.7
16
34.0
16
37.2
84
46.2
3
20.0
No identified asbestos exposure or garage work
Garage employment
but no brake work Brake work
kody work
( ) = Percentage
Nonsmokers
0 **
0.0
3
12.0
0
0.0
4
13.8
2
1.7
7
5.9
O
0.0
0
0.0
11
44.0
16
55.2
59
50.0
4
80.0
11
44.0
9
31.0
50
42.4
1
20.0
48
Table 27
The distribution of forced expiratory volume in one second as a percentage of forced vital capacity 100 x FEV1
according to job category and smoking history
Job category
No identified asbestos exposure or garage work
Garage employment
but no brake work Brake work
Body work
No identified asbestos exposure or garage work
Garage employment
but no brake work Brake work
-
Body work
No identified asbestos exposure or garage work
Garage employment
but no brake work Brake work
Body work
( ) = percentage
55
100 ^ FEV1
55-64.9
65-74.9
75-84.9
85+
Smokers
0
7
0.0
15.6
0
0.0
4
11.1
4
3.1
11
8.6
1
8.3
0
0.0
12
26.7
10
27.8
42
32.8
25.3
25.0
17
37.8
9
20.0
18
50.0
4
11.1
53
41.4
18
14.1
8
66.7
0
0.0
Smokers
3
6.4
3
7.0
1
0.6
1
6.7
3
6.4
2
4.7
9
5.0
0
0.0
8
17.0
14
32.6
35
29.2
6
40.0
23
48.9
10
21.3
18
41.9
6
= 14.0
99
54.4
38
20.9
6
40.0
2
13.3
Nonsmokers
0
0.0
1
4.0
2
6.9
2
6.9
0
0.0
0
0.0
U
0.0
1
20.0
2
8.0
5
17.2
26
22.0
0
0.0
19
76.0
15
51.7
64
54.2
3
60.0
3
12.0
5
17.2
28
23.7
20.0
20.0
49
Table 28
The distribution of forced expiratory volume in one second
that predicted 100 x PFEV by job category
and smoking history
Job category
60
100 ^ FEV1 PFEV
FEV1
1
60-79.9
80-99.9
100+
No identified asbestos exposure or garage work
Smokers
0
0.0
11.191
11.191
Garage employment
but no brake work
I
2.8
6
16.7
Brake work
2
1.6
14
8.6
Body work
1
8.3
0
0.0
19
42.2
20
55.6
57
44.5
7
58.3
21
46.7
9
25.0
58
45.3
4
33.3
No identified asbestos exposure or garage work
Ex smokers
2
2
4.3
4.3
Garage employment
but no brake work
4
9.3
3
7.0
Brake work
2
1.1
9
5.0
Body work
1
6.7
1
6.7
Nonsmokers
No identified asbestos exposure or garage work
0
0.0
0
0.0
Garage employment
but no brake work
~
1
3.5
1
( 3.5
Brake work
1
0.9
4
3.4
Body work
0
0.0
.)
0.0
) percent
15
31.9
17
9.5
41 22.5
6
40.0
28
59.6
19
44.2
130
71.4
7
46.7
7
28.0
9
31.0
29
24.6
3
60.0
18
72.0
18
62.1
84
71.2
2
40.0
50
Table 29
The distribution of forced expiratory flow between 25 and 75 of forced vital capacity as a percent of that predicted
100 x PMMF according to job category and smoking history
100 x MMF PMMF
Job category
60
60-74.9 60-74.9
75-89.9
90-104.9
105+
No identified asbestos exposure or garage work
Garage employment
but no brake work Brake work
Body work
Smokers
10
9
25.6
23.1
3
7.7
9
30.0
9
30.0
-
4
13.3
37
*
33.6
16
14.6
19
17.3
2
18.2
3
27.3
2
18.2
5
12.8
12
30.8
10.0
10.0
16.7
16.7
14
12.7
24
= 21.8
9.1
9.1
3
27.2
No identified asbestos exposure or garage work
Garage employment
but no brake work Brake work
Body work
No identified asbestos exposure or garage work
Garage employment
but no brake work Brake work
Body work
( ) = percentage
Smokers
7
16.7
5
11.9
12
36.4
5
15.2
14
9.3
17
11.3
4
36.4
1
9.1
Nonsmokers
0
0.0
3
15.8
3
12.5
5
20.8
1
1.1
11
12.2
1
25.0
25.0
25.0
7
16.7
5
15.2
33
22.0
5
45.5
1
5.3
5
20.8
16
17.8
25.0
25.0
5
11.9
3
9.1
31
20.7
0
0.0
18
42.9
8
24.2
51
36.7
1
9.1
1
5.3
6
25.0
21
23.3
0.0
0.0
14
73.7
5
20.8
41
45.6
25.0
25.0
51
Table 30
Smoking standardized,, means and percentages of abnormal pulmonary function tests by job category
category
No identified asbestos exposure or garage work Garage employment but no brake work
Brake work
Body work Definite and possible
asbestos exposure
Mean value
100 x PFVC 95.7 - 1.2
91.3
1.5
96.9 0.7 92.9 - 2.4 96.1 - 1.1
abnormal
10.2 - 2.9 23.2 - 4.7 10.9 - 1.6
5.7 - 4.0 13.1 - 2.6
No identified asbestos exposure or garage work
Garage employment
but no brake work
Brake work
Body work
Definite and possible
asbestos exposure
100 ^ FEV PFEV
102.6 - 1.6
97.6 - 1.9
,
105.2 -0.8 97.6 -3.4
102.8 - 1.3
7.2 - 3.2
14.9 - 4.9
7.1 1.3 8.3 - 4.8 8.7 - 2.1
No identified asbestos exposure or garage work
100 x PMMF 95.1 - 3.5
31.6 -5.4 5.4
Garage employment but
no brake work
80.5 -3.6
49.5 7.5
Brake work
93.6 - 1.6
27.5 - 2.8
Body work
80.0 -8.8
46.6 - 13.5
Definite and possible
asbestos exposure
89.0 - 2.8
43.9 -5.2
1
Standardized to the smoking distribution of all with valid pulmonary function test Smokers 31.6 smokers 42.4 Nonsmokers 26.0
FEV PYTV 2
Abnormal is less than 80 for 100 x PFVC and 100 x and less than 75 for 100 x PHMF
52
diate values and those mechanic garage workers the lowest values The difference between the mechanic and mechanic garage workers is
significant at the 0.001 sided level See section on possible health effects of mechanic garage employment The same difference wag seen in auto body repair workers but because of the smaller
number of individuals it did not achieve significance at the 0.05 level 0.12
Possible effects from mechanic garage employment
For the principal three spirometric tests as well as for MMF PMMF
individuals with garage employment but who did not engage in brake
maintenance work had significantly lower means and a greater percent-
age of abnormal pulmonary function results than either controls brake
workers or those with possible exposure to asbestos otherwise We
. investigated whether this may be the result of the greater percentage
of blacks and Hispanics employed in this category compared to other job
activities coupled with improper pulmonary function standards for
these groups
Table 31 shows the percentage of individuals in the
various job categories according to their race As can be seen among
those with garage employment but no brake work more than 40 were
black or Hispanic compared to 28 of those with no identified asbestos
exposure and 16 of those who worked in brake maintenance and repair
To the extent possible we took into account the known differences
between black and white populations in the predicted standards for
forced vital capacity and forced expiratory volume in one second black
normals were 89 of those of whites For MMF the same prediction
parameters were used for blacks and whites as there appears little
racial difference in flow rates Schoenberg et al 1978 However
data on these standards are relatively limited and they may not be
fully accurate
For Hispanics we used the same criteria as for whites
Table 32 shows the overall spirometric data according to race As can
be seen the means for PFVC and FEV PFEV for the black
are generally lower than the white population in all smoking
population categories
The smoking standardized difference is significant at the 0.01 level
sided for PFVC On the other hand the data for the Hispanic
53
Table 31
The distribution and percentages by race
accordintgo the work activity of study participants
who had valid pulmonary function tests
Race
Type of work activity
No identified asbestos exposure or garage work
Garage employment
but no brake work Brake work
Body work
Identified and possible
asbestos exposure Totals
White
Black
89
76.1
63
58.9
19
16.2
40
37.4
356
83.4
24
75.0
177
88.9
709
86.3
56
13.1
6
18.7
19
9.5
140
17.0
Hispanic
9
7.7
4
3.7
15
3.5
2
6.3
3
1.5
33
4.0
54
Table 32
The means of spirometric tests by race
Race
White
Black1
|
Hispanic
Current smokers
93.0 222 91.2 53 96.9 9
Smoking history
smokers
100 x PFVC 97.4 300 89.9 51 94.4 17
Nonsmokers
99.6 187 96.5 36 81.6 7
Smoking standardized
96.6 92.0 91.9
White
Black,, Hispanic
96.2 220 98.4 53 105.0 9
100 FEV,PFEV
104.9 300
110.0 186
100.4 51
106.8 36
101.7 17
95.3 7
103.5 101.4 101.1
White Black
Hispanic
77.5 197 83.5 44 95.9
100 x MMF PMMF
92.7 248
102.9 144
89.8 40
95.5 24
94.1
113.3 5
90.6 89.3 99.7
PFEV 1 PFVC and
for blacks were 0.89 that for whites
2
Standardized to the smoking distribution of all with valid pulmonary function Lests Smokers 31.6 smokers 42.4 Nonsmokers 26.0
55
population is similar to that of whites with the exception of the nonsmoking group which is comprised of only six individuals Thus the use of the same prediction function for Hispanics as for whites would appear to be a correct procedure but the prediction correction
for blacks remains in question
Table 33 depicts the means of PFVC and whites by smoking history and job category
FEV
and
PFEV
Table
for blacks and
34 the smoking
standardized means by race and job category Too few Hispanics were
available for this analysis As can be seen the deficits for those
categorized as garage employees but who do no brake repair or mainten-
ance work exist for both racial groups However it is particularly
notable for the blacks where the means of PFVC and FEV PFEV1 for
brake garage workers are 10 lower than for blacks employed in other jobs The pulmonary function deficits in this group largely
account for the lower values seen for blacks overall in Table 32 and
suggest that proper normal spirometry parameters were used
The origin of these deficits is not clear The group is largely comprised of car jockeys auto polishers and new car preparation men There was considerable movement of individuals among these jobs and often a person would do all three They are employed in the same
facilities as the brake workers Also included are a small group of skilled mechanics who would perform difficult mechanical or electrical
repairs parts department personnel and a few men in DC 37 who were
dispatchers working out of the repair area Table 35 lists the spiro-
metric data for the three groups in commercial garages compared to those engaged in brake work those exposed to asbestos otherwise or the unexposed control group As can be seen the deficits are associ-
ated with the group working as car jockeys or car preparation men and
those employed in auto body shops
The differences in the smoking
standardized means for PFVC and FEV
vehicle preparation men and mechanics
PIEV , between the car jockeyincluding those who do brake
work are significant at 0.01 sided
56
aWNd/W
X
spirometric
standrized acording means race
96
OOT
tests
category
"88
T'L4968
9CF6C6 621F9
identfied 1.3 LC+L <OT - activtywork T 96.2 Ad d/
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garage work "Agr x
6 0
1.7 926" OF 940
86
SOT 66
1
<42S6 19FT06
Garage
employment employment
oot
but
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.
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O
0
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L6 6
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adky on aduzey4NG oyeIAg Apog
yom
PAaTYUopTSOJaqSE dansodxaa8e18 quawsoy93.9 ao dws 6 .1 - ysom OU
on a3vze4ANG ayeay Apoy
57
Table 34
Pulmonary function results of garage workers who do not
repair brakes according to work activity and smoking history
Pulmonary
function
parameter
Current Smoker
smokers
smokers
Mechanical Parts Department
PFVC
FEV PFEV
MMF / PMMF
88.8 3.4 98.8 4.3 106.1 14.7
105.3 1.4 110.7 6.5
80.7 7.5
95.2 100.1
12.1
Auto body repair work
PFVC
FEV PFEV1
MMF PMMF
93.0 2.8 95.9 5.5 82.3 8.8
92.8 96.9 15 71.4 11
92.9 4.5 100.6 6.5
91.3
New vehicle preparation jockey polisher
PFVC
FEV PFEV1
MMF PMMF
83.6 4.7 87.0 5.2 10.6
88.5 3.1 93.7 4.0 81.0 8.2
96.9 6.6 108.3 6.9
15.3
58
Table 35
Smoking standardized pulmonary function results of .
garage workers who do not repair brakes
compared to other groups
Job category
;
PFVC
No identified asbestos exposure or garage work
,
Brake work
102.6 96.9
Parts department Body work
97.5 92.9
Vehicle preparation car jockeys car polishers
Definite and possible asbestos exposure
89.1 2.6 96.1
FEF PFEV
102.6
105.2 104.2 3.5
97.6 95.4
102.8
MMF / PMMF
95.1
.
93.6 90.9 80.0 82.9
89.0
1 Standardized to the
ary function test
smokers 26.0
smoking distribution of all with valid pulmonSmokers 31.6 smokers 42.4 Non-
To the extent that occupational factors may be associated with these deficits the possibility exists that greater exposure to automobile
exhaust among individuals in this group has contributed to these find-
ings A greater exposure could arise if the mechanics generally worked on cars with engines off or if on with exhaust hoses attached That auto exhaust may be contributory is suggested by the data of Ayers et al 1973 who have observed significant pulmonary deficits among bridge and tunnel workers who are heavily exposed to automobile exhaust during the course of their work in the bridges and tunnels in and around New York City There deficits in forced vital capacity of %
for nonsmokers and 13 for smokers compared to a normal population
smoking not specified were seen Greater deficits were seen for various measures of airway flow The association of automobile exhaust with the deficits in pulmonary function among a limited group of garage workers is of course only suggestive For a definitive association
to be demonstrated it is necessary that a detailed study be made of the work activities and the exposures of this group of workers in order to determine if they do have significantly more exposure to auto exbaust than do garage mechanics
Auto body repair
Workers who were engaged in auto body repair had mean values for the various spirometric tests that were considerably lower than those of garage mechanics unexposed controls and even the groups exposed to asbestos otherwise Because of the few individuals in this group the
differences between the auto body workers and garage mechanics only
achieve sided statistical significance for PFEV
to asbestos and other dusts which could primarily affect
In
FVC
addition the auto
body shop workers are exposed to solvents from paints and fillers and
welding fumes The manifestations of disease seen in both the rays
and the pulmonary function tests in the limited populations observed in
this study warrant further definiation
Similarly an industrial
hygiene survey of the materials to which auto body repairmen are ex-
posed is also necessary
60
Correlations between ray abnormalities and pulmonary function tests
Table 36 lists three pulmonary function results accordintgo the ray reading of the individuals Two criteria were utilized for ray
abnormality a 1/0 or greater parenchymal reading and any pleural
change including the presence of diaphragmatic plaques and a 1/1 or
greater parenchymal reading and pleural thickening or calcification
The presence only of a diaphramatic plaque was not considered abnormal
in the latter criterion The results show that in general those with
abnormal rays have lower pulmonary function than those with normal
rays
This is evident for smokers and smokers
The pulmonary
function means for the nonsmokers however are the same for those with
abnormal rays as for those with normal rays
This is to be ex-
pected as minimal asbestos effects can be seen on ray before signi-
ficant deficits in FVC occur However even minimal asbestos effects
can be exacerbated by smoking leading to the deficits seen in Table
36. The data of Table 36 are consistent with the previous discussed
data suggesting a greater percentage of ray abnormalities among
"
current and previous smokers compared to nonsmokers
Also as ex-
pected the pulmonary deficits in those with abnormal rays are great-
er when the criteria for abnormality is more stringent
Comparisons with other populations
Table 37 provides a comparison between pulmonary function results measured in this study and those determined in a study of the general population of Michigan Miller et al 1980 For this comparison the mechanic garage workers are excluded because of factors that may be unique to that group The studies overlapped considerably in time and
the same technical personnel were used in each The field dates for
the Michigan survey were February 1978 through December 1979 and for this study May 1978 through February 1980. The purpose of the Michigan survey was to measure levels of polybrominated biphenyls in blood and adipose tissue and to evaluate other health indicators The group was chosen by a random selection process using Michigan phone numbers Predicted values utilized the regression equations for the data of
61
Spirometric
parameter
x 100
Table 36
The means
reading
of spirometric values according to ray
and smoking history using two criteria for ray abnormality
ray reading
Normal
1/0 Pl.Th.
Abnormal
or Pqs
Normal
Abnormal
1/1 or Pl.Th
PFVC
FEV PFEV1
MMF PMMF
92.7 176 97.2 175 80.3 152
Smokers
91.6 84 94.0 83 76.1 73
94.0 213 96.8 212 80.7 190
89.2 43 89.0 42 69.5 35
PFVC
FEV PFEV
MMF PMMF
97.2 264 105.2 264
92.4 216
92.4 81 98.7 81 89.4 62
PFVC
98.5 173
Nonsmokers 98.3 48
FEV PFEV1
MMF / PMMF
108.8 172 110.2 48 101.0 127 105.3 37
( ) = Number in category
98.1 299 104.1 299
91.6 243
90.1 43 96.1 43 91.3 34
99.8 191 108.5 190 101.9 144
99.2 24 108.6 24 107.6 17
62
Table 37
A with comparison of spirometric results in this cohort
with those observed in the general population of Michigan *
Smoking history
Observation group
This study excluding
mechanic garage
workers
Michigan general population
Blacks
Whites
Whites
Smokers smokers Nonsmokers
100 x PFVC
96.5
96.5 2.3
98.2
94.3 98.6 101.1
94.7 97.3 99.2
Smokers smokers Nonsmokers
100 ^ FEV1 PFEV
104.1
95.5
102.4
_
104.8
106.7
110.2
96.1 101.6 105.8
Smokers smokers Nonsmokers
100 x PMMF
90.2 90.8 98.9
76.5 95.5 106.6 2.6
80.5 88.2 97.6
* Predicted values were obtained from the data of Morris et al
63
Morris et al 1971 As can be seen the data for the whites in this
study compare very favorably with Michigan white males
Had the
mechanic garage workers been included mean values from % to %
lower would have been obtained c.f. Table 30
A variety of different research groups have produced regression equations for pulmonary function parameters on the basis of measurements on
normal populations The equations of Kory et al 1961 Cherniak and
Raber 1972 and Morris Koski and Johnson 1971 particularly have
gained widespread acceptance for comparative purposes The populations utilized and the criteria for acceptable data are shown in Table 38 for these three studies along with five others that have also established
regression equations for normal populations and this study As can be seen only two of these research groups included only nonsmokers in the
study group A third included individuals who smoked for less than six
months and one included individuals who were smokers of less than
pack years of cigarettes In some cases averages of best efforts
were utilized in others values for all parameters were taken from the flow volume curve of the best effort as determined by forced vital capacity Of most importance a considerable diversity exists in the age distributions of the study populations selected Values for FVC
and FEV increase until about age 25 then remain relatively unchanged
until about age 35 and thereafter declining steadily with age Because of this complexity regression equations based upon a wide range of ages and utilizing only a single linear term to account for age can be significantly in error The errors are such as to produce overestimates of pulmonary functions for young and older groups and underesti mates for those in the middle years see e.g. Schoenberg et al 1978 As the population in this study is largely between the ages of 40 and 70 most regression equations are likely to understate the values for these parameters Additionally lower predicted values will clearly be obtained from populations that include smokers or from
studies that include averages of several
the maximal ones
The use of standards
expiratory efforts rather from such populations can
than lead
to underestimates of effect from agents in the workplace that can affect pulmonary function
64
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In this study valid pulmonary function tests exist for 163 nonsmokers in other than the mechanic garage group The previous discussion
has indicated their pulmonary function parameters FVC FEV and MMF
compare favorably with the group studied by Morris Koski and Johnson It is instructive to utilize the regression equations from the above studies of normal populations to obtain other comparative data The various regression equations utilized are shown in Table 39 and the
percent ratios of observed to predicted spirometry parameters are
listed in Table 43. As can be seen the values obtained for PFVC
and FEV PFEV1 are in excess of 1.00 for all regression equations
This is the result of the inclusion of smokers among comparative groups
the use of averages of several efforts or the underprediction result-
ing from the broad age distributions utilized for the regression equa-
tions High values of FEV PFEV result in part from an extrapolated
origin of expiration c.f. Table 39 The values for PMMF FEF ~
PFEF 50
and 75 PFEF75 PFEF75
are
less
than
tions of Cherniak and Knudson This is
1.00 for the the result of
prediction equa-
their use of the
maximum flow value obtained in any effort rather than the flow in the effort with maximum FVC It is generally found that lower flow rates
are obtained during the achievement of a maximal FVC The Morris
Koski and Johnson equations would appear to give the best comparison
for FVC and MMF because a large proportion
above age 30 only nonsmokers were studied
of and
their population
the best effort
was was
utilized
The very complicated equation of Schoenberg which was
developed to properly take account of age is limited by the relatively
few individuals over age 30 and the use of averages of efforts
Regression equations for the various spirometric parameters obtained from data on the 163 white nonsmokers tested in this survey are listed in Table 41. Because only three individuals were under age 30 only the linear dependence on age could be established
PHYSICAL EXAMINATION RESULTS
Table 42 lists the number and percentage of abnormalities found on physical examination according to job category and organ system The only
66
Table 39
The parameters in regression equations for the prediction of spirometric functions in nine studies
Study
x Ht in
Morris et al Miller et al Cherniak & Raber Knudson et al Ferris et al Kory et al Bass Higgens & Keller
FVC
0.148 0.147
0.12102
0.1651 0.11684 0.13208 0.159 0.15748
x Age yrs
Constant
-0.025 -0.026 -0.01357 -0.029 -0.027 -0.022 -0.023 -0.024
-4.241 -4.053 -3.18373 -5.459 -2.79 -3.60 -5.72 -5.38
Morriest al
Miller et al Cherniak & Raber Knudson & Keller Ferris et al
Kory et al Higgens & Keller
FEV1
0.092 0.094 . 0.09107 0.13208 0.07366 0.09398 0.11684
-0.032
-0.032 -0.0232 -0.027 -0.028 -0.028 -0.028
-1.260 -1.426 -1.50723 -4.203 -0.70 -1.59 -3.18
Morris et al Miller et al Cherniak & Raber
Knudson et al Higgens & Keller
Cherniak & Raber Knudson et al Higgens & Keller
Michigan
Cherniak & Raber Knudson et al
Michigan
MMF
0.047 0.044 0.05948 0.1143 0.05588
FEF50 FEF50 0.06526 0.06526 0.069 0.069 0.0635 0.10255
FEF75
0.0903 0.044 0.0497
-0.045 -0.046 -0.037 -0.031 -0.044 -0.044
+2.513 +2.806 +2.61187 -1.864 +1.89
-0.03049 -0.03049 -0.015 -0.037 -0.0252
+2.40337 -5.4 +1.577
-1.1121
-0.01987
-0.012
-0.02895
+2.72554 +2.72554 -4.143
0.03562
67
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Table 41
Prediction equations determined for various spirometric parameters from 163 nonsmoking whites in this study
Parameters
FVC
FEV
MMF
FEF 50
FEF 75
Regression equation
0.0136 x Ht - 0.0267 x Age - 3.29 0.0858 x Ht - 0.0270 x Age - 0.792 0.0159 x Ht - 0.0289 x Age + 4.017 - 0.0033 x Ht - 0.0259 x Age + 6.124 0.0060 x Ht - 0.0196 x Age + 2.093
the R
0.43 0.43 0.09 0.04 0.12
No mechanical garage workers are included However there were no other exclusions based on health information.or job
69
Cyanosi503 examined (7) (7T) (9z) (et) exposure (1) ( <) (se) (OT) work (8) (90T)
59qSY Cyanosis extremites extremites extremites 9 9 8.7 8.7 10 8T 9.6 12 8 o @S
Go
Joints (ot) (ZE) {s7) (9%) 8.4 8.4 ) (28) 8.1 9 (TT) (62)
punoj Kazoseo ayeag Skin 0 9 zz 9 8 OOT 9S 11.5 11.5 ) $6T 18.4 23 $ 6 10.0
Gof
sefipmacuqe 2 a8eiey 02
ay yO
Thyroid (7) (6) (ez) (S$) 0.0 0.0 ) (Sz) 1.6 2 (8) (6S)
Thyroid Lymphatics Lymphatics 1 8 vst O 11.2 11.2 ) 2 02 0.0 0 2 92 8 9%
87
Sufpiose 18.7 =PEWeL zaqunu
PetsTIVpt Gastroineal,, pue
26
Dry (e) (6) (ct) (6) 17.3 17.3 ) (Iz) 9.3 10 (6) (7) 37 yIFA 9
Gastrointesinal,, Gastrointestinal,, Gastrointesinal,, Gastrointesinal,, 0 8 11.5 11.5 ) C stT 24.2 8 $*T de 11
uofFyepwxs ON
257
sejuid STeNpAuF Abdominal
TeoysdAu Fo
uosiedt syL
Number . wegsd^'s abAnormralitgy oe TeUWOP as=quny
peuexa Number sopaeydus indvuals us3i9
BqUpoL UtAS saky yznoy prozAy
352UD
FPA
(
Auy GY, )
70
circumstance in which a statistically significant greater percentage of abnormalities is found is for abnormal lymph glands among the popu-
lation serving as an unexposed control With the numbeorf subcate-
gories established in Table 42 such a finding would be expected on the basis of chance alone We attribute no significance to it
Table 43 shows the number and percentage of individuals with rales or finger clubbing according to their ray reading A greater percentage of individuals with abnormal rays have dry rales than do individuals with normal rays The numbers however are so small that the data do not achieve significance There was no correlation of finger clubbing with ray findings Overall rales were observed in 4.8 of the entire study group and clubbing in 2.6 compared to 25.2 with abnormal rays for 13.1 if more stringent ray reading criteria were utilized c.f. Table 11 Thus in contrast to earlier data from Great Britain
British Occupational Hygiene Committee 1968 it would appear that
the presence of ray abnormalities is a considerably more sensitive parameter than rales or restrictive pulmonary function deficits for the categorization of asbestos disease This has also been seen in several other asbestos groups including shipyard workers to be published and chemical or oil refinery maintenance employees Lilis et al 1980
Data for the blood pressures are shown in Table 44 according to age job category and race As can be seen the systolic and diastolic blood pressures of the blacks are significantly above those of the whites Systolic pressures increase from 5 to 7 percent per decade and diastolic from 2 to 3 percent each decade with the rates of increase being greater for blacks than whites The analyses of the age standardized blood pressures according to smoking history or job category are shown in Table 45. White cigarette smokers appear to have somewhat
lower blood pressures but this could be artifactual as it is not
reflected in blacks No significant differences are seen in the analysis of blood pressures according to work activity
71
Table 43
The
number and percentage ofindividuals with rales and finger clubbing
according to ray reading
Rales present
Clubbing present
Both rales and clubbing
present*
ray reading
Normal
Abnormal
30 4.3
17 6.9
16 2.6
6 2.7
3 0.5
1 0.5
The cases with both rales and clubbing in the separate categories as well
are
included
72
(T) (9) (OT) (2T) ( <)
Systolic Systolic Black presure pressure
9 % T'S 123.4
3.8
123.4 126.6
1.9
20 0
0ZT ZEZT 78ZT 128.0 128.0136.8 1.4
137.0 -3.0 3.0 B T
131.8 -2.5 2.5
+
134.0
.
134.0 134.0 -3.3 3.3 7 98
S3aANseid (Z)( <2()82) 152.2152.2 -
166.5 166.5 -6.8 6.8 12
standardized standardized < 135.4< 135.4 - 0.6 143.2 143.2 143.2 1.6 1.6 OS T T
standrized dinsead poTq 9Y
BoOBY yYoutg =
F F F
=
ade DT Diastolic 8
Diastolic Diastolic Diastolic pressure
F
+
pus
I;[oysep 29 presure eTqPL soe.
O'LET TET O'FET 76.2 76.2 - 1.8 Diastolic 75.5 75.5 -presure presure 0 68
)
pue fq
( <T)(49) ( <T8)3.1 83.1 - 90.4 90.4 -2.6 2.6 41
OT
BE 6 TT 7 85.8 85.8 - 0.8 93.3 93.3 -2.2 2.2 28 7 O0
[oysds Age F F 89.3 89.3 -
2.1
93.5 93.5 -5.0 5.0 12
+
ayy
standrized standrized O'8ZT 84.6 84.6 - 0.4 89.0 89.0 -1.1 1.1 768 948
pezTavus 6% 6 6% 6S 69
aay
-
-
-
-
-
0% OF OV OS O09 +02 asy
peztaurs 62 6 6<7 6S 69 -~-~ -
02 0 0<% 0S 09 +04 ady
73
Table 45
Age standardized systolic and diastolic
blood pressures accordintgo race smoking histaondrjy ob category
Race
Smoking history
White
Black
Smokers smokers Nonsmokers
Smokers smokers Nonsmokers
131.5 - 1.3 137.3 - 1.0 135.6 1.4
140.8 - 143.4 - 141.7 - 3.8
Diastolic
82.9 - 0.8
88.5 - 2.1
85.3 - 0.6
90.0 - 1.6
84.8 - 0.7
86.3 - 2.3
Job category
White
Black
No identified exposure
Garage work but
no brakes
Systolic
140.1 - 2.5
.150.4 - 5.3
136.1 - 2.7
139.4 - 4.0
Brake work
134.5 - 1.0
140.5 - 2.7
Asbestos exposure
135.5 1.4
.
149.6 - 5.2
No identified exposure
Diastolic
85.1 - 1.2
89.9 - 3.6
Garage work but
no brakes
85.5 1.3
87.8 - 1.5
Brake work Asbestos exposure
84.4 - 0.6 84.4 - 0.6
87.0 - 1.9 94.9 - 2.4
74
LABORATORY FINDINGS
The data on the blood analyses CBC and SMA are shown in Tables 46 and 47. No unusual findings are present for any parameter The means of the various parameters according to job category are listed in Table 48 and do not show anything remarkable Tables 49 and 50 show the results of the analysis of sputum specimens for abnormal cytology and the blood
analysis for carcinogenic embryonic antigen CEA They show no find-
ings suggestive of neoplasia most values are within the normal range Further there is no difference in the distribution of either parameter for the different job categories
MRC RESPIRATORY SYMPTOMS
The principal results of the respiratory symptoms questionnaire are shown in Tables 51 52 and 53. Tables 51 and 52 show the expected
correlation with cigarette smoking In Table 53 the smoking stand-
ardized percentages of chronic bronchitis and shortness of breath categories are listed for different job categories
NICKEL CONCENTRATIONS IN WELDERS
As part of a study to assess effects on welders plasma nickel concen-
trations were measured in twelve welders in the control group engaged
in amphibious vehicle construction The results are shown in Table 54 and indicate that the particular group within this study had higher nickel concentrations than a group of 62 welders in a large shipyard and ten times the concentration of hospital controls While no physiological effects can be associated with such concentrations the toxic and potentially carcinogenic effects of nickel would suggest identification of the exposure source and implementation of abatement measures
75 Table 46
The distribution of blood count values CBC Analysis
Range See headings
..
.. for concentration unit
Individuals within range
Number
Percentage
White blood cell count thousands 13.9-11.3
< 3.00 3.00 G 4.99 5.00 - 6.99 7.00 - 8.99 9.00 -10.99
11.00
1 70 342 308 124 39
0.1 7.9 38.7 34.9 14.0 3.1
Red blood cell count millions
< 4.25 4.25 - 4.74 4.75 - 5.24 5.25 - 5.74
,
5.75 - 6.24
> 6.25
S 130 462
.
228
34 12
4.3-6.3
2.0 14.7 52.3 25.8
3.8 1.4
13.0
13.0 - 13.9
14.0 - 14.9
15.0 16.0 -
15.9 16.9
17.0 - 17.9
> 18.0
Hemoglobin gm
12 54 237 335 186 54
6
12.9-18.12.29-18.2
1.4 6.1 26.8 37.9 21.0 6.1 0.7
37.5 37.5-39.9 37.5-39.9 40.0 -42.4
42.5-44.9 42.5-44.9 45.0 -47.4 47.5 -49.9 50.0 -52.4
52.5
Hematocrit percent
4 13 92 245 308 154 53 15
38.9-54.9
0.5 1.4 10.4 27.7 34.8 17.4 6.0 1.7
] = Laboratory normal rance
76 Table 47
The distribution of concentrations of various blood components SMA Analysis
Range
See headings for
~
concentration unit
Within range
Number
Percentage
Glucose mg 65-125
< 80 80 - 99 100 - 119 120 - 139 140 - 159
160
46 415 294
61 25 47
nitrogen dl 8-25
< 10 10 - 14 15 - 19 20 - 24
> 25
44 250 420 150
22
5.0 46.8 33.2
6.9 2.8 3.5
5.0 28.2 47.4 16.9
2.5
Creatinine mg 0.7-1.5
< 0.80 0.80 - 0.99 1.00 - 1.19 1.20 - 1.39 1.40 - 1.59
> 1.60
5
113
339
315
:
89
22
0.6 12.8 38.4 35.6 10.0
2.5
Sodium meq 135-145
< 138 138 - 139 140 - 141 142 - 143 144 - 145 146 - 147
> 148
14 102 234 237 125
76 98
Potassium meg 3.5-5.0
< 3.00 3.00 - 3.49 3.50 - 3.99 4.00 - 4.49 4.50 - 4.99
> 5.00
5
38
222 .
451
.
209
56
1.6 11.5 26.4 26.7 14.1
8.6 11.1
0.6 4.3 25.2 39.8 23.7 6.2
Table 47 continued 2
Range See headings for concentration unit
Within range
Number
Percentage
Chloride meq 95-107
< 100 100.0 - 102.4 102.5 - 104.9 105.0 1 107.4 107.5 ~ 109.9
> 110.0
50 215 212 229
88 92
Carbon dioxide meg 24-32
< 25.0 25.0 - 27.4 27.5 - 29.9 30.0 - 32.4
> 32.5
39 238 310 244
55
Uric acid mg 3.5-9.0
24
4.0
6.0
8.0 8.0 9.9> 9.910.0
376 392
88 6
Calcium mg 8.5-10.5
9.0
1.0 9.0 >
9.9 10.9 10.9 11.0 11.0
16 510 340
17
Inorganic phosphate mg 12.0-4.5
<
2.00 2.50 3.00 3.50 -
2
2.00 2.49 2.99 3.49 3.99 4.00
16
134
15.1 15.1
37.4 331
280
37.4 37.4 31.6
10.4 92
10.4
33
Total protein dl 6.0-8.5
< 6.50 6.50 - 6.90 7.00 - 7.49 7.50 -7.99 -7.99 8.00 - 8.49
8.50
26 197 401 197
55 7
2.9 2.9
2.3 22.3
45.445.
45.4 45.4
22.3 22.3
0.8 0.8
Table 47 continued
Range . See headings for concentration unit
Within
Within range
Number
Percentage
Albumin dl 3.0-5.5
3.50 - 3.99 4.00 - 4.49 4.50 - 4.99 5.00 - 5.49
18 439 398
29
2.0 49.7 45.0
3.3
Cholesterol mg 140-330
< 150 150 - 174 175 - 199 200 - 249 250 - 299
300
13 66 162 443 178 24
1.5 7.4 18.3 50.0 20.1 2.7
Creatine phosphokinase U 0-225
< 50 50 - 74 75 - 99 100 - 149 150 - 199 200 - 249 250 - 299
$ 300
52 162 196 258 104
49 22 43
5.9 18.3 22.1 29.0 11.7
5.6 2.5
4.9
719
oT O 0 O800 c O6 t <100 O 2 070 O c O z 06090 <O0 <0O00 020 O 972 c0 0 T ? 6 0 9 70 O'o bib
pue
+ + + += ++F++ +++ + ++
+ >++= F
BTQyso5 einsodx 3 asqyutjag soq s cs7^'Ot*s fest es#oet $9TCUT TeT Table COT687oT 9^'2668CGara eye ZS7% <C0ckd 10z 602 6TLT LTt
@
SUOFIEWZGS &208a 382 qof
puw os
ey sajowusdSuypricz28
fiTqIeL alu
unos
po[q ouedwos
jo POTQ
soenTeA snoyaB
uUs U
ay}
identifed identifed so o 10 B T 2 O TO O z 020 0 f'0 TO UO020 0 cO O 2O O 10 O 6 T 1070 g T 709 O 0 2L 9
identified identified + + + + Garage Garage Garage employment employment employment employment = + + + + + % + +
exposure
.
garage -0.20 0.20 09 670T Zot7.14 7.14 T2 4TSOT 882 0.19 0.19 0.19 627% Ly9 <2z7.40 7.40 ote <*2z-0.09
-0.01 1.18 -0.5 0.01 $0 O0 0 16.2 0.01 t 07 $ 015.7 1.18 9 0 C0
C o t -0.2
1.15 t+ -0.3 0.3 + + F 143.5 143.5 + + + -0.4 + + = 143.4 143.4
+
-0.2
Yalow4.24
142.1103.6 3yHvIQ 0.3
28.1 -0.12 0.12 c sOIT dest 28.5 6.42 6.42 ZSOT $ 8e -0.14 0.14 6E%17) 2C228.8 6.43 $6T S22 -0.17
0.58
yaom
72.5 19.6168.9 v8e203
-2.8 2.8 22.7 4.41 -3.6 0.03 90 O Z0 O 22.2 Ott
270% 971s -0.03 0.03 + +
222.7 c o c 0
222.2 222.2
F 0.57 0.57 = + -0.03 0.03 + + + 0.59 0.59
che -1.9
aes -0.01
22.5
-5.6
5.6
9
94
6
01
a
ST
17
.7
13
.8
177.7
9
fOT
1
82
-3.6
8
?
ord
0$
7 177.9
133.1
17
.9
17
.9
9
6T
Lez
-2.0
*Ado>
orp
peenaqepe
aevydso esvuaopAyasvuTHoUdy ayedsoy FUND VUNOD
4adUsied Pod VpaO udtoayu UR BPTXOTp LOnB
Ag
podey1599
BUPTIGAD syur3sou, puortg arzuy4 pPonrylyy yUPQyg Opon VUE, vseurg wo2} pwoasy FSEUICY ePTIOUD uoyrzeg PStTaOnR enpILeG poqo8sgupTenyge[O3U2D9 tSyQiPaayC suyreiy Ad9S $085 o3ryory auTIWs95
80
66T-St (0'0) 0 Table Table 49 0(0 90) if(1'0)
distribution
(
The {uwdistribution acording T acording T category i category (v< 0) =
99
6
/wsouen)6-6
3
cytology
Spu< tum S cytology 41 cytology 9 (t' <) 82 (ee)
~~
Category =6(<96) (796) ( < (0
(<
YA
>
LOT
26)
etl $6)
617 96)
HQT
<28
garage
67 brakes work
ra
<
T
9
0 21 (9) ($T) (ZT) )
0.0
,
work
repair with FTqPL work
c ot 34.0 3 ( 6 (<$61) 3 ( < <Z) 419
0.2 =
Identifed ) Identifed
posible
@
( (Ove) (2 32
a4
)
37.2
)
1
)
96.3
0.5
yo ~ s = = ou
(0Sy) ) 0.4 (9 (9
(7
T
Lt
%Z
06
143 (
6
)
823
ersjdhpJo
Totals ) aTqtsod percentages
IO
atyse[dqow atypia considerd
20 eqpd^'qe
atypia normal ASoTORAD no
normal
etdqe
sagequoiad atypia considerd considerd
dysplasi ajerpoyzepneoy dysplasi sayeig OF
ST = JewsroN pity
patyrzuapy soq se sozqse gor on aserey ou ere axe1q
(
PIO]
) fy 7oc y
81
66I-Sl
0 (0 0)
t Table
0 (0
0)
6
distribution
distrbution /w2 = 6
distrbuionYY) ouew)6S
according acording to cytology smoking results Sputum Sputum cytology cytology 9 ( %)
Category (2 <6) 3 4
Category
1 2 6S < Slz 6)
pue
Azodayeo smokers smokers Suryous Nonsmokers ASOTYAD Nonsmokers 03
) 22.6 1.1 36.7
39.5
22.6
(
< 04 . cz 24.8 ZI 2.8
34.0
umyndssutpz0doe
waQNdS
z
(87) (6
OL
64
6)
(O2 ve)
Jo
146
77
percntages 41.0
37.3 37.3
19.7
19.7
( 1.8
Regular
dysplasi
BuTyoug SIBYOUS xS19xOyUws SADYOWSUN
I (1'0)
conetr< aions
82 (ee)
< ( <96)
93.2
93.2
0.8
0.3 LL 97.8 97.3
941 (ELE) 0.0
822
3
96.3 96.3 0.4 etsdsp 0.4 40
ABoTOYADaTyserdyaw ao etd^'je
sagequ
ciad
Tewsi0onN
azeynsay
erdAye
pripn
ajer
poy
=
STRIO]
(
) T 7* < y
83
Table 52
The number and percentage of individuals
reporting symptoms of chronic bronchitis MRC
accordintgo smoking category
Chronic bronchitis Yes No
Totals
Smoking category
Smokers
smokers
smokers
80
29.1
195
70.9
275
34 9.5
325
90.5
359
21
9.5
199 90.5
220
84
pez number
reporting number symptos
reporting
Category
Category garage or garage
smoking standraized standraized percentage acording
Non
Bt/L ($2)
L7/2(9 20/68
Ex 12/56
Os/s (0
OT)
L/T7/28
Gargeasbetos 9S/7zT(T9Z)
19.4 )
98T/0% 20/186
) (9 TT)
cT/t 7.4
eg
repair sADHoOWS-xXq eTder
.
Garge Identifed
posible
posible (R62)
92T/0% 40.6 28/69 10/88 ) 11.4
10/8 (904) zt/s 10.0
body
Auto
pue suoqdus Ao )
a8equoiad percntage1
yAOn sanodxa qnq YafA pue aInsodxa yom
suzy
k108.e)
edvATs
RAO yao ayedez soyxeAg
Lpoq =
psTIUopT gor oN soqase |VsBAavy ou advary29281q soqjase o3ny
( )
85
Tabl5e4
Nickel concentrations in the plasma of amphibious
vehicle construction welders compared to other groups
Group Vehicle welders
Shipyard welders Hospital controls
No. of individuals
12 62 15
'
Plasma nickel concentrations
liter
Median
Range
Mean
SD
11.8 2.5 0.7
5.4 te 14.3
0.5 - 15.3
-
0.5
2.6
10.8 - 3.2
3.1 - 3.3
1.0
0.7
ASBESTOS EXPOSURE DATA
REVIEW OF PUBLISHED RESULTS
Review of fiber concentration data for brake work
A variety of measurements have been made of asbestos air concentrations during brake lining repair and maintenance activities in the United States and Great Britain These include both term sampling over a working day to obtain information on weighted average exposures to workers and short sampling to document the concentrations during various work practices
The largest set of samples of brake maintenance work is that obtained
by NIOSH during the years 1975 through 1976 where 283 samples were
taken in five brake repair facilities including 152 over a one week
period in one facility documenting both term weighted
average TWA exposures and asbestos concentrations in specific brake
repair activities NIOSH 1972-1976 Unfortunately no documentation
exists as to the number of brake jobs performed in a facility or by
workmen during sampling periods or on the work practices utilized
during the repair and maintenance work
Table 55 summarizes the data
on weighted exposures over a sampling period for men changing
lining material punching out rivets riveting linings to shoes and
working in the parts department Table 56 lists general area samples
taken during the course of a day
These data demonstrate that iu
general the term asbestos exposures of garage employees are below
0.5 ml However during the air blowing of drums punching out of
rivets and riveting asbestos concentrations can be considerably higher
Further area samples taken distant from the location of brake repair
show widespread dissemination of airborne asbestos with concentrations
up to 1.3 ml found to be present
More limited date are available from industry sources
In Great Bri-
tain lickish and Knight 1570 of the Ford Motor Company Lave provid-
ed information on both long and short sampling during different
87
Number
Number 60 0 repair and maintenace
work
92
0
Te T OT'O 2 0
Garge
poyied
Sojsqye (Tw
SUJUT B197619761976 ;
BxeIG YAOM 1976
.
FO D A S[CpAo
SJPOAF uBR STeyjoq
ss
OueojzyPTWeL Suf[dues
E
) JIUpUPY] 89T~S0"O 2 rama) 4700 0.4 0.2-0.3 LePr-T2e JRO Z2SL-SE0 Szazg Te'T 9TO~-<0 SuTUpY zo (eRep
pues
poysFTqndu JTruoszdaprdz A Suysry9
SuPysung
SuPsepTday
Jo
wasq~Juoy
soTdues
A
fo
T@ S
Punching
Punching
out
Zz
Zz
T
S
t
| 9/61-ST)
FO
satdurs 9T TZ
<%
@
9T
TT
T eT Z HSOIN
A
(9267) 5 (9261) (Sl6T) 1.21
(2L61) <swory
B
V
@
9
@
@
Vv
@
a
88
Number
Garge
Boucjrvu (Tu/sroqt)SoOJsqepofaed
SUFUT AZutdwes
OxvVIq YAOM 1976
jo B
9
=8TIPL Bupldues C ) pur wore aredsz F wiej-Fuoz F1972 From From ,
Jo
2eqUnN seTdurs
aSvas9
repair repair maintenace maintenace maintenance average
,
18
teay 7<T-<0 T0-TO 400 0.04 T0O 6*0-90 Ceaup
poystrqndu [Tersuy |
8T 9
T
T
T
a
*9/61-Z2) O& 66 % T T
HSOIN
(9261) (9461) (9261) ($261) (9461) (261)
V
9
a
4
4
wor
89
cirumstanceIO
sucop total
sampling
ayeaq Asbetos fibers conetraions conetraions
Staic SAPIG samples is TT samples yonz3 Range *TIUy yonag DEAIOS fibers Meansfeq
C
Static
BOUCITFEM9YvIQ 3Snp cloud
byuNap
SUyANp Jc
Personal
LS sSuoftSuzMOTG soyeqsy cleaning
3TqeL eajuso Ate yo Jeqyjy BSufAToOu Jequny Personal
Staicwoysads so0yArzos guy[ducs
Static
samples
Sta
ic
wisj-Suc7
FromSut
Tdurs
car sz 89 O
60 L
oT
brake Z9E-TL
T-8e
"0
60 L
Z
z
9
I
weighted
average
above
samples
ae2
Hickish ,
E. asnp
L. dyxvIq Knight
Ann
apts
oT3219
,
ze.
97325 pnojys
L. Knight KnightKnight
An
fq
fq
uo
changes
800 <8 TST"
"
CT
vehicles
800 0.68 serviced
SaTdurs truck
incl omy
T
9
. oA0de
truck
JO
service
cleaning
OO B8rzvaP 1.83 nearby
nearby
aTduvs pozyston 17-21 bays ,
Hyg BF4uAqS 1970 swo2z
brake repair activities These are shown in Table 57. The work prac-
tices sampled by Hickish and Knight appeared typical of those of past years with the drum dust being removed by air blowing During the full
course of brake service air concentrations of from 0.4 to 3.6 ml were
found More recent information has been supplied by Manhattan
Marsh 1979 These show that during the course of well ~ controlled
brake repair work with exhaust ventilation utilized asbestos exposures of 0.02 to 0.3 ml may occur during the course of a brake job
Short asbestos concentrations during specific work activities have been measured by several groups in both automotive and truck servicing
These are shown in Table 58
They demonstrate that short asbestos concentrations during brake maintenance work can be high However because they comprise only a portion of the work involved in brake maintenance the TWA concentrations are generally much lower Clearly reduction of these peak exposures by engineering controls or by work practices can significantly
reduce THA exposures
Two sets of data on the time course of asbestos concentrations exist The measurements of total dust by Lee indicate that after air blowing short dust concentrations are high but fall within minutes to lower values The data on fiber counts by Rohl4 indicate that measurable concentrations of asbestos persists in the workplace for as long as 15 minutes after air blowing as far as 75 feet away These data
coupled with the previous information on asbestos concentrations in general garage areas indicate that a general level background contamination of asbestos can exist throughout a garage where brake repair is conducted
MEASUREMENTS IN NEW YORK CITY FACILITIES 1979
During 1979 NIOSHI made measurement at three New York City facilities employing workers who attended examinations in this survey These were the repair shops of the Departments of Sanitation Transpolation and Police The results are shown in Table 59. They are similar to those
91
Activy (Tu Activity uoT3.
UBD.
STFGOWoIHe
Air
blowing
fromblowing
GUPANp SOPFIAOLY Brushing
drums
GrindgGrinding
BOULVTRWgc Grindg linings
SUoTPJejIDeTIeL BYCAG suyinp porexhaust
Sojsaye BONA Bevling
fo pue Riveting
Aqewuns Sweping
cleanig
~ wo
NIOSH Knight
1972-76
ml
ml
Om wo
e le
samples
samples
aT 0.45-14W .O 5W 4
Nn
Zz
.
Marsh Marsh 8 1979 1979 0-20 0.2-0.4 0.2-0.4 VT-B%S*TZ-70 OZL-E 02-6T 9E-7's |
Rohl
Rohl
Rohl
et
1976 1976
39
1976
Rohl Rohl et , 1976
23.7-2.0 9L6T 9161 9/61
1.9-2.0 1.9-2.0 6461 Te Te *T@
1.9-2.0
33
38
2.4-3.6 2.4-3.6 UsIeH THON [HOY TYyoY
33
yO SNYXSssneyxs
pue
BauypMyoTqwAoslnzp sunap Zupsnagywsonrpj swnap pBuzuayyS3UTT poos r0d TSOAUOgP SUTIAFY SuzdonsSuypUBIaTo
92
Table 59
Long and short sampling of brake lining repair
and maintenance work in New York City garage facilities
Activity
Sampling
time
fiber concentration
Sample
TWA
rl
Brake change After finishing Wet brushing of Area sample Area sample
job
dust
Department of Sanitation
136 190
10 395 390
0.33 0.12 0.54 0.06 0.05
Department of Transporation
Brake mechanic 1
Brake mechanic 2
Brake mechanic 3
Wet brushing of dust mechanics 1,2,3
150 196 175 194 135
3 3 9
0.15 0.30 0.31 0.26 0.24
2.62 2.22 0.87
0.21 0.21
0.23 0.23 0.28 0.28
;
Brake mechanic 1
Brake mechanic 2
Brake mechanic 3
Dry brushing of dust
Police Department
129 68
124 177
47 12 21
0.20 0.21 0.34 0.08 0.03 0.81 0.61
0.20 0.20 0.19 0.19
93
discussed previously TWA exposures during a full brake job averaged
about 0.20 ml
During either wet or dry brushing of brake dust
concentrations could exceed 2 ml
ESTIMATES OF STUDY POPULATION EXPOSURE
TWA exposures during automobile brake maintenance ranged generally be-
tween 0.2 to 0.7 ml if brushing or air blowing of brake dust occurred
Prior to 1950 riveted brake linings were used and somewhat higher
concentrations may have occurred Table 60 lists the distribution of
brake jobs per week done by U.A.W. Local 259 members The average is
about one every two days for those who do brake work If the exposure
during the 1-2 hours required for a job is 1 ml an approximate TWA
exposure would be 1 ml 1.5 or about 0.1 ml
General garage
exposure from other jobs would add slightly to this but the upper
limit of the average exposure for the commercial garage mechanics
examined in this study would be 0.2 ml For the S.E.I.U. Local 246
mechanics employed by the City higher average exposures would have
occurred from the riveting drilling and grinding that was done on
large truck brake assemblies However these high exposure work acti-
vities would only require a few minutes of work As with commercial
garage workers few City employees worked on a brake job as often as
daily Thus even with the intermittently higher exposures experienced
by S.E.I.U. members the average exposure for the group over time is
unlikely to exceed 0.5 ml
SUMMARY
The clinical examination of garage employees engaged in the repair and maintenance of vehicles indicate the following results
1
A greater prevalence of ray abnormalities is found among garage
mechanics who repaired brakes than among blue collar controls or
garage workers who do not engage in brake or auto body work The
age standardized percentage of abnormalities is significantly
gleator
0.05
in
those
with
30
or
wire
years
of
employment
jo
AtoNuyxsIq ory oujeox0g now 1-4 week 9T z LZ -OOT
Jo sdous JO
AQuoNbyxz SOABWTSTruosan 09 66% azqunay udu
8TICL TRI0T Jo mM sqof VA UT o7e1q
no brake work % parts :
Lt
sjaed
@20W yquo/T 470M (939
uoTtAngy24stq sopuryou yquow/c- Jo
20
yaoa/
Teuosad zequny ouop Acp/T 7-1
usyQ O7yUAQG
ssaz oubuyzsu) STBROL
T
95
compared to workers with lesser service The increased prevalence in commercial garage workers exposed on average to less than 0.2 ml was not statistically significant while a significant excess is seen in workers who had occasion to grind and machine brake linings prior to installation on larger vehicles The prevalence of ray abnormalities is in accord with estimates of asbestos
exposure in the different circumstances
The prevalence of ray abnormalities among workers in auto body shops was particularly high and although the number of such individuals was limited also achieved a level of significance at 0.05 The higher percentage of abnormalities in this group can be attributed to the past sanding of auto body fillers containing
asbestos
Individuals who had previous employment in shipyards averaging five years in duration also had a greater percentage of abnormal rays The percentage age standardized percentage was significantly greater in those whose shipyard employment began 30 or more years previously
The pulmonary function results of garage mechanics engaged in
brake work are no different from garage workers and other
general population controls As the major spirometric tests are less sensitive measures of asbestos exposure than rays this finding is in accord with the low exposures of the groups under study
Car jockeys new vehicle preparation men and auto body shop work-
ers have significantly
FEV and MMF compared
lation controls
reduced pulmonary function
to other garage workers and
tests FVC
general popu-
The auto body shop employees had exposure to asbestos and 3 Var-
iety of solvents The causal exposure among the car vehicle
preparation men is uncertain
The role of automobile exhaust
should be investigated
96
Pulmonary function deficits correlated with ray abnormalities Greater percentages of ray abnormalities and pulmonary function
deficits were seen among current and former smokers than among smokers
No unusual physical examination of laboratory findings were identified As in other studies a high prevalence of hypertension was observed among blacks which was not correlated with any job category
A small group of welderisn amphibious vehicle construction showed
significantly elevated plasma concentrations of nickel
97
REFERENCES
Anderson H.A. Lilis
I.J. Household
311-323 1976
R. Daum S.M. Fischbein A.S. and asbestos neoplastic risk Ann N.Y.
Selikoff
Acad Sci
Ayres S.M. Evans R. Licht D. Griesbach J. Reimold F. Ferrand
E. and Criscitiello A.
Health effects of expsoure to high concentra-
tions of automotive emissions Arch Envir Health 168-178 1973
Bass H. The flow volume loop normal standards and abnormalities in
chronic obstructive pulmonary - diseaCs hee st 171-176 1973
British Occupational Hygiene Society Hygiene asbestos dust Ann Occup Hyg 47-69
standard
for
chrysotile
Bureau of 1909-1978 ton D.C.
Labor Statistics Employment and
BLS Bulletin 1312-11 Government 1979
earnings United States Printing Office Washing-
Cherniak R.M. and Raber tion using an automated 38-46 1972
M.F. Normal standards for ventilatory funcwedge spirometer Am Rev. Respir Dis
Ferris B.D. Anderson D.O. and Zickmantel screening tests of pulmonary function Amer
1965
R. Prediction values for
Rev. Resp Dis 252-261
Glover J.R. Bevan Lowe C. McDermott
dust in North Wales
C. Cotes J. Elwood P. Hodges N. Kell R. M. and Oldham P. Effects of exposure to slate Brit J. Indus Med 152-162 1980
Greenberg M. and Davies T.A. Brit J. Indus Med 91-104 1974
Mesothelioma Register 1967-1968
Hammond cigarette
1979
E.C. Selikoff I.J. and smoking and death rates
Seidman
Ann N.Y.
H.
Asbestos exposure
Acad Sci 473-490
Hickish D.E. and Knight K.L. Exposure to maintenance Ann Occup Hyg 17-21 1970
asbestos
during brake
Higgins M.W. and Keller J.B.
Seven measures of ventilatory lung
function
Population values and a comparison of their ability to
discriminate between persons with and without chronic respiratory
symptoms and disease Tecumset Michigan
Am Rev. Respir Dis
258-272 1973
Knight M.L. and Hickish D.E. Investigations into alternative forms of control for dust generated during the cleaning of brake assemblies and drums Ann Occ Hyg 37-39 1970
98
wy
Knudson R.J. mal expiratory
effects of age
Slatin R.C. Lebowitz M.D. and Burrows B. The maxivolume curve Normal standards variability and
Am Rev. Respir Dis 587-600 1976
Kory R.C. Callahan R. Boren Administration Cooperative Clinical Spiromety in Normal Man
H.G. and Snyer J.D. The Veterans
Study of Pulmonary Function
I.
Am J. Med 243-258 1961
Lee G.L.
Removing dust from brake assemblies during servicing -
alternative cleaning methods Ann Occ Hyg 33-36 1970
Lilis R. Daum S. Anderson H. Andrews G. and Selikoff I.J.
Asbestosis among maintenance workers in the chemical industry and in
oil refinery workers In J.C. Wagner and W. Davis eds Biological
Effects of Mineral Fibres
'
IARC Scientific Pub No. 30 Lyon pp
795-810 1980
Lorimer W.V. Rohl A.N. Miller A. .J Asbestos exposure of brake repair Mt. Sinai J. Med 207-218 1976
Nicholson
workers in
W.J. and Selikoff
the United States
Marsh J. | Unpublished data
Personal Communication 1979
of Manhattan Corporation
Miller A. Thornton J.C. Smith H. and Morris J.F. Spirometric abnormality in a normal male reference population further analysis of the 1971 Oregon study Am J. Indus Med 55-68 1980
Morris healthy
J.R. Koski A. and nonsmoking adults
Johnson L.D. Spirometric standards for Am Rev. Respr Dis 57-67 1971
National Institute for Occupational Safety and Health 1972-1976
Personal Communication Ralph Zumwalde
-
-"
National Institute for Occupational Safety and Health
Industrial
Hygiene Survey Report of the New York City Sanitation Traffic and Police Brake Servicing Facilities Queens New York Cinciunati Ohio
May 12 1979
Nicholson W.J. Perkel G. and to asbestos population at risk Am J. Ind Med 259-311 1982
Selikoff I.J. Occupational exposure and projected mortality - 1980-2030
-
Rohl
sure
A.N. Langer A.M. Wolff M.S. and during brake lining maintenance
110-128 1976
Weisman Il and repair
Asbestos Envir
expoRes
Rossiter C.E. and Harries Study survey of the sample Indus Med 281-291 1979
P.G.
U.K. Naval Dockyards Asbestosis
population aged 50-59 years Brit J.
Rossiter C.E.
Initial repeatability trials of
Classification of the radiographic appearances
Brit J. Industr Med 407-419 1972
the Cincinnati c^> pneumoconiones
99
Schoenberg J.B. Beck G.J. and Bouhuys A. Growth and decay of pulmonary function in healthy blacks and whites Respir Physiol
367-393 1978
Selikoff I.J. Nicholson W.J. and Lilis R. Radiological evidence of
asbestos disease among ship repair workers Amer J. Indus Med
9-22 1980
Weiss W. Levin R. and Goodman L. Pleural plaques and cigarette
smoking in asbestos workers J. Occup Med 427-430 1981
Weiss W. Cigarette smoking asbestos and pulmonary fibrosis
Rev. Respir Dis 223-227 1971
Amer
100 APPENDIX I
-.
Name
101
BRAKE REPAIR AND MAINTENANCE WORKERS SURVEY
Date
No.
Union Local :
Address Telephone
Street
Carage Facility
City
Date of Birth
State Age
ZIF Sex
Name of Physician optional
.
Address
URINE
Albumin Albumin
ce
Protein
ENVIRONMENTAL SCIENOIS LABORATO ENVIRONMENTAL
ENVIRONMENTAL ENVIRONMENTAL
SCIENOIS SCIENOIS
LABORATO
LABORATO MORN MORN
MORN MORN
MOUNT SCHOOL OF MEDICINE OF THE CITYCITY UNIVERSITY OF NEW YORK
AE
a
owen He
ST RENE Ua aad OTROS ABN TY AY ABE OT Oe
Oem
een
8
Mee
ace
OA
verke
yIuoay
V. ,
V.
V. V.
svanodxi
V.V. V.
sae
SUDAUON V.
aovuo V.
V.=
V.
ANOLSIN V. V. V.
V. V.
V.
AVNOTEYIDO wuOM
V.HOLAID
aNy nor
TAVUH
TULYosSud) wOoTrL
1 POTdIY O1/aoug
3anqoudsiunvare
}
1
iv
ON
10
20 M
ESVUO
NVI
MWuosrs
WAHL
2J9O
--
TNAO WOlNLOUILS3S0 7S
LIRA
SROTADUd .
NOLAVISEDdUOA JO
=| senc
yo fem
-Je ouay adh, opus,
ce}e
{|
pourOL
ng o
|
A
= 3]
:
es
Se
.
ra
4
1
'
va .
.
;
10)
GlavouG
wTyjuod eens
oem
orem
yyy
.
~~ GozyaTSY
co
chalet
-
|
me
e
{mee
ame
rf
Ren
TuNopyedansw
2 12
;
f
Last
First
Year first exposed to asbestos occupationally
Year last exposed to asbestos occupationally
Total
number of years
-subtract -subtract -subtract
and months exposed to asbestos
exposent
# yrs dising period not exposenet xpHosOent
Dates employed as Garage forker
]
YR
orclutch orclutch
Work
Dates performing brake Work
D
Datas performing undercosting
|
|
i|
| 11
123 115
6 6 6to 6 to to to
i dus | 27
25 25
|
<3
1
} j { ^'
| f | Jes
Exposed to other dusts
1-30
Yes
3
If F29 Silica
Year first exposed
Year last exposed
Total number of years and months exposed
rd
Coal
. Year first exposed Year last exposed
Total amber of years and months exposed Total years underground
Year first exposed
Your last exposed
Total number of years and months exposed
stor
stor
to becoming a
garage Forte did
mediate family work withwith asbestos
any member of your
No
2-7
:
: Nes who
and employed
as
from from AM
-
Lenplaegt=a | 4 / An }
c nat
<0
Geant coe
bi a ite
i
;
Yi
{
Reproduced
best
copy Reproduced from
available
GD
34 34 36 36
fi,
to |
... bey
ta (1 /AY ; las
175
RESPIRATORY QUESTIONNAIZE
Last
First
Middle initial
I am now like you
going to ask you some questions to answer YES or NO whenever
mainly about possible
your
chest
I would
COUGH
.
Do you usually cough first thing in the morning on getting up
Count a cough with first smoke or on first going out of doors
Exclude clearing throat or a single cough 1 - No
2 - Yes
2
Do you usually cough during the day or at night
Ignore an occasional cough
1 No
2 - Yes
3
12 yes Do you cough like this on most days
or nights for as much as three months each year
No
2 - Yes
Have you 1
2
been coughing like this
- less than two years
-
more
than
two
years
PHLEC
Do you usually bring up any phlegm morning on getting up
Count phiegs with first smoke Exclude phlegm from the nose Count swallowed phlegn
from your chest first
or on first going out
i
No
thing in the
of doors 2 - Yes
5
Do you usually bring up any phlegm from your chest during the day
or at night
1 No
2 - Yes
6
.
+
If yes Do you bring up phlegm like this on most days
or nights for as much as three months each year
1 - No
2 - Yes
Have you
2 2
done so for
- less than
-
more than
two two
years years
What color is your sputum or phlegm
1
- whitish
2 3
- yellow and green - grey and black
4
- brown
Column Number * For night shift employees
12
] ]
15 15
16
17 17 18
19
Use of air hoses to blow out brake shoes Which years done
did you bevel or machine shoes
Which years done
What current dust removal practice is used during brake or clutch jobs at your garage
When did this begin What was done before
Did you do undercoating work or were you near such work
CONTIUED Describe
ercnma
mee
HISTORY ot RESPIRATORS RESPIRATORS
Do you wear a respirator
1 = No
2 = Yes
What type is it mainly
1 - Filter
OCUPATINL 2 Cartridge 3 Air Supply
Do you wear it usually 1 Usually 2 Occasionally 3 Infrequently
Do you eat at your work site
- No
2 - Yes
:
-
.
: (ie |
Do you smoke at your work site
1 No
2 - Yes
3 - Nonsmoker
Do you change your clothes before going home
1 No
2 - Yes
Temas T
T rene
syns Ryn vores
etek
te
a-
Does your employer
launder them
1 - No
2-
furnish Yes
work
clothes
and
Do you have separate
work clothes
1 - No
?-
lockers Yes
for
street
and
Do you shower before going home
1 - No
2 - Yes
ne eemeeaal
189
17
yes
attacks
was
your breathing absolutely normal between
1 - No
2 - Yes
WEATHER
18
Does
the weather
Only record
affect your chest
YES if adverse weather
causes chest symptoms
definitely
and
regularly
19
-
If yes
Does the weather pake you short of breath
.
Type of weather 1 - heat
2 - cold
3 - dampness
-
4 - dryness
5 - any extreme
NASAL CATARRH
20
Do you usually have a stuffy nose or catarrah at the back of your
nose in the winter
No
2
Yes
35 35 tw nm wy ~
3939
39 39 40 40
21
Do you have this in the summer
PHYSICIAN COMBIENT Nasal catarrh
:
1 bas no relation to chest condition
2
-
aggravates cough tion from chest
and phlegm produc-
as described above
3 4
5
is * cause of cough and phleg is a separate entity - no cough phlegm are produced by patient cannot be specified
an~
CHEST ILLNESSES
22.
During the past three years have you had any chest kept you from your usual activities for as much as
illness a week
which
has
.
23
If yes Did you bring up more phlegm than usual in any of these illnesses
y 44 44 45 45
24
:
How many illnesses like this have you had in the past
three years
46 46
25
Do you have a heart condition for which you are under a doctor's care
1 - No
- Yes
---- f --------
If YES specify conditions and drug therapy
TOPACCO SMOKING
103
26 Do you now smoke cigarettes
27
If NO Have you ever smoked cigarettes 1 - No
2 Yes
28 How old were you when you started smoking regularly
29 29
How old were you when you last gave up smoking cigarettes
uw ws
nad years
List year Derson last stopped smoking
rt
30 How much did you smoke on the average
31. did you inhale the cigarette smoke
What did you mostly smoke
Type
1 2
- filter + filter
Size 1 - regular 2 ~ king size 3 - 100 millimeter
Do you smoke a pipe
1 - No
If NO Have you ever smoked a pipe
1 - No
How many pipefuls & day did you smoke
Do you smoke cigars
1 - No
If NO Have you ever smoked cigars
1 No
How many cigars a did you smoke
2 - Yes 2 Yes
2 Yes 2 Yes
Do you chew tobacco
1 ~ No
2
Yes
NAME }
| I]
a
wr?
First
_
|
NUMBER
MI MI
AGE
DATE OF BIRTH TUTL TUL
TUL
TUTL
|
05
TUL | 11 |
on
+ last examined by a physician month & year {
{
|
T
343
4%.
acute illness not hospitalized other than trauma ) acute illness hospitalized other than trauma
3 trauma not hospitalized
. trauma hospitalized
3 follow acute illness 6 follow chronic illness
7 routine check
8 occupational surveillance program exam supplied by employer
3. employment physical
-
soe
ee
+", 1 was your last chest ray
month
1 ii |
year
|
{ 22
Result = normal
2 = 2bnormal 3 = doesn't know
PHYSICIAN
| 25 |
Code 0001 if never bad chest ray
Y _ 27 27 ~ -
Have you ever been hospitalized hospitalized
1. No
2. Yes Describe below
TATE
HOSPITAL
REASON
Have release forms been signed
1 = No
= Yes
28
Have you ever been told by a doctor that you had any of the following conditions
Vascular
ren
01
Heart murmur
02 03
Angina
Heart
Attack
GE
05 06
Any
are
other under
heart condation for which you the care of a doctor specify
High blood pressure
Claudication
Pulmonary
piiai Pulmonary Pun lmonari y b
07 Pneumonia
08 Pleurisy
09 Asthma
10 Bronchitis
11. 12
Emphysema Bronchiectasis
13. Pulmonary tuberculosis 14 Silicosis
15 Asbestosis
16 Other Pulmonary specify
Gastrointestinal
17. 18 19 20 21 22 23 24 25
Gastric ulcer - told by H.D.
"
"
- UGIS
.
"
- Hemorrhage Hemorrhage
Duodenal ulcer - told by M.
...
et UGIS
"
- Hemorrhage
Bleeding from ulcer
Other GI bleeding
Hiatus hernia
26 27
28
29
Hepatitis Jaundice
Gall bladder disease Liver disease
30 31 32
Enlarged liver
Cirrhosis - alcoholic
...
- Other
33
Ulcerative colitis
34 Diverticulitis
35. Other GI specify
Genitourina Genitourina
36 Nephritis
37 38
Kidney disease indicate
Urinary infection
type
39 Kidney stones
40 41
Prostate enlargement Blood in urine not caused by above
42
Protein in urine
not caused by above conditions
43 Other genitourinary
Skin
44 Psoriasis
45 Eczena
46 Other Blood
skin
specify
47. Acute Anemia
er
48 Chronic Anemia
49
Low white blood count
50 52
Problems with blood clotting
or bleeding
Sickle cell
52 Thales
53 Other Blood specify
Eve
54
Require glasses
55 Glaucoma
56 Cataracts
57 Weak or lazy eye
58 Optic neuritis
59
Other Eye specify
Ear Nose and Throat
60
Chronic Sinusitis
61 62
Impaired hearing Nasal allergies
Reproduced from
best available copy
(o)
63 Nasal polyps
64 Laryngeal polyps
65 Tonsilectory
66. Other ENT specify
ervous System
67 Seizure disorder
..
69
Stroke Parkinson's
Disease
70 Psychiatric illness
71 Other Nervous Musculoskeletal
specify
72. Rheumatoid arthritis
73 Other arthritis
74 75 76 77
Back injury Degenerative disc disease
Yes Neurologic involvement
Bone lesions
78. Other Musculoskeletal specify
General and Metabolic 79 Thyroid disease or goiter 80 Diabetes
$ 82 83
Gout
Night seats
Fever
84 Other specify
Cancer
85
Skin
86
Throat
87 85
Lung Storach
89 B2
90 Rectum
91. Prostate
92
Breast
93 Cervix
94
95.
Uterine
Other CA specify
.
Currently
B=
,
inactive
condition
number
D=
not under
physician's care
year
diagnosed
Active under
of physician
care
| rmeaaed
iqis
{
11
|
15 |
I
19
23
i : 27
{
131
|
35
|
i!
* Col
39 i 143
1-5 as above
punch E in col 6
Other
}
Col
47 51 55 59 63 67 71 75
7
11
1-5 as above
rT
1|
!
fas
19
|
23 |
:
27 |
31|
i
35 !
ia
39
|
43
i
147 |
i}
151
punch & in col 6
ALCOROL
2 Tyde
1 . Beer 2. Wine
3 Whisky
Quantity
.
3
cans week
quarts pints week
approx 10 shots = 1 pint
1
no alcohol intake
2
6 cans < 1 ct < 1/2 pint
3
6-24 cans 1-4 quarts
2-2 pants week
4
> 24
cans > 6
quaris
2 pints quaris
5 alcoholic < year
6 alcoholic 1-5 years
1 alcoholic > five years
55 |
MEDICATION ARE YOU CURRENTLY TAKING ANY OF THE FOLLOWING MEDICATIONS
1= 2
Not taking any medication Currently taking medication medication
56 |
01 - Diuretics water pills 02 - High Blood Pressure meds 03 - Nitroglycerine 04 - Digitalis
other
05 - Other cardiac
06 - Antihyperlipidemics 07 " Anticoagulants blood thinner
08 - TB medication
09 - Long antibiotics
10 - Short antibiotics
11 - Stercids - oral
12 - Steroids - topical 13 - dilators 14 - Insulan
15 - Oral diabetes meds
16 - Thyroid meds
17 - Gout medication
18 - Tranquilizers 19 - depressants 20 - psychotics 21 + Sleeping pills daily 22 - Eave you ever had radiotherapy
23 - convulsants
24 - inflammatories
25 -
Lanatives
26 - Antahistimines
27 - Decongestants -
28 - Analgerics 29 - Antacids
30 - Other specify
List medications currently being taken by number
:
| 5577
59 61 63 6363 57 69 71
72 72
75
77 77
79
PHYSICAL EXAMINATION
ese ! { L. |
234
. f
"
Height
11 in
re o-
.
led
wi *.
_:
he Toa oan
>
aot
f
Cessure!
H
a
.
Weight
Middle initial
| 13
|
27 | -
Number
JS JS
1 - male
Sex 2 - female
1616
Pulse rate
|||||| 23 |
Regularity
1 = normal
7
2 = irregular
3 = other
|
26
j
ODOLE
EARANCE
oo ceca cece venaae seeeeees eevee ven cecescneeseeeee
3 w developed well nourished
2 = obese
3 under Ight
4 = appears chronically ill
5 = pale
6 = other
28
fi
CYANOSIS
29
CYANOSIS 29 ...
.
PUTER
etre terete errs s sere ererer eres ceses eases
lips fingers eeeera | 1 = absent
2=
tongue
3<
toes
29
~
EXTREMITIES clubbing
nails
.
1 No
2
Yes
normal 1 1 other = 2 characterize
_
s
>
|
30
31
arkle edema
1 = No
2 = Yes
32
JOINTS
1 = normal 2 = abnormal
If abnormal
Joint code 1 = PIP
2 = DIP
3 = Wrist 4 = Elbow
5 = Shoulder
6 = Knee
7 = Ankle
8 = More than 3
.
= 9
other
descriptive code
1 = swelling 2 = rudness heat 3 = deformity 4 = crepitations
5 = associated with hx of trauma 6 * other
33 | ,
joint description
34
[| | 34 } |
34
|{
37
37 |
|
I
T
Reproduced from best available copy
5
1 = normal
2 = abnormality present
.
.
If abnormal
1 = seborria
2 = acne valgaris
3 = psoriasis
4 = other describe
T 44
.
EYES
Pupils normal abnormal Specify
No Sclera icteric
corr teers
Yes
etter espe eter easvans
Conjunctiva normal injected pale other seessseesecese
Describe other
46 47 48
MOUTH normal gingival abnormality ot ccch eere te rtr e ees
49
-
Describe other
THYROID t cress etesseeeeeseeeereneseeeeeseeseseresssetrersecsseerseeeses
1 = normal
2 = enlarged
3 = nodular
LYMPHADENOPATHY list locations
1 = normal 2 = cervical 3 = supraclavicular = axillary
5 = inguinal 6 = more than 3 sites
7 - other
| I | | 51
CHEST INSPECTION +. ec ee ce ess i
aaa
|
1 = normal
2 = dullness right 3 = dullness left
4 = increased AP diameter 5 = flaring of costal margins
1
CHEST PERCUSSION .. ccc eee nee cence nec ene e cece ecco tent eteeeas
156
156
1 = normal
2 dullness right 3 = dullness left 4 K resonant right
5 = resonant 6 = resonant
7 * other
left
bilateral
Describe other
AUSCULTATION .. ... meses ccc nc ac ee ea tanner sees nace
ancseasee
57
1 = normal breath sounds
6 = wheezing and diffuse
2 = decreased - right
3 = decreased - left
7 = lenghtening of respiratory phase
8 = moist rales
4 = decreased bilaterally
9 = other
5 = wheezing and rhonchi in a
localized area
Describe other
1 = none 2 = RAAL 3 = RPAL
4 = RMAL 5 = Base 6 = LAAL
7 - LPAL 8 = Base
0 diffuse more than 3
CARDIAC PALPATION AND PERCUSSION ccccncceccocscceceecerceucs
63
1 = normal
2 = heart palpable in epigastrum 3 1 heart enlarged by percussion
4 = left ventrical heave 5 " right ventricular heave
6 = displaces P.M.I.
HEART SOUNDS .... ccc cee cece e cna c ences sence ween ter cebastrentes
se
1 = normal
_
2 = murmur 3 = distant heart sounds
Describe other
= pII II
53
6 = other
ASDOMEN Inspection
Masses
Abdominal tenderness to palpation
69
1 = none
2 = RUG
3 = FLQ
4 = Epigastric
5 - umbilical 6 - LUQ 7 * LLQ 8 = other
Describe other
1-7
PALPABLE LIVER not palpable palpable
*
"
7e ee7""t * amer ane tee
|
If palpable span on clavicular line ~ in cm be eeeeeeeeceeece dd
Liver tenderness No Yes tte ccs esse ese ce es re ace eee neers
Liver consistency a a
.
normal
irregular nodular
increased firmness other
---- 71 73
74
PALPABLE SPLEEN not palpable palpable --.---++.s.-seee0- eaaeee
If palpable two dimensions by percussion cm
Ze
PALPABLE KIDNEYS
not palpable palpable
palpable left left
right
eet eee ben eas
ABDOMINAL MASSES BY PALIATION none present eee en enne Location size and consistency
7% 76
~
|7
| 72
NEUROLOGICAL EXAMINATION
Deep tendon reflexes
normal
hyperactive
decreased absent
ie
Specify abnormality ankle
1]
biceps
12
knee
13
wrist
14
NOTOR
cect cece cece sc ce ees rane cet a teaser tence esse ves tepessererenene
normal decreased strength
Indicate muscle group wrist drop
teleky sign
extensor weakness Babinski other
involved
TRcE cc c cM eceO er cR tw e sce
none
outstretched intention face other
hands
eeeece ee
ee eeeee asec eecene peewee ecercee
Describe other
15
18
| | 18
Col 1-9 as above punch kK in col 10
emerge
ee,
Oe et ee ne
Sr em re me ee
eee
ra
won
118
SENSORY pin
Arms 1 = absent = present
20
Legs 1 - absent 2 = present
OTHER NEUROLOGIC
1 = none
2
present describe
EXAMINER'S CODE ete
[
[
|
2 Selikoff Anderson
3
=5
4 =10
Daum Fischbein Holstein
Lilis Loriner Rom Rosenmann Todaro
| 23 23
twee
et
pe
te ee
oe
8
wren
pee
wee
.
.
-
HUMAN RESEARCH CONSENT FORM
I. PROJECT DESCRIPTION
1. Investigation of Health Hazards in Brake Lining Repair and Maintenance Workers Occupationally Exposed to Asbestos
.
NIOSH 210-77-0119-0000
2. Investigators Irving J. Selikoff M.D. and William J. Nicholson Ph.D. Purpose To identify any human health hazards associated with
brake repair and maintenance
II CONSENT TO PARTICIPATE
I
> age
hereby voluntarily agree to cooperate
in the above named study and to undergo the tests listed in Attachment A.
The study has been discussed with me and I have been given a copy of this
document I understand that
1 The procedures and tests to be followed are as stated in
AttachmenAt no procedures are experimental
2. Attendant discomforts and risks are as noted in Attachment A and except as noted are minimal and provision has been made for any
Decessary medical care and I have been told what to do if I have any reaction
3 Benefits are as indicated in the Purpose statement above Part I Item 3
4 If alternative procedure advantageous to me are available they are specified in Attachment A and if they become available during the project the procedure most advantageious for me will be indicated and used or an explanation will be given to me as to
use of any other procedure
5. My inquiries will be answered by the project directors or other
personnel invovled in the project
Telephone 212-650-5823 212-650-5823
6 I am free to terminate my consent and to discontinue participation in the project at any time without prejudice to myself
7. My identity and my relationship to any information 1 disclosed
by me in completing any project questionnaire and 2 reported by me or derived from me during my participation in the above named
project shall be kept confidential and will be disclosed to others
without my written consent that such information will
except as required by law and except
be used for statistical and research
purposes in such a manner that no individual can be identified
I understand that
that can endanger
if any information is
the health and safety
found out concerning me of others this infor-
mation will be given to the proper authority
8 If any of my medical records are required for purposes of this project a separate written consent for release of the records will be requested from me
me
ee
pee
se eeer meeee our cena pueyaen sone 8 = RL oh ee
eR
es
wee
-
seo
. .
1.
9. There will be questions that I will be asked to answer
and my inquifies concerning the questions will be answered by
Dr. Selikotf or Dr. Nicholson
212-650-5823
10
A report of any significant information from the study that specifically concerns me including medical information will be furnished by the project officer or his designated representative to me or to my designated physician upon completion of the study or earlier if appropriate
SIGNATURE
Subject'Subjsect's Name
Date
Will r 11.
INVESTIGATOR
LU
Nichol
n, r Associate Professor
fy
2 ie
SigSniatgurneature L,
III CONSENT FOR MAINTENANCE OF RECORDS
I hereby give consent for Mount Sinai School of Medicine to maintain all
records of this examination They will be completely confidential as
information will be released to any physician I designate upon my
Titten request and authorization at any time in the future
-
above
and
SIGNATURE
Subject Name
Date
IV REQUEST AND AUTHORIZATION FOR RELEASE OF INFORMATION
I the Project addresses I named study DO NOT WISH
' hereby request and authorize Director to inform the following physicians whose names and
have entered below of any significant findings from the above
concerning me DO NOT LEAVE BLANK WRITE NO WHERE YOU TO GIVE A NAME AND ADDRESS
.
1. My personal physician
Dr.
Street
2. Other physician
Dr. Street
City
.
State
City State
wee en Ope eg
ae
Soe tr gee ...
... ee
re
- pe = ra
a
~ weet tee
my SPN ee a eee
ATTACHMENT A
Investigation of Health Hazards in Brake Lining Repairs Maintenance Workers Occupationally Exposed to Asbestos NIOSH 210-77-0119-0000
and
The procedures and tests which involve human subjects in conduct
of this project are as follows
Blood tests
Urine analysis
Sputum cytology
Chest ray Pulmonary function tests Physical examination
Each of the above provides important information the evaluation of health status There is minor disconfort associated with the drawing of blood from the arm The sputum cytology involves coughing up phlegta from the throat into a container which is provided The pulmonary function test involves a maximum breathing effort
Rights under the Privacy Act of 1974 Title 5 United States Code
Section 55 e2 3
The information required to be given to me under the Privacy Act of 1974 is as follows
1 Authority for collecting information is the Occupational Safety and Health Act of 1970
2 The principal purpose of this study is as stated in Section I
Item 3
1
3 Routine use of this information is in developing criteria and programs for a safe and healthy place of employment
4 I do not have to furnish any information I do not wish to
Nothing
whether
happens to me as a result of my not providing all or in part of that requested except that
information
I may be
terminated from the project
5
LOR 4 SWRMUIOD
OP
poquats
|
5
SCIENCES
SCIENCES
SCIENCES SCIENCES
ENVIRONMETAL THE OF MEDICINE |
MEDICNE SCIENS SIP
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Comentreqainy Saz2 aShu}oote g a5zqiz 77o>
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Clasifcton ILO Radiographs {
Radiographs
Pneumoconioses
4
of Radiogrphs MAN
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5 AMOLVUd!Date
ALIO
SHONIS BHL YO
ANIDOSW
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39 380
paungs S1uGisp ,U0j50D) TUNG Aya fouNse WIA Enwuds WGI
IUar0}29 MWOoswnad Ayeuoge aysuo 28s043-es7UY puaesjco quioahuoy pyoeutmays sIu;nos0qQNy spoSargny saedo Buroyiubes ainsodue (p01lajeo SUOIDUAS uisLe2un Lovel pr {A9}49%) pratingeSuap O.umud zaueo Lovel paunlS qduAy Beicnhnbituonisd eyng eunajyd Aus sapou fit2015 jewsCOM
40
FS
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20
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40
a745 Nd pag
Kp 390 icus ayy
pou WY as FAI PU
14 IAL JO
Yes 26
sey] puns jo puss so
Ul]
Bun]
NIUE
Ga
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BY) OU 40 a1IUOag
sn0 je) Omer Cae.
das a up wap
Bichnitions
0M ma
Q0ad ALI
47
334 BAUER
2.00 Agee
xe
the afected
.
.
Category smal rounited opicties are 1
4290( predominat 4amO} SONd Nate nodules S2UOT
-- --
01-001
small rounded
opalities
2/2
small
303 Category ta smalt rounded opacities
are
PUT
clasfied
acording
parsaye padncsqy priz2ye RU opsties aholt dipius Ayman M Apius m a4q1
aNn ut
fanIatda samed JIWEID Iregular Profusionfi Penge prinago zonescategory of the based of 4818hKyatides KuedALysUan sauar profusion conetraion in ye
mid opacites Ayensn jewsou Ayensa profuse profusiont (unr
UAE,ETL Arveaynd sforqiew:s2uryivat J21yOwUeIuEnTmopPasdatuetip Combined 4wousnyord) Ssodacsaqunysdunyiewurqsew EBBEaMt RL Categoryof^'uties standrrounde whiricehgular opaciirteegsular dimenso mdimeensnions normal FeUpNGs) symyuad wherae iauiou paps asnyosd (RWIOU prusay 312 the rounde smal iregular the rounde rounde rounde inusmber diTvihdede tinhtealyy intalyobbsceureduopbsceurred 1
EL tude was d the separtely separtelyand HeaUE pe
9.1uyapweu2ine IndaA Surpozan2FurpazEs khpwoypbrsIuNU VaswNY SaevdyC ikourh opaertis of ITP the are VANE
ovnTane8 Wanye ywasys On
FOF spucktiesaINEdAszaVcdE site than those such - opacity . Pagpoe SoucredY banIed saiprtespuckties spuckties sauzcdo sIETY sanideo senaeCngry) Category equivalent zone vw oy pomnodpoanespa sPrpynod PrynseypounosPapunsPopunos Sretodes wortnjosd sepnBaus ndseyndacs , sartder dehned the A or abreviatus in mAyoadUY YLYs DUYyIp MIE.Gorge Cane " anrrea should be sua.it whetheruper yoVUE)
-- KsDar
Other Costphrenic Right pouews sav0d Sawer Obliteration the thickenigthickenig .asoyt dsentpucrs
CawdairAvtarActa diaphragmdiaphragm robe lower lumut standard film Za diaphragm provide partofany ape, apraryapray aprat>pag ayayy
(Was ay SWIM
EP
. 2324)
ae WE WO] aie
ose
IUYE RAGE
O)
OF
Juny ayy
dis dA
te
ee
Ue Fury
pe
PUT Pre
Kany
vey Haz
WUEWuil yorq
5
ing MYL Wars
AL a1RUH InOge InoYye
9505
Inge
ad
OF
Combined
dn
Large yy
ures
Large
aan
qeus Wry yews yews
-
+
~
~
y 4 qT 4
ai
219
-
-
-
aseOyqual(us
UI
y
ays
SUL
>
t'
Ap
ayy
aie AM
ui
LM
waye
Care
{ rounded
zones which
spaci ies
ay2 spaciies
1y2es LM .
Fury kayh
Jo
ing
ayy aie
01-01 "p MEL ase 4/0
standard profusion
standard
Js
smal Category |
Category opscitcs PIP
Category
define the mid opacities
FYE
JO
.
Ivar
er
Sunt
te
ur ve Bony June
weg) may
yorg
ing JQ
JUL vs9y
30
EBEM
EBEM
Pre dee
oy ase
iregular opacities
small
Category
ir egular
of^'uties iregularare
ve of^'uties ... line iregular
Gua sit 15 15
egarse blotchy
opacities
for
Aroe unded
When bath rounded
profusioprnofusion
ikourh all
U Category A opacity WLYOI hoas A vod Category greatest
DME Jo aur
parieg site piu sedu Myb
Category
one
the equivalent
snare 82 Jy sep
Category
Cane
Cane
snare
Category
snare
stynBseynd leter . den dost der
nd 3ye vor well well
let er
IIT = - >
dehned
te
Jo du
thickenig ews rus [UE yews inte --- thickening
41
YE saup
counphrenic thickening -
+
angle angle &
Obliteraon counphrenic we
counphrenic
Obliteration
the counphrenic
provided
Costophrenic Cliorwaedro and diaphragm 5
thick Width Width | |
IQS
sey
Right
Ig) i
t'
Grade Grade
provided
we
mm
b over. about about Sinm
b
asesment shrent dolinutely
opacities opacities
were
diameter
larger
whose
qdabreviatusu
aya
recorded
recorded
JEL)the widest
about
entegnty
inarkings
markings
Ju
up
to
to ayt
slisided slisided prey
profusiont
concentration
category
few
normal
The
egy
recorded a Each 1
recorded ga
number
lung markings markings
opacities cannot cannot
Wye canot canot
is trea, yond
divided
provent provent
provent This between lant lant
record profusion
optional optional feiture feiture
Som several
at lant ee
we Ot
numerous than
numerous combined numerous exceds thosethe
combined combined exceds excedsthe
should should
ad ---- ----
op
septrately thickenig septrately
over septrately
from
thickening thickening
--
-
' yy 3
yy t
z
op
Lumim
thich
widest
partly
of
the ly)
10
3 tala
normal markings markings markings
usually
are
used can roughly
IHN IO ty gu ZI]
- three
zones upper
three
three
jo fur
separately
clasifcationclasification
clasifcation
clasification
opacities opacities tum
such
whose opacites the tum
combined combined category whose de combined24
equivalent
right right upper
equivalent Ue
equivalent whether eens indicate
whether
the
--ind-icate-
VELTE ------- -
suo
otohtheerr . sarEH
-
-
SaBmaeert U ft 2 (
3onH 9
SWS,
UOQN
WOE UY
Lag
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lower LROQE MOTE 928 ..pooTdmsp9Id 928928
928 visble Atal NaI. 928 THe 1, |
into thre thre |saq
into into
MS Fo
lower- lower- +
att Tia 24d
the combined hihi
greatest greatest
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DOU DEN
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