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Toxicology of Industrial Compounds

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Figure 7.2 Continued<br />

where RCF products are manufactured show that exposures are generally<br />

below 1.0 f cm −3 , typically below 0.2 f cm −3 . In a recent study, RCF levels<br />

during various end-user operations ranged from 0.12 to 1.55 f cm −3 with<br />

an overall mean and SD <strong>of</strong> 0.74±0.49 f cm −3 (Lees et al., 1993b). Other<br />

end-user studies have indicated that RCF exposures can exceed 5 f cm −3 or<br />

higher if appropriate engineering controls and work practices are not<br />

followed (Schuller, 1985–1988).<br />

Fiber glass<br />

T.W.HESTERBERG ET AL. 107<br />

Recently, studies which examined human aerosol exposure to fiber glass in<br />

manufacturing, installation and removal, and in ambient air were reviewed<br />

(Hesterberg and Hart, 1994). In most cases, human exposures to airborne<br />

fiber glass during manufacturing and installation fell well below the OSHAproposed<br />

permissible exposure limit (PEL) <strong>of</strong> 1 f cm −3 air (OSHA, 1992).<br />

Airborne fiber concentrations during FG manufacturing operations are<br />

typically less than 0.2 f cm −3 , with the majority being less than 0.1 f cm −3 .<br />

Exceptions include manufacture <strong>of</strong> finer diameter fiber glass and blowing<br />

installation <strong>of</strong> loose fiber glass that is either milled or lacks binder. Airborne<br />

levels averaging greater than 1 f cm −3 have been reported in the production<br />

<strong>of</strong> finer diameter fiber glass (TIMA, 1990), while blowing installation <strong>of</strong><br />

loose fiber glass without binder resulted in a task length average (TLA) <strong>of</strong><br />

7.67 f cm −3 , and an 8-h TWA <strong>of</strong> 1.96 f cm −3 (Lees et al., 1993a). Blowing<br />

installation <strong>of</strong> loose mineral wool also resulted in higher aerosol levels; a

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