Document nm0MKOovJkV7yawRjxqzVMDDw
Exposure to Asbestos during the Servicing of Brakes of Passenger
Cars July 1968
Dr D E Hickish - 1/163 Industrial Hygiene Specialist
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PLAINTIFF'S 4 EXHIBIT
1 WV-06336
PLAINTIFF'S EXHIBIT
I INTRODUCTION
.
This investigation was undertaken in view of the increased national concern regarding exposure to asbestos,
and of the impending revision of the Asbestos Regulations of the Ministry of Labour,
One of the operations within the motor industry which
could involve exposure to asbestos dust is the cleaning of brake drums and clutch assemblies, normally carried out during
routine servicing by "blowing-out" with compressed air jets.
The brake linings in current use may contain
40 to 60$ asbestos when manufactured - the asbestos being
normally in the chrysotile form, and occasionally in the amosite form. Crocidolite asbestos is said not to be used. I! FIELD INVESTIGATION
It was considered that any hazard to health from
exposure to brake-drum or clutch dust would be more widespread
within the Dealer Repair Organisation than within Ford of
Britain, so the Initial investigation was carried out at
a large Main Dealer service bay. At this garage, the number
of cars per day given a routine service varies between 10 and 20, but not all servicing involves brake cleaning.
Air sampling was carried out initially on two
occasions, A and B, using thermal precipitators (T.Ps) as the
sampling instruments. On the second occasion, samples were
also collected on membrane filters. This latter technique
has been developed in recent years, and is likely to become,
the preferred method of sanpling for asbestos in Croat Britain and the U.S.A.
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In each case, measurements were made:
(a) By the side of cars being given a service which included
brake cleaning, and
(b) In the dust-cloud during brake cleaning, and then near
to the car for the remainder of the service period. Ab the mechanic normally blowa the dust away from
himself, the sampler at (b) would be exposed during "blow-off"
to dust concentrations greater than those actually pertaining
at the breathing zone. It was considered, however, that to
sample in this way would provide an additional factor of safety.
Details of the sampling are given in Table 1,
A further period of air sampling, C, was carried out,
when membrane filter samples were collected from the breathing
zone of the brake-clean operative, by means of a personal
sampler, with suitably modified flow rate (approx. 250 cc/min.).
The sampling covered an entire work shift, during which
brake blow-out was carried out on the following vehicles:
.
5 Corsairs I Zodiac 4 Cortinas
1 Prefect
'
The thermal precipitator slides were subsequently
Incinerated and examined by micro-projection using
a 4 mm objective and X, 17 eyepiece. The membrane filter
samples were rendered translucent by the addition of
triacetin, and examined in a similar manner. Phase
contrast microscopy was not used.
.
The results of the T.P. counts for occasions A and B
are given in Table 2, and for the membrane counts on the
t. occasions
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occasions B and C in Table 3. The counts are expressed in
terms of particles with diameter greater than lp, and of
fibres (i.e. particles with aspect ratio greater than 3:1
and length greater than Sp).
LABORATORY INVESTIGATION
In view of the relatively few fibres present in the
. air samples, a laboratory investigation was undertaken,
comprising microscopic examination of samples from brake lining
material (which was filed to produce dust) and brake drum dust
(collected by spatula from brake drums immediately prior to
blowing-out). The samples were sieved through 200-mesh
screens and then examined before and after incineration.
The results are shown as fibre proportions
in Table 4.
,
Samples of material collected from the brake drums
of (a) an Anglia van, (b) a Mark II Cortina, and (c) an Anglia
car were analysed by Dr S Holmes of Messrs.Turner Brothers
Asbestos Co.Ltd., and his findings are shown in Table 5. DISCUSSION OF RESULTS
(a) Standards of dustiness In June 1968, the British Occupational Hygiene Society
published a Hygiene Standard for Chrysotile Asbestos Dust, which suggested that in order to reduce the risk of contracting asbestosis to l# of those with a lifetime's exposure to the dust, the accumulated exposure should not exceed 100 fibre-years/cc, i.e* 2 fibres/oo for 50 years, or 4 fibres/cc for 25 years. In this standard, fibres are
... defined
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defined as those exceeding 5,u in length, as determined by
the membrane filter method.
Categories of dustiness are designated as follows:
Dust Categoi
Concentration averaged over 3 months ( FPiibres/cnr \
Negligible Low
Medium High
0 - 0,4 0.5 - 1.9 2.0 - 10.0
Over 10.0
As an alternative index, a thermal precipitator
count of 25 particlee/cc greater than lu after incineration
is regarded as equivalent to 2 fibres/cc by membrane filter
count.
While it is considered unlikely that a mechanic will
be engaged on brake cleaning for a working lifetime of up to
50 years, an additional factor of safety should be provided if
a Threshold Limit Value (TLV) of 2 fibres/cc, i.e. corresponding
to this length of exposure, is adopted in considering the
results of the present air sampling.
.
(b) Field Investigation
The thermal precipitator particle counts are in
excess of the alternative TLV of 25 particles/cc. but these
counts would Include many non-asbestos particles - road
dust etc., whereas the TLV was determined from counts within
asbestos factories. The fibre counts by thermal precipitator
are lower than those obtained by membrane filter.
Membrane filter counts show a concentration in the
general atmosphere below the TLV, except when the sampler la
placed in the dust cloud during blow-out. The personal
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exposure is shown to be at a level of 1/3 of the TLV, and
corresponds to a "low" dust category. (c) Laboratory investigation
It is, at first eight, surprising that the exposure
to asbestos is as low as found. In vLew of the quantity of
asbestos present in the original material of the brake linings.
Comparison of the fibre proportions in brake lining
material and brake drum or air-boms dust (Table 4) shows that
in the latter, the percentage of fibres is greatly reduced.
^ The analyses of the brake drum dust samples confirm a very
low asbestos content. These findings suggest that during
usage, the material undergoes changes in physical and/or
chemical form.
Enquiries from research workers in UK and USA
indicate that this is a finding wjiich has been observed
elsewhere, and current thought is that during braking,
high point contact temperatures are reached. As a result,
thermal decomposition of chryeottle asbestos takes place,
producing an amorphous, non-fibroua magnesium silicate.
' Under very extreme operating conditions, the binder may.
decompose and release part of the asbestos as free fibre,
but such circumstances would be most unusual.
(d) Conclusions
On the environmental and analytical evidence obtained,
it does not appear that a significant hazard to health should
occur during brake drum blow~out in a typical Dealer
Passenger Car Repair Shop. It would be helpful, however, for
clinical
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6 clinical examinations to be made of some repair mechanics with long experience of brake cleaning to confirm this view.
It would also be desirable to include in Service
manuals, a general instruction that Inhalation of dust during brake cleaning should be minimised, and If practical alternative methods, which would produce less dust, can be devised, their use should be recommended, The present investigation has been confined to servicing of passenger cars, and a further study of heavy vehicle servicing Is under consideration.
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Table 1, Details of aLr samplln
Day A Al
' Location
' bur m
________________________________________
T.P.*
(a) Static by car
(b) Dust cloud, then static
(b) "
"
"
(a) Static, by car
(b) Dust cloud, then static
(a) Static, by car
Day B Bl
T.P. m/
(a) Static, by car I
T.P. M.
; (b) Duet cloud, then static
II {a) Static, by car
t.p.; M. <
(b) Dust cloud, then static
1 Cortina Estate
1 Anglia Van l Cortina
Estate 1 Anglia Van
1 New Cortina
1 New Cortina
a DC
o
u.1
Q Ul o 3 Q O oc CL
Day C Cl
Personal sample
60 1 Corsair
56 (1 Corsair (1 Zodiac
59 None
56 Jl Cortina (2 Corsairs
60 1 Cortina 1 Prefect (part)
64 1 Prefect (contd.)
70 J 2 Cortlnas (1 Corsair
* T.P. Thermal Precipitator
/ Membrane
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Table 2. Results of Thermal Precipitator Samples
Sample No.
sample details r
(a)Static - by car
Time-weighted average
Time-weighted average (b) In duet cloud.
then static
Time-weighted average Time-weighted average
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Table 4
Fibres - as percentage of total particles observed__________ _______
Sample
Brake lining material Brake drum dust Air-borne dust
Fibre proportion - % Un-Incinerated Incine rated
28 12.3 0.6 1.6
1.3
Table 5. Analysis of Brake drum dust
Sample 1.Anglia Van
2.Cortina Mk.II 3.Anglia car
Elec tron ------------ XTH7-------
diffrac tion
diffraction
microscopy
(normal
specimen}
X-ray diffraction
(extracted
specimen)
Chrysotile present
Iron & quartz
present. No chryso tile
detected.
Less than 5$ chrysotile, possibly 0.1$
to 1$.
n Less than specimen 1.
It m As specimen 1.
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Table 4
Fibres - as percentage of total particles observed__________ __ _____
Sample
Brake lining material Brake drum dust Air-borne dust
Fibre proportion - % Un-Incinerated Incinerated
28 12.3 0.6 1.6
1.3
Table 5. Analysis of Brake drum dust
Sample 1.Anglia Van
Elec tron diffraction microscopy
Chrysotile present
2.Cortina Mk.II 3.Anglia car
ft
n
X-ray diffraction
(normal specimen)
X-ray diffraction
(extracted
specimen)
Iron & quartz present. No chrysotile
detected.
Less than 5% chrysotile, possibly 0.19#
to 1%.
n Less than specimen 1.
ft As specimen 1.
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