Document mBOLOx04dq85woNmvYyxxGDJb
FILE NAME Brakes BRK DATE 1972 Aug
DOC BRK126
DOCUMENT DESCRIPTION NIOSH Report - Air Sampling & Industrial Hygiene Survey - Genuine Parts Co Rayloc
AIR SAMPLING
&
INDUSTRIAL HYGIENE SURVEY
@
GENUINE PARTS COMPANY RAYLOC DIVISION
ATLANTA GEORGIA
Survey Conducted By
JOHN M. DEMENT PATRICK J. SHULER
Report Prepared By
JOHN M. DEMENT PATRICK J. SHULER
Division NATIONAL
Environmental Environmental Investigations Branch
HEALTH of Field Studies and Clinical Investigations
INSTITUTE FOR OCCUPATIONAL SAFETY &
1014 Broadway
Cincinnati Ohio 45202
August 1972
REPRODUCED
INFORMATION NATIONAL TECHNICAL SERVICE
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1.3
DEPARDTEPMARETMNENTT
OFCOMMERCE ae
PLACE VISITED
DATE OF TRIP PERSONS MAKING TRIP PERSONS CONTACTED PURPOSE OF TRIP
Rayloc 4200 Gordon Road Atlanta Georgia Phone : 404-691-3780
July 17-19 1972
John M. Dement Patrick J. Shuler
Mr. Edward Kipling Plant Manager Mr. Thomas Damiel Production Manager
To conduct an industrial hygiene survey and take asbestos and lead dust samples in the plant
INTRODUCTION
During the week of July 17-21 1972 an industrial hygiene survey and air sampling for asbestos and lead dusts
were conducted at the Rayloc Division of the Genuine Parts
Company Atlanta Georgia
From the sample results and industrial hygiene survey several conclusions can be drawn The following paragraphs discuss plant operations and industrial hygiene practices along with conclusions and recommendations
DESCRIPTION OF THE PLANT
The plant is located west of Atlanta and employs
approximately 540 people operating on three shifts of these
Workers about 50 come into contact with brake linings or clutch
facings on a routine basis This facility was constructed by
Genuine Parts Company in 1959 for the purpose of rebuilding
various automotive automotive parts The plant is enclosed under one roof
additions having been made over
s^>te
s^>te
the years
to the original
plant
Genuine Parts Company provides consultation to assist
Rayloc and their other divisions with any safety and industrial hygiene problems These services are also provided by Sentry Rayloc's insurance company The production manger is responsible for safety in the plant and is chairman of a five member safety
committee which meets each month The union Teamsters Local
528 is also actively involved in the safety program in the plant
The medical program consists of local physician retained
as a time consultant and workers trained in first aid who
are always in the plant A employment physical is given which includes a chest ray and blood and urine analysis No pulmonary function tests or further physical examinations are
Products of the plant presently include rebuilt starters generators alternators water pumps fuel pumps clutch pressure plates and relined clutch dises and brake shoes Cluten disc
and brake shoe relining has been done here since the plant opened
DESCRIPTION OF THE PROCESSES
The processes sampled were the relining of riveted and
bonded brake shoes and clutch dises
A. Brake Shoe Relining
The used brake assemblies are first sorted according to
size The old worn linings are removed next Riveted linings are sheared off and bonded linings are burned off Next the
shoes are degreased by heat if necessary then cleaned in a
Wheelabrator which uses high velocity steel shot to abrade
the surfaces The shoes are then dipped in a corrosion|
inhibitor and straightened if needed Next the new linings
are either assemblies
riveted or are bonded to the shoe
are then surface ground to provide
All relined
the correct
radius of curvature
inspection and packed
The for
finished products shipment
are
given
a final
-
B. Clutch Disc Relining
The used clutch dises are first wheelabrated with the old friction pad still on to insure that the thin metal torque members are not damaged Next the old friction surface is
removed by deriveting the clutch disc with either a drill or punch press A new pad is riveted on the disc the whole assembly is inspected and boxed for shipment
SURVEY PROCEDURES
The actual sampling for asbestos fibers and lead dust was confined to the brake and clutch rebuilding areas since these
were the only areas using these materials No other
exposures were noticed in to toluene in the starter
the rest of the plant with
rebuilding area Personal
were collected on workers at each of
the steps in the
of relining brakes and clutches in
order to determine jobs if any pose potential health
problems
potential
exception
samples
process which
Samples were collected on a Millipore Type AA cellulose
ester membrane filter The type of pump used
at a calibrated flow of 1.7 minute
was a MSA permissible personal air sampler
Analysis for asbestos fibers was done by counting fibers
greater than 5 ...m in length at a magnification of 430x
under a phase contrast microscope
The amount of lead was determined
same by chemical analysison the
filters as the ascestos
concentration was evaluated
An industrial hygiene survey of the plant was also conducted to try to evaluate general housekeeping and ventilation systems
INSPECTION OF THE PLANT PLANT
Potential Health Hazards Health Hazards
The potential health hazards which were noticed during the
survey are as follows follows :
1. Exposure to asbestos dust during brake and cluten
relining 2. Lead exposure from lining materials during brake
and clutch relining 3. Toluene exposure during insulation coating of
various armatures
Measurements were made of both asbestos dust and lead exposure in each of the friction operation No measurements of solvent
exposure were ide
Personal Protection
Safety glasses are required in certain areas of the plant Approximately 40 of the plant employees wear safety glasses
Respirators are not required in production operations however
respirators are required when cleaning or repairing the bag dust collectors Safety shoes are not required but the company does
have a program to aid in their purchase A noise study has been conducted in the plant recenti sv Ser-
Insurance Mr. Kipling indicated that the only operation near the 90 dba present standard was grinding No hearing protection
is required at the present time
Ventilation
~
Local exhaust ventilation is provided on all 3 brake lining
grinders and on all 5 Wheelabrator cleaning machines These
machines are vented to 6 Wheelabrator bag dust collectors
Figure 1 shows a layout of the friction products area of the plant along with locations of the dust collectors and their respective capacities
Velocity asurements at the entrance to the grinder hoods
showed velocities ranging from 600 fpm to 1100 fpm No
ventilation is provided at the clutch deriveting operation
Housekeeping
In general the plant was quite well kept with sufficient
room to minimize overcrowding All floor cleaning is done with
vacuum sweepers on a continual basis Compressed air is used for cleaning but all outlets have low pressure nozzles
Results and Discussion
The results of this survey are presented in Table 1. The present standard for asbestos was published in the Fecerai
Register on June 7 1972. In essence the standard is as fol lows:
The hour weighted average airborne
concentration of asbestos fibers which
any employes maybe exposed shall not exceed
five fibers longer than five micrometers
per cubic centimeter of air as determined
by the membrane filter method at 400-450x
magnification 4 millimeter objective phase
contrast illumination No employes shall
be exposed at any time to airborne asbestos
fibers in excess of ten fibers longer than five micrometers per cubic centimeter of
air
On July 7 1976 a new standard of 2.0 fibers greater
than 5 micrometers in length per cubic centimeter of air will be
effective
None of the 45 samples exceeded the present standard for
asbestos the highest value being 4.8 fibers fibers greater
than 5 micrometers in length per milliliter There were only
three samples that exceeded the future asbestos standard of 2.0
fibers All of these samples were taken on person deriveting
old clutch facings by drilling out the rivets A total of four
samples were taken at this operation the mean being 2.6 fibers
Surface grinding produced the second highest average excosure
its value being 1.4 fibers All other operations had an average
value at or below 1.0 fibers
Lead concentrations were very low except for the clutch de-
rivating and brake shoe sorting operations
rd
The present standard
for lead dust exposure is 0.15 mg results are also
given in Table .
CONCLUSIONS AND RECOMMENDATIONS-
From the sample results and the industrial hygiene survey
the following conclusions and recommendations are made
1. There was no operation that had asbestos exposures
in excess of the present standard of 5 fibers The only
operation in excess of the future standard of 2.0 fibers
was the removal of old clutch facings by drilling This
Operation also had lead exposures in excess of the present
standard of 0.15 mParticle size estimates of the lead
particles has shown that 80 of the particles were less than
3.5u in diameter and would therefore by respirable Due to
the high lead exposures local exhaust ventilation should be
|
added at these drills immediately
2. Lead concentrations in the old shoe sorting operation
_ were also above the present standard of 0.15 mParticle
Size estimates on these samples has shown that 85 of these
particles were smaller than the 3.54 respirable diameter
The high concentrations appear to be the result of brake lining west dust clinging to old brake shoe assemblies Our past
experience has shown that most wear dust contains approximately
62 lead by weight Two possible solutions to this problem
would be to either first wet or vacuum off the brake assemblies
before sorting
3 There was a detectable toluene odor in the area of <ne
ature possible
dip tank Although this odor was present
that toluene concentrations are well below
it is highly
the present
standard of 100 ppm the 2.1 ppm In any event
odor threshold for toluene is toluene concentrations should
only
be
determined for this area and local exhaust
If levels are found excessive 100 ppm
ventilation
Installed
ny Due to the elevated lead exposures found in the brake
sorting shoe
operation and clutch derivating operation blood
these lead levels should be determined for workers in
areas
A program of periodic blood lead checks should be established .
.
.
+ (bh soca
22 .0e
10
REFERENCES
.
Edwards G.H. and J.R. Lynch The Method Used
by the U.S. Public Health Service for
Enumeration of Asbestos Dust on Membrane
Filters Am Occup Hyg 1-6 1968
2 Keenan Robert G. etal The U.S.P.H.S. Method for Determining Lead in Air and in Biological Materials Am Ind Hyg Assoc Journal 481-491 1963
3
Interoffice Report on Garage Lead Exposures
March 16 1972
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1 TABLE
RESULTS OF SURVEY AT
RAYLOC
Atlanta Georgie | July 17-19 1978
JOB
SAMPLE f
Brake Shoe Section
Sort old brake shoes
584422E2uff
Sort old brake shoes
584422E2uff
Deriviter brake shoes
584422E2uff
Load old bonded shoes in oven that removes lining
584422E2uff
Load old bonded shoes in oven that removes lining
584422E2uff
Wheelabrator brake shoes
584 2 E2uf
Wheelabrator brake shoes t
584 2 E2uf
Wheelabrator brake shoes
584422E2uff
Wheelabrator brake shoes
584422E2uff
Apply adhesive to linings
584 2 E2uf
Apply adhesive to linings
584422E2uff
Riviter neiger
=
Riviter helper
~
Riviter
==
Riviter Riviter ==
Rivitor #
Riviter 82
Rivitar
82
Rivicar
.
=
;
Riviter
%
Rivitor
57447
Inspector after rivit
57447
Sonder
57447
Bender
57447
Sander
.
**
CONCENTRATIONS
ASTESTOS PIZES
Fibers bum in length
DET 2
oEis
==
-
1.0 0.2 1.0 0.4. 0.6
0.7
0.7 0.8 0.4 0.3 0.3
0.5 0.5 0. 0.7 0.2 0.3 0.6 0.9 0.6 0.5 1.0 1.4 1.2
0.3
0.32
0.21
0.08 0.05
0.07 0.12
|
0.11 0.08 0.2 $37 Q.25 3.22 0 0.06
0.12
0.05
0.05 0.05 0.08 0.17 0.06 0.05 .06 0.06
0.14
13
Rayloc Sample Results Atlanta Georgia
Page 2
GF
JOS
Surface Grinder Surface Grinder
Surface Grinder
inspector Inspector inspector Inspector
Packer
by grinder by grinder by grinder
final product
Packar
Clutch Parring Section
Wheelabrator clutch facings Derivit clutch facings punch press Derivit clutch facings drilling Derivit clutch facings drilling Derivit clutch facings drilling Darivit clutch facings drilling Riviter clutch facings Rivitar clutch facings Packer clutch facings
SAMPLE s
513883882 513883882 513883882 513883882 513883882 513883882 513883882 513883882 513883882
CONCENTRATIONS _
ASBESTOS STREAS
Pibere Sum in length
Der ml
arg
ogre
1.5 1.0 1.6 0.8 0.9 0.8 0.8
0.9 1.1 1.1
0.10 0.05 0.09 0.06 0.09 0.07 0.03 0.09 0.07
wwwwwwwYN
0.6
wwwwwwwYN
0.19
0.9
0.06
wwwwwwwYN
2.8
wwwwwwwYN
4.8 -
0.30
0.25
wwwwwwwYN
044MN
0.70
wwwwwwwYN
044MN
0.21
wwwwwwwYN 044MN 0.07
wwwwwwwYN 0.3 0.04 |.
wwwwwwwYN
044MN
.07