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n survival -e '""8 e were 17 . 118 ,nly 6 of tiung
'bestosis (250/ * ,nce ^<o.0o,J:
lung
"'f: other 'that, eboma 0f th ere observed ire adenoma(a y adenomata mortem fi,,(|,,' mata occurred females as j,, >ese tumours. d maligJlai)( asbestos an*
none of t)1(.
nours at Sites 9
Malifr.
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ther tumours
t4 158
7 J 77
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:e between s treated * detail is `s with all he largest and conre ovary, rols, and rgans, 11 Towever,
alignant thelioma rcinoma rcinoma
EFFECTS OF INHALATION OF ASBESTOS IN RATS
Table IX.--Sites of Tumours Other than Lung
Asbestos treated
Control
Site/Tumour type
Digestive organs and peritoneum
Bone and skin Breast Ovary Other female gemto-urinary organs Male genito-urinary organs Intracranial Thymoma Lymphoma/leukaemia
Others
Benign
4 3 100 3 2 3 173 7
Malignant
3 4 0 7 8 8 1 1
63 thyroid mediastinum adrenal (4) salivary gland
thyroid
Benign
1 0 20 0 0 0 34 0
1 suprarenal
267
,,f the lung had a mesothelioma tunica from the worn hammer of the mill used
vaginalis. Mesotheliomata of the vagin- to produce the respirable fibre could
.,|is were seen in this and one other rat; have been a factor in the causation of
ilirre is no evidence to suggest an associa- the tumours. However, our results now
,jon with exposure to asbestos. Also, show that there is no need to invoke
in some cases there were secondaries, for such a hypothesis to explain the high
example, a synovioma had spread to the rate of lung tumours.
lung. In all such cases tumours have
The amount of chrysotile retained in
been classified by the primary site and the lungs did not show any clear increase
in the few cases of multiple malignant with dose in rats exposed for longer
tumours there was no difficulty in recog than 3 months. In two earlier experi
nizing the distinct types, i.e. one was ments (Wagner and Skidmore, 1965;
not a secondary of the other.
Morris et al., 1967) a higher airborne
dust concentration was used to give a
DISCUSSION
cumulative dose in 6 weeks similar to that given in the present experiment
Our finding that the asbestosis pro over 3 months. The weight of asbestos
duced by exposure progressed after cessa found in the lungs of rats exposed to
tion of exposure is in agreement with amphibole was 3 times greater than in
human experience but contrasts with those exposed to chrysotile. In the
the early inhalation experiments reported present experiments the ratio was 6 to 1
by Vorwald, Durkan and Pratt (1951) after 3 months, but increased with
in which progression did not occur. continuing exposure as the weight of
Wagner (1963) reported more asbestosis amphibole in the lungs continued to
with amosite than with chrysotile in increase, but the amount of chrysotile
guinea-pigs, rats and monkeys but our did not. The previous experiments had
experiments show that of the UICC shown that the rate of elimination of
standard reference samples amosite is the dust from the lungs was much greater
least fibrogenic in rats.
for chrysotile than for the amphiboles.
Gross et al. (1967) found lung cancers The present results may be explained on
in 25 of 72 rats which survived 16 months' this basis, the weight of chrysotile having
exposure to chrysotile dust at a mean reached equilibrium level, i.e. the rate of
concentration of 86 mg/m3 for 30 hours elimination equalling the rate of retention.
a week. They considered that contami
There are a number of features of the
nation of the asbestos by trace metals results presented above which we found
I