M. Albin et al., RETENTION PATTERNS OF ASBESTOS FIBERS IN LUNG-TISSUE AMONG ASBESTOS-CEMENT WORKERS, Occupational and environmental medicine, 51(3), 1994, pp. 205-211
Retention patterns in lung tissue (determined by transmission electron
microscopy and energy dispersive spectrometry) of chrysotile, tremoli
te, and crocidolite fibres were analysed in 69 dead asbestos cement wo
rkers and 96 referents. There was an accumulation of tremolite with ti
me of employment. Among workers who died within three years of the end
of exposure, the 13 with high tremolite concentrations had a signific
antly longer duration of exposure than seven in a low to intermediate
category (medians 32 v 20 years; p = 0.018, one sided). Crocidolite sh
owed similar patterns of accumulation. In workers who died more than t
hree years after the end of exposure, there were no correlations betwe
en concentrations of amphibole fibres and time between the end of expo
sure and death. Chrysotile concentrations among workers who died short
ly after the end of exposure were higher than among the referents (med
ian difference in concentrations 13 million fibres (f)/g dry weight; p
= 0.033, one sided). No quantitative differences in exposure (duratio
n or intensity) could be shown between workers with high and low to in
termediate concentrations. Interestingly, all seven workers who had ha
d a high intensity at the end of exposure (>2.5 f/ml), had low to inte
rmediate chrysotile concentrations at death, whereas those with low ex
posure were evenly distributed (31 subjects in both concentration cate
gories); hence, there was a dependence between last intensity of expos
ure and chrysotile concentration (p = 0.014). Among 14 workers with a
high average intensity of exposure, both those (n = 5) with high tissu
e concentrations of chrysotile and those (n = 10) with high tissue con
centrations of tremolite fibres had more pronounced fibrosis than thos
e with low to intermediate concentrations (median fibrosis grades for
chrysotile: 2 v 1, p = 0.021; for tremolite: 2 v 0.5, p = 0.012). Addi
tionally, workers who died shortly after the end of exposure with high
concentrations of chrysotile and crocidolite had smoked more than tho
se with low to intermediate concentrations (medians for chrysotile 35
v 15 pack-years, p = 0.030; for crocidolite 37 v 15 pack-years, p = 0.
012). The present data indicate that chrysotile has a relatively rapid
turnover in human lungs, whereas the amphiboles, tremolite and crocid
olite, have a slower turnover. Further, chrysotile retention may be de
pendent on dose rate. Chrysotile and crocidolite deposition and retent
ion may be increased by tobacco smoking; chrysotile and tremolite by f
ibrosis.