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Br. /. exp. Path. (1986) 67. 113-129
Inhalation and injection studies in rats using dust samples from chrysotile asbestos prepared by a wet
dispersion process
J.M.G. Davis. J. Addison. R.E. Bolton. K. Donaldson and A.D. Jones
The Institute of Occupational Medicine. H Roxburgh Place. Edinburgh F.HR 9SU
Received for publicnlion 1 9 April 1985 Accepted for publication 30 July 1985
Summary. Long term inhalation studies and intraperitoneal injection studies in rats were undertaken with a series of chrysotile asbestos dusts. Three dust samples were generated from chrysotile modified by the wet dispersion process (WDC) and one was from unmodified chrysotile. Following a 1 year inhalation period, all the chrysotile samples proved extremely fibrogenie and carcinogenic and there were no .significant differences between the WDC dusts and normal chrysotile. In all experimental groups approximately 25% of animals developed pulmonary carcinomas and in the oldest rats advanced interstitial fibrosis occupied on average lo% of all lung tissue, fn the injection studies all the dust samples produced mesotheliomas in over 90% of animals. Very little chrysotile remained in the lungs of the animals that survived longest following dust inhalation and what there was was present as individual chrysotile fibrils. It is suggested that chrysotile is potentially the most harmful variety of asbestos as shown in these and other animal studies but that it is removed from lung tissue quite rapidly. In the long lived human species this may mean that except where exposure levels are very high and of long duration, chrysotile should be less hazardous than other asbestos types.
Keywords: Chrysotile asbestos, wet dispersion process, carcinoma, fibrosis
The industrial use of asbestos has been taken in order to examine these effects but
shown to result in considerable health risk to most have used either in vitro or injection
asbestos workers (Selikoff & Lee 1978). techniques because these require only small
Heavy exposure can result in pulmonary amounts of dust which can be specially
interstitial fibrosis (asbestosis). bronchial prepared. Long-term inhalation studies
carcinoma and mesothelioma.
unfortunately require large amounts of
While the main commercially used asbes asbestos dust and so far it has not been
tos varieties differ markedly in their chemical possible to obtain sufficient size-selected
composition, all show considerable potential dusts of any single asbestos type to examine
to produce pulmonary disease when inhaled. the effects of fibre length when dusts are
It is now believed that the most important inh,aled. As an alternative approach, studies
dust factor in disease development may be are continuing in this Institute using such
the physical dimension of the fibres, particu asbestos materials as are available that are
larly length (Stanton 1972: 1977). Numer likely to produce dust clouds of significantly
/
ous experimental studies have been under different fibre dimensions.rOne such type of
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Table 1. Dust sampling techniques
Type of sample Total dust Respirable dust
Fibre number
Description of sampling equipment
Open filter. 50 mm diameter sampling flow rate x Ittres/tnln facing downwards
Casella MRE 11 jA gravimetric* dust sampler
Vertical elutrlatorf
Open filter holder. 25 mm filter diameter In Getman head facing downwards sartorius membrane filter and nudepore polycarbonate membrane filter
* Dunmore el el. (1964)t Walton (1954). * Dodgson & Whittaker (1973). Asbestosis Research Council (1971). || Walton & Beckett (1977).
Sampling period
The full 7 h exposure
The full 7 h exposure
At least 1 full day
Of the order of 1 min
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gravimetric
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Infra-red spectroscopy*
counting iirnl sizing of fibres by phase contrast optical mlcroscope|| x 600
sizing of fibres by electron micro scopy x itMinn
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Table 2. Mass and fibre number concentrations for the dust clouds generated from wet dispersed chrysotile products and standard chrysodle textile yam
Dust" Exposure
WDCyam Factory WDC Chrysotile
yam Exp. WDC Exp. WDC
(Reversed daylight)
Type of measurement
Respirable dust concentration mg/m** (Means of daily estimations--see text)
Casella MRE 113A
(Incorporating a horizontal elutriator)
Vertical elutriator
gravimetric gravimetric
gravimetric fibres/ml
Infra-red absorption spectroscopy
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Total dust concentration
mg/m"1
Fibre number
'Snatch' samples on membrane
filters. Counted by phase contrast
opticnl micnwcnpy. Mean of too samples
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4-3 5-7
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428 108
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Table j. Mean levels of pulmonary Hbroslj produced by wet dispersed chrysolite duns and dust from ehrysoclle textile yam (ranges in brackets)
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yam** Pulmonary tumours and mesotheliomas produced by wet dispersed chrysotile dusts and dust from standard chrysotile textile
No. of rats examined Adenomas Total carcinomas
Adenocarcinomas Squamous carcinomas Mesotheliomas
WDC yam
41
*3 7 6 O
Factory WDC
lI 10
3 0
Chrysotile yam 42 <3
1
Exp. WDC
43
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Exp. WDC (Reversed Daylight)
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12 5 7 1
Controls 1
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Table s- Numbers of tumours occurring at sites other than lung
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Number of rats examined
Organ System
Digestive/peritoneal Urinogenita! Endocrine Musculo, skeletal and
Integumentary Reticuloendothelial/
vascular Totals
WDC yarn
41 SM
tI f
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1 66
Factory WDC
44
BM
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3 39
Chrysolite yam
42
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B. benign: M. malignant
Exp. WDC
43
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Exp. WDC (Reveraxi Daylight)
37
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Controls 1
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