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Occupational Exposure to Carbon Nanotubes and Nanofibers

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As part of the evaluation of worker exposures <strong>to</strong>CNT <strong>and</strong> CNF, ‘background’ samples for EC determinationshould be collected outdoors (or atair intakes of the facility) <strong>and</strong> at indoor locationswhere exposure <strong>to</strong> CNT or CNF is unlikely. The ECconcentrations (using Method 5040) determinedfrom ‘background’ samples should be subtractedfrom the EC personal sample results <strong>to</strong> determinewhether worker exposures exceeded the REL. Initially,more samples may be required <strong>to</strong> characterizethe workplace thoroughly. This initial assessmentwill help refine the sampling approach <strong>and</strong> determinewhether EC interference is an issue. Carefulconsideration of environmental background is essential.For example, outdoor EC may sometimesbe higher than indoor background depending onthe facility’s air h<strong>and</strong>ling system. If so, the indoorEC background may be more representative of area<strong>and</strong> worker samples.In workplaces where exposure <strong>to</strong> other types of EC(e.g., diesel soot, carbon black) may occur, the initialevaluation of a worker’s exposure should includethe simultaneous collection of a personal respirableEC sample <strong>and</strong> a personal sample for electron microscopyanalysis (e.g., TEM, SEM). Electron microscopyanalysis, in conjunction with energy dispersivex-ray spectroscopy (EDS), can be used forCNT <strong>and</strong> CNF identification. In addition, considerationshould be given <strong>to</strong> the sizing <strong>and</strong> counting ofCNT <strong>and</strong> CNF structures during electron microscopyanalysis should future efforts <strong>to</strong> control occupationalexposures be based on a different exposuremetric (e.g., number concentrations of airborneCNT <strong>and</strong> CNF structures in a given size bin). Whileno specific electron microscopy (e.g., TEM, SEM)method exists for the sizing <strong>and</strong> counting of CNT<strong>and</strong> CNF structures, methods used in the analysisof other ‘fibrous’ materials are available [NIOSH1994a; ISO 1999, 2002] <strong>and</strong> could be adapted in thecharacterization of exposures.NIOSH investiga<strong>to</strong>rs have conducted a numberof surveys at CNT <strong>and</strong> CNF producers <strong>and</strong>/orsecondary users [Evans et al. 2010; Birch 2011a;Birch et al. 2011b; Dahm et al. 2011]. In manycases ‘background’ EC concentrations were

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