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A Pilot Study: The UNC Passive Aerosol Sampler in a Working Environment

OBJECTIVES: Dust is generally sampled on a filter using air pumps, but passive sampling could be a cost-effective alternative. One promising passive sampler is the University of North Carolina passive aerosol sampler (UNC sampler). The aim of this study is to characterize and compare the UNC sampler...

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Autores principales: Shirdel, Mariam, Wingfors, Håkan, Andersson, Britt M, Sommar, Johan N, Bergdahl, Ingvar A, Liljelind, Ingrid E
Formato: Online Artículo Texto
Lenguaje:English
Publicado: Oxford University Press 2017
Materias:
Acceso en línea:https://www.ncbi.nlm.nih.gov/pmc/articles/PMC6824523/
https://www.ncbi.nlm.nih.gov/pubmed/29028256
http://dx.doi.org/10.1093/annweh/wxx067
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author Shirdel, Mariam
Wingfors, Håkan
Andersson, Britt M
Sommar, Johan N
Bergdahl, Ingvar A
Liljelind, Ingrid E
author_facet Shirdel, Mariam
Wingfors, Håkan
Andersson, Britt M
Sommar, Johan N
Bergdahl, Ingvar A
Liljelind, Ingrid E
author_sort Shirdel, Mariam
collection PubMed
description OBJECTIVES: Dust is generally sampled on a filter using air pumps, but passive sampling could be a cost-effective alternative. One promising passive sampler is the University of North Carolina passive aerosol sampler (UNC sampler). The aim of this study is to characterize and compare the UNC sampler’s performance with PM(10) and PM(2.5) impactors in a working environment. METHODS: Area sampling was carried out at different mining locations using UNC samplers in parallel with PM(2.5) and PM(10) impactors. Two different collection surfaces, polycarbonate (PC) and carbon tabs (CT), were employed for the UNC sampling. Sampling was carried out for 4–25 hours. RESULTS: The UNC samplers underestimated the concentrations compared to PM(10) and PM(2.5) impactor data. At the location with the highest aerosol concentration, the time-averaged mean of PC showed 24% and CT 35% of the impactor result for PM(2.5). For PM(10), it was 39% with PC and 58% with CT. Sample blank values differed between PC and CT. For PM(2.5), PC blank values were ~7 times higher than those of CT, but only 1.8 times higher for PM(10). The blank variations were larger for PC than for CT. CONCLUSIONS: Particle mass concentrations appear to be underestimated by the UNC sampler compared to impactors, more so for PM(2.5) than for PM(10). CT may be preferred as a collection surface because the blank values were lower and less variable than for PC. Future validations in the working environment should include respirable dust sampling.
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spelling pubmed-68245232019-11-06 A Pilot Study: The UNC Passive Aerosol Sampler in a Working Environment Shirdel, Mariam Wingfors, Håkan Andersson, Britt M Sommar, Johan N Bergdahl, Ingvar A Liljelind, Ingrid E Ann Work Expo Health Short Communications OBJECTIVES: Dust is generally sampled on a filter using air pumps, but passive sampling could be a cost-effective alternative. One promising passive sampler is the University of North Carolina passive aerosol sampler (UNC sampler). The aim of this study is to characterize and compare the UNC sampler’s performance with PM(10) and PM(2.5) impactors in a working environment. METHODS: Area sampling was carried out at different mining locations using UNC samplers in parallel with PM(2.5) and PM(10) impactors. Two different collection surfaces, polycarbonate (PC) and carbon tabs (CT), were employed for the UNC sampling. Sampling was carried out for 4–25 hours. RESULTS: The UNC samplers underestimated the concentrations compared to PM(10) and PM(2.5) impactor data. At the location with the highest aerosol concentration, the time-averaged mean of PC showed 24% and CT 35% of the impactor result for PM(2.5). For PM(10), it was 39% with PC and 58% with CT. Sample blank values differed between PC and CT. For PM(2.5), PC blank values were ~7 times higher than those of CT, but only 1.8 times higher for PM(10). The blank variations were larger for PC than for CT. CONCLUSIONS: Particle mass concentrations appear to be underestimated by the UNC sampler compared to impactors, more so for PM(2.5) than for PM(10). CT may be preferred as a collection surface because the blank values were lower and less variable than for PC. Future validations in the working environment should include respirable dust sampling. Oxford University Press 2017-10 2017-08-05 /pmc/articles/PMC6824523/ /pubmed/29028256 http://dx.doi.org/10.1093/annweh/wxx067 Text en © The Author 2017. Published by Oxford University Press on behalf of the British Occupational Hygiene Society. http://creativecommons.org/licenses/by/4.0 This is an Open Access article distributed under the terms of the Creative Commons Attribution License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted reuse, distribution, and reproduction in any medium, provided the original work is properly cited.
spellingShingle Short Communications
Shirdel, Mariam
Wingfors, Håkan
Andersson, Britt M
Sommar, Johan N
Bergdahl, Ingvar A
Liljelind, Ingrid E
A Pilot Study: The UNC Passive Aerosol Sampler in a Working Environment
title A Pilot Study: The UNC Passive Aerosol Sampler in a Working Environment
title_full A Pilot Study: The UNC Passive Aerosol Sampler in a Working Environment
title_fullStr A Pilot Study: The UNC Passive Aerosol Sampler in a Working Environment
title_full_unstemmed A Pilot Study: The UNC Passive Aerosol Sampler in a Working Environment
title_short A Pilot Study: The UNC Passive Aerosol Sampler in a Working Environment
title_sort pilot study: the unc passive aerosol sampler in a working environment
topic Short Communications
url https://www.ncbi.nlm.nih.gov/pmc/articles/PMC6824523/
https://www.ncbi.nlm.nih.gov/pubmed/29028256
http://dx.doi.org/10.1093/annweh/wxx067
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