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Toxicology of Industrial Compounds

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118 PULMONARY TOXICITY STUDIES WITH MAN-MADE ORGANIC FIBRES<br />

lung and mesothelial cell proliferation at 0 hrs, 5 days 1, 3, 6 and 12<br />

months postexposure.<br />

Fibre preparation and inhalation exposure<br />

Ultrafine Kevlar ® p-aramid fibrils were supplied by DuPont Fibres. A<br />

special preparation <strong>of</strong> respirable p-aramid fibrils which had been prepared<br />

for the 2-year inhalation study (Lee et al., 1988) was utilized for this study.<br />

Bulk Canadian chrysotile asbestos fibres were obtained from Mr John<br />

Addison <strong>of</strong> the Institute <strong>of</strong> Occupational Medicine in Edinburgh, Scotland.<br />

Attempts were made to size-separate the bulk fibre preparation (i.e.<br />

selectively enhance the percentages <strong>of</strong> long fibres while removing the short<br />

fibres) by placing the fibres in a rotating sieve shaker and sieving through a<br />

series <strong>of</strong> metal mesh screens. The fraction containing the longer fibres (and<br />

a number <strong>of</strong> short fibres) was collected and generated for inhalation<br />

studies; fibres were collected on a filter and dimensional analysis (i.e. length<br />

and diameter assessments) was performed using scanning electron<br />

microscopy. The results showed that this technique was partially successful<br />

as the median and mean lengths <strong>of</strong> fibres were increased from 3 and 5 µm,<br />

respectively, in the original bulk sample to 6 and 9 µm in the generated<br />

sample preparation. The median lengths and diameters <strong>of</strong> p-aramid fibrils<br />

used in the study were 9 µm and 0.3 µm, respectively.<br />

The methods for aerosol generation <strong>of</strong> p-aramid fibrils have previously<br />

been reported (Warheit et al., 1992). Final mean fibre concentrations for<br />

the p-aramid exposures were 772 and 419 f cm −3 .<br />

Aerosols <strong>of</strong> chrysotile asbestos fibres were generated in a similar<br />

manner, i.e. with a binfeeder and baffles, but without the microjet<br />

apparatus. Final mean fibre concentrations for the chrysotile asbestos<br />

exposures were 782 and 458 f cm −3 . Fibre lung burdens were quantified<br />

from digested lung tissue <strong>of</strong> animals sacrificed immediately after the end <strong>of</strong><br />

the 2-week exposure.<br />

Pulmonary lavage and biochemical assays on lavaged<br />

fluids<br />

Bronchoalveolar lavage procedures, cell quantification, and biochemical<br />

assays were conducted according to methods previously described (Warheit<br />

et al., 1984a, 1992). In addition, the methods for measuring lactate<br />

dehydrogenase (LDH), N-acetyl-β-glucosaminidase (NAG), and alkaline<br />

phosphatase (ALP) and protein in BAL fluids have been reported (Warheit<br />

et al., 1992).

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