Ann. occup. Hyg., Vol. 37, No. 3, pp. 271-285, 1993
© 1993 British Occupational Hygiene Society
Published by Oxford University Press
research-article |
DUST FROM COTTON MANUFACTURE: CHANGING FROM STATIC TO PERSONAL SAMPLING

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*Health and Safety Executive, Research and Laboratory Services Division 403 Edgware Road, London NW2 6LN, U.K.
London School of Hygiene and Tropical Medicine London WC1E 7HT, U.K.
**Health and Safety Executive Quay Street, Manchester M3 3JB, U.K.
To whom correspondence should be addressed at: Health and Safety Executive, 1 Chepstow Place, London W2 4TF, U.K.
Several designs of personal samplers were tested for use to collect cotton dust. The IOM personal inhalable-dust sampler was selected because: (1) collection of the whole inhalable fraction was preferred, since all inhaled sizes are under suspicion as contributing to respiratory symptoms in cotton exposure; (2) this sampler is well characterized; and (3) it was found to be practicable in the environments examined. Gauze shields to exclude fly from the personal sampler were tried, but were rejected mainly because measurement of the whole inhalable fraction by a validated sampler was felt to be more appropriate.
A range of processes at a representative selection of mills was assessed by a hygiene team, and classified as clean or dirty in terms of present standards of control. This classification agreed well with subsequent measurements using the present method, which uses a large static sampler. A personal sampling survey then showed that in about two-thirds of clean processes personal exposure of at least 80% of those employed was less than about 22.5 mg m3 Only one-tenth of dirty processes met this standard.
Personal exposure correlates poorly with the present static method, as expected, but comparison of the results suggested that a mean background level of 0.5 mg m3 would correspond to a median personal exposure of about 2.2 mg m3. Side-by-side measurements by the background method differed by less than 0.15 mg m3 on about 95% of occasions.
NIVEN et al. (to be published) have compared the IOM head used in this study with the Manchester University sampler previously used by CINKOTAI et al. [Ann. occup. Hyg. 32, 103113 (1988)] to derive a relationship between personal exposure and prevalence of byssinotic symptoms in spinners. According to CINKOTAJ et al.'s results the concentrations of 22.5 mg m3 discussed would correspond to a prevalence of 35%. However, this prevalence probably reflects higher exposures in the past.
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