Literature DB >> 19037817

Efficiency of sampling and analysis of asbestos fibers on filter media: implications for exposure assessment.

Daniel A Vallero1, John R Kominsky, Michael E Beard, Owen S Crankshaw.   

Abstract

To measure airborne asbestos and other fibers, an air sample must represent the actual number and size of fibers. Typically, mixed cellulose ester (MCE, 0.45 or 0.8 microm pore size) and, to a much lesser extent, capillary-pore polycarbonate (PC, 0.4 microm pore size) membrane filters are used to collect airborne asbestos for count measurement and fiber size analysis. In this research study, chrysotile asbestos (fibers both shorter and longer than 5 microm) were generated in an aerosol chamber and sampled by 25 mm diameter MCE filter media to compare the fiber retention efficiency of 0.45 microm pore size filters vs. 0.8 microm pore size filter media. In addition, the effect of plasma etching times on fiber densities was evaluated. This study demonstrated a significant difference in fiber retention efficiency between 0.45 microm and 0.8 microm pore size MCE filters for asbestos aerosols (structures longer than or equal to 0.5 microm length). The fiber retention efficiency of a 0.45 microm pore size MCE filter is statistically significantly higher than that of the 0.8 microm pore size MCE filter. However, for asbestos structures longer than 5 microm, there is no statistically significant difference between the fiber retention efficiencies of the 0.45 microm and 0.8 microm pore size MCE filters. The mean density of asbestos fibers (longer than or equal to 0.5 microm) increased with etching time. Doubling the etching time increased the asbestos filter loading in this study by an average of 13%. The amount of plasma etching time had no effect on the filter loading for fibers longer than 5 microm. Many asbestos exposure risk models attribute health effects to fibers longer than 5 microm. In these models, both the 0.45 microm and 0.8 microm pore size MCE filter can produce suitable estimates of the airborne asbestos concentrations. However, some models suggest a more significant role for asbestos fibers shorter than 5 microm. Exposure monitoring for these models should consider only the 0.45 microm pore size MCE filters as recommended by the U.S. Environmental Protection Agency Asbestos Hazard Emergency Response Act (AHERA) protocol and other methods.

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Year:  2009        PMID: 19037817     DOI: 10.1080/15459620802577485

Source DB:  PubMed          Journal:  J Occup Environ Hyg        ISSN: 1545-9624            Impact factor:   2.155


  2 in total

1.  Dispersion and Filtration of Carbon Nanotubes (CNTs) and Measurement of Nanoparticle Agglomerates in Diesel Exhaust.

Authors:  Jing Wang; David Y H Pui
Journal:  Chem Eng Sci       Date:  2012-02-16       Impact factor: 4.311

2.  Health implications of atmospheric aerosols from asbestos-bearing road pavements traditionally used in Southern Brazil.

Authors:  Ricardo H M Godoi; Sérgio J Gonçalves; Célia Sayama; Gabriela Polezer; José M Reis Neto; Bálint Alföldy; René Van Grieken; Carlos A Riedi; Carlos I Yamamoto; Ana F L Godoi; László Bencs
Journal:  Environ Sci Pollut Res Int       Date:  2016-09-28       Impact factor: 4.223

  2 in total

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