Assessing the Influence of Meteorological Parameters on the Performance of Polyurethane Foam-Based Passive Air Samplers

Polyurethane foam (PUF) disk passive air samplers were evaluated under field conditions to assess the effect of temperature and wind speed on the sampling rate for polycyclic aromatic hydrocarbons (PAHs), polychlorinated biphenyls (PCBs), and organochlorine pesticides (OCPs). Passive samples integra...

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Published inEnvironmental science & technology Vol. 42; no. 2; pp. 550 - 555
Main Authors Klánová, Jana, Èupr, Pavel, Kohoutek, Jiří, Harner, Tom
Format Journal Article
LanguageEnglish
Published Washington, DC American Chemical Society 15.01.2008
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ISSN0013-936X
1520-5851
DOI10.1021/es072098o

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Abstract Polyurethane foam (PUF) disk passive air samplers were evaluated under field conditions to assess the effect of temperature and wind speed on the sampling rate for polycyclic aromatic hydrocarbons (PAHs), polychlorinated biphenyls (PCBs), and organochlorine pesticides (OCPs). Passive samples integrated over 28-day periods were compared to high-volume air samples collected for 24 h, every 7 days. This provided a large data set of 42 passive sampling events and 168 high-volume samples over a 3-year period, starting in October 2003. Average PUF disk sampling rates for gas-phase chemicals was ∼7 m3 d−1 and comparable to previous reports. The high molecular weight PAHs, which are mainly particle-bound, experienced much lower sampling rates of ∼0.7 m3 d−1. This small rate was attributed to the ability of the sampling chamber to filter out coarse particles with only the fine/ultrafine fraction capable of penetration and collection on the PUF disk. Passive sampler-derived data were converted to equivalent air volumes (V EQ, m3) using the high-volume air measurement results. Correlations of V EQ against meteorological data collected on-site yielded different behavior for gas- and particle-associated compounds. For gas-phase chemicals, sampling rates varied by about a factor of 2 with temperature and wind speed. The higher sampling rates at colder temperatures were explained by the wind effect on sampling rates. Temperature and wind were strongly correlated with the greatest winds at colder temperatures. Mainly particle-phase compounds (namely, the high molecular weight PAHs) had more variable sampling rates. Sampling rates increased greatly at warmer temperatures as the high molecular weight PAH burden was shifted toward the gas phase and subject to higher gas-phase sampling rates. At colder temperatures, sampling rates were reduced as the partitioning of the high molecular weight PAHs was shifted toward the particle phase. The observed wind effect on sampling for the particle-phase compounds is believed to be tied to this strong temperature dependence on phase partitioning and hence sampling rate. For purposes of comparing passive sampler derived data for persistent organic pollutants, the factor of 2 variability observed for mainly gas-phase compounds is deemed to be acceptable in many instances for semiquantitative analysis. Depuration compounds may be used to improve accuracy and provide site-specific sampling rates, although this adds a level of complexity to the analysis. More research is needed to develop and test passive air samplers for particle-associated chemicals.
AbstractList Polyurethane foam (PUF) disk passive air samplers were evaluated under field conditionsto assessthe effect of temperature and wind speed on the sampling rate for polycyclic aromatic hydrocarbons (PAHs), polychlorinated biphenyls (PCBs), and organochlorine pesticides (OCPs). Passive samples integrated over 28-day periods were compared to high-volume air samples collected for 24 h, every 7 days. This provided a large data set of 42 passive sampling events and 168 high-volume samples over a 3-year period, starting in October 2003. Average PUF disk sampling rates for gas-phase chemicals was approximately 7 m3 d(-1) and comparable to previous reports. The high molecular weight PAHs, which are mainly particle-bound, experienced much lower sampling rates of approximately 0.7 m3 d(-1). This small rate was attributed to the ability of the sampling chamber to filter out coarse particles with only the fine/ultrafine fraction capable of penetration and collection on the PUF disk. Passive sampler-derived data were converted to equivalent air volumes (V(EQ), m3) using the high-volume air measurement results. Correlations of V(EQ) against meteorological data collected on-site yielded different behavior for gas- and particle-associated compounds. For gas-phase chemicals, sampling rates varied by about a factor of 2 with temperature and wind speed. The higher sampling rates at colder temperatures were explained bythe wind effecton sampling rates. Temperature and wind were strongly correlated with the greatest winds at coldertemperatures. Mainly particle-phase compounds (namely, the high molecular weight PAHs) had more variable sampling rates. Sampling rates increased greatly atwarmertemperatures as the high molecular weight PAH burden was shifted toward the gas phase and subject to higher gas-phase sampling rates. At colder temperatures, sampling rates were reduced as the partitioning of the high molecular weight PAHs was shifted toward the particle phase. The observed wind effect on sampling for the particle-phase compounds is believed to be tied to this strong temperature dependence on phase partitioning and hence sampling rate. For purposes of comparing passive sampler derived data for persistent organic pollutants, the factor of 2 variability observed for mainly gas-phase compounds is deemed to be acceptable in many instances for semiquantitative analysis. Depuration compounds may be used to improve accuracy and provide site-specific sampling rates, although this adds a level of complexity to the analysis. More research is needed to develop and test passive air samplers for particle-associated chemicals.Polyurethane foam (PUF) disk passive air samplers were evaluated under field conditionsto assessthe effect of temperature and wind speed on the sampling rate for polycyclic aromatic hydrocarbons (PAHs), polychlorinated biphenyls (PCBs), and organochlorine pesticides (OCPs). Passive samples integrated over 28-day periods were compared to high-volume air samples collected for 24 h, every 7 days. This provided a large data set of 42 passive sampling events and 168 high-volume samples over a 3-year period, starting in October 2003. Average PUF disk sampling rates for gas-phase chemicals was approximately 7 m3 d(-1) and comparable to previous reports. The high molecular weight PAHs, which are mainly particle-bound, experienced much lower sampling rates of approximately 0.7 m3 d(-1). This small rate was attributed to the ability of the sampling chamber to filter out coarse particles with only the fine/ultrafine fraction capable of penetration and collection on the PUF disk. Passive sampler-derived data were converted to equivalent air volumes (V(EQ), m3) using the high-volume air measurement results. Correlations of V(EQ) against meteorological data collected on-site yielded different behavior for gas- and particle-associated compounds. For gas-phase chemicals, sampling rates varied by about a factor of 2 with temperature and wind speed. The higher sampling rates at colder temperatures were explained bythe wind effecton sampling rates. Temperature and wind were strongly correlated with the greatest winds at coldertemperatures. Mainly particle-phase compounds (namely, the high molecular weight PAHs) had more variable sampling rates. Sampling rates increased greatly atwarmertemperatures as the high molecular weight PAH burden was shifted toward the gas phase and subject to higher gas-phase sampling rates. At colder temperatures, sampling rates were reduced as the partitioning of the high molecular weight PAHs was shifted toward the particle phase. The observed wind effect on sampling for the particle-phase compounds is believed to be tied to this strong temperature dependence on phase partitioning and hence sampling rate. For purposes of comparing passive sampler derived data for persistent organic pollutants, the factor of 2 variability observed for mainly gas-phase compounds is deemed to be acceptable in many instances for semiquantitative analysis. Depuration compounds may be used to improve accuracy and provide site-specific sampling rates, although this adds a level of complexity to the analysis. More research is needed to develop and test passive air samplers for particle-associated chemicals.
Polyurethane foam (PUF) disk passive air samplers were evaluated under field conditions to assess the effect of temperature and wind speed on the sampling rate for polycyclic aromatic hydrocarbons (PAHs), polychlorinated biphenyls (PCBs), and organochlorine pesticides (OCPs). Passive samples integrated over 28-day periods were compared to high-volume air samples collected for 24 h, every 7 days. This provided a large data set of 42 passive sampling events and 168 high-volume samples over a 3-year period, starting in October 2003. Average PUF disk sampling rates for gas-phase chemicals was ...7 m... d... and comparable to previous reports. The high molecular weight PAHs, which are mainly particle-bound, experienced much lower sampling rates of ...0.7 m... d... This small rate was attributed to the ability of the sampling chamber to filter out coarse particles with only the fine/ultrafine fraction capable of penetration and collection on the PUF disk. Passive sampler-derived data were converted to equivalent air volumes (V..., m...) using the high-volume air measurement results. Correlations of V... against meteorological data collected on-site yielded different behavior for gas- and particle-associated compounds. For gas-phase chemicals, sampling rates varied by about a factor of 2 with temperature and wind speed. The higher sampling rates at colder temperatures were explained by the wind effect on sampling rates. Temperature and wind were strongly correlated with the greatest winds at colder temperatures. Mainly particle-phase compounds (namely, the high molecular weight PAHs) had more variable sampling rates. Sampling rates increased greatly at warmer temperatures as the high molecular weight PAH burden was shifted toward the gas phase and subject to higher gas-phase sampling rates. At colder temperatures, sampling rates were reduced as the partitioning of the high molecular weight PAHs was shifted toward the particle phase. The observed wind effect on sampling for the particle-phase compounds is believed to be tied to this strong temperature dependence on phase partitioning and hence sampling rate. For purposes of comparing passive sampler derived data for persistent organic pollutants, the factor of 2 variability observed for mainly gas-phase compounds is deemed to be acceptable in many instances for semiquantitative analysis. Depuration compounds may be used to improve accuracy and provide site-specific sampling rates, although this adds a level of complexity to the analysis. More research is needed to develop and test passive air samplers for particle-associated chemicals. (ProQuest: ... denotes formulae/symbols omitted.)
Polyurethane foam (PUF) disk passive air samplers were evaluated under field conditions to assess the effect of temperature and wind speed on the sampling rate for polycyclic aromatic hydrocarbons (PAHs), polychlorinated biphenyls (PCBs), and organochlorine pesticides (OCPs). Passive samples integrated over 28-day periods were compared to high-volume air samples collected for 24 h, every 7 days. This provided a large data set of 42 passive sampling events and 168 high-volume samples over a 3-year period, starting in October 2003. Average PUF disk sampling rates for gas-phase chemicals was ∼7 m3 d−1 and comparable to previous reports. The high molecular weight PAHs, which are mainly particle-bound, experienced much lower sampling rates of ∼0.7 m3 d−1. This small rate was attributed to the ability of the sampling chamber to filter out coarse particles with only the fine/ultrafine fraction capable of penetration and collection on the PUF disk. Passive sampler-derived data were converted to equivalent air volumes (V EQ, m3) using the high-volume air measurement results. Correlations of V EQ against meteorological data collected on-site yielded different behavior for gas- and particle-associated compounds. For gas-phase chemicals, sampling rates varied by about a factor of 2 with temperature and wind speed. The higher sampling rates at colder temperatures were explained by the wind effect on sampling rates. Temperature and wind were strongly correlated with the greatest winds at colder temperatures. Mainly particle-phase compounds (namely, the high molecular weight PAHs) had more variable sampling rates. Sampling rates increased greatly at warmer temperatures as the high molecular weight PAH burden was shifted toward the gas phase and subject to higher gas-phase sampling rates. At colder temperatures, sampling rates were reduced as the partitioning of the high molecular weight PAHs was shifted toward the particle phase. The observed wind effect on sampling for the particle-phase compounds is believed to be tied to this strong temperature dependence on phase partitioning and hence sampling rate. For purposes of comparing passive sampler derived data for persistent organic pollutants, the factor of 2 variability observed for mainly gas-phase compounds is deemed to be acceptable in many instances for semiquantitative analysis. Depuration compounds may be used to improve accuracy and provide site-specific sampling rates, although this adds a level of complexity to the analysis. More research is needed to develop and test passive air samplers for particle-associated chemicals.
Polyurethane foam (PUF) disk passive air samplers were evaluated under field conditionsto assessthe effect of temperature and wind speed on the sampling rate for polycyclic aromatic hydrocarbons (PAHs), polychlorinated biphenyls (PCBs), and organochlorine pesticides (OCPs). Passive samples integrated over 28-day periods were compared to high-volume air samples collected for 24 h, every 7 days. This provided a large data set of 42 passive sampling events and 168 high-volume samples over a 3-year period, starting in October 2003. Average PUF disk sampling rates for gas-phase chemicals was approximately 7 m3 d(-1) and comparable to previous reports. The high molecular weight PAHs, which are mainly particle-bound, experienced much lower sampling rates of approximately 0.7 m3 d(-1). This small rate was attributed to the ability of the sampling chamber to filter out coarse particles with only the fine/ultrafine fraction capable of penetration and collection on the PUF disk. Passive sampler-derived data were converted to equivalent air volumes (V(EQ), m3) using the high-volume air measurement results. Correlations of V(EQ) against meteorological data collected on-site yielded different behavior for gas- and particle-associated compounds. For gas-phase chemicals, sampling rates varied by about a factor of 2 with temperature and wind speed. The higher sampling rates at colder temperatures were explained bythe wind effecton sampling rates. Temperature and wind were strongly correlated with the greatest winds at coldertemperatures. Mainly particle-phase compounds (namely, the high molecular weight PAHs) had more variable sampling rates. Sampling rates increased greatly atwarmertemperatures as the high molecular weight PAH burden was shifted toward the gas phase and subject to higher gas-phase sampling rates. At colder temperatures, sampling rates were reduced as the partitioning of the high molecular weight PAHs was shifted toward the particle phase. The observed wind effect on sampling for the particle-phase compounds is believed to be tied to this strong temperature dependence on phase partitioning and hence sampling rate. For purposes of comparing passive sampler derived data for persistent organic pollutants, the factor of 2 variability observed for mainly gas-phase compounds is deemed to be acceptable in many instances for semiquantitative analysis. Depuration compounds may be used to improve accuracy and provide site-specific sampling rates, although this adds a level of complexity to the analysis. More research is needed to develop and test passive air samplers for particle-associated chemicals.
Polyurethane foam (PUF) disk passive air samplers were evaluated under field conditions to assess the effect of temperature and wind speed on the sampling rate for polycyclic aromatic hydrocarbons (PAHs), polychlorinated biphenyls (PCBs), and organochlorine pesticides (OCPs). Passive samples integrated over 28-day periods were compared to high-volume air samples collected for 24 h, every 7 days. This provided a large data set of 42 passive sampling events and 168 high-volume samples over a 3-year period, starting in October 2003. Average PUF disk sampling rates for gas-phase chemicals was similar to 7 m super(3) d super(-1) and comparable to previous reports. The high molecular weight PAHs, which are mainly particle-bound, experienced much lower sampling rates of similar to 0.7 m super(3) d super(-1). This small rate was attributed to the ability of the sampling chamber to filter out coarse particles with only the fine/ultrafine fraction capable of penetration and collection on the PUF disk. Passive sampler-derived data were converted to equivalent air volumes (V sub(EQ), m super(3)) using the high-volume air measurement results. Correlations of V sub(EQ) against meteorological data collected on-site yielded different behavior for gas- and particle-associated compounds. For gas-phase chemicals, sampling rates varied by about a factor of 2 with temperature and wind speed. The higher sampling rates at colder temperatures were explained by the wind effect on sampling rates. Temperature and wind were strongly correlated with the greatest winds at colder temperatures. Mainly particle-phase compounds (namely, the high molecular weight PAHs) had more variable sampling rates. Sampling rates increased greatly at warmer temperatures as the high molecular weight PAH burden was shifted toward the gas phase and subject to higher gas-phase sampling rates. At colder temperatures, sampling rates were reduced as the partitioning of the high molecular weight PAHs was shifted toward the particle phase. The observed wind effect on sampling for the particle-phase compounds is believed to be tied to this strong temperature dependence on phase partitioning and hence sampling rate. For purposes of comparing passive sampler derived data for persistent organic pollutants, the factor of 2 variability observed for mainly gas-phase compounds is deemed to be acceptable in many instances for semiquantitative analysis. Depuration compounds may be used to improve accuracy and provide site-specific sampling rates, although this adds a level of complexity to the analysis. More research is needed to develop and test passive air samplers for particle-associated chemicals.
Author Kohoutek, Jiří
Klánová, Jana
Èupr, Pavel
Harner, Tom
Author_xml – sequence: 1
  givenname: Jana
  surname: Klánová
  fullname: Klánová, Jana
  email: klanova@recetox.muni.cz
– sequence: 2
  givenname: Pavel
  surname: Èupr
  fullname: Èupr, Pavel
– sequence: 3
  givenname: Jiří
  surname: Kohoutek
  fullname: Kohoutek, Jiří
– sequence: 4
  givenname: Tom
  surname: Harner
  fullname: Harner, Tom
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Cites_doi 10.1021/es035292t
10.1016/j.envpol.2005.12.047
10.1021/es040302r
10.1016/j.envpol.2005.12.048
10.1016/j.envpol.2005.12.045
10.1021/es060872m
10.1016/j.envpol.2005.12.057
10.1039/B700750G
10.1021/je0155148
10.1021/es026166c
10.1039/B701096F
10.1021/es034705n
10.1021/es048340y
10.1021/es049260x
10.1021/es0348849
10.1021/es051397f
10.1021/es020635t
10.1016/j.envpol.2005.12.042
10.1016/j.chemosphere.2005.12.018
10.1016/j.envpol.2005.12.053
10.1021/es048907a
10.1016/j.atmosenv.2004.09.022
10.1021/es0209215
10.1021/es062352x
10.1021/es049065i
10.1897/03-420
10.1021/es0504183
10.1016/j.atmosenv.2004.06.036
10.1016/j.envpol.2005.12.044
10.1021/es060447t
ContentType Journal Article
Copyright Copyright © 2008 American Chemical Society
2008 INIST-CNRS
Copyright American Chemical Society Jan 15, 2008
Copyright_xml – notice: Copyright © 2008 American Chemical Society
– notice: 2008 INIST-CNRS
– notice: Copyright American Chemical Society Jan 15, 2008
DBID BSCLL
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Keywords Atmospheric condition
Meteorological observation
Hydrocarbon
Pollutant behavior
Pesticides
Temperature effect
Polychlorobiphenyls
Wind effect
Polycyclic aromatic compound
Coarse particle
Persistent organic pollutant
Passive detection
Volume measurement
Foam
Correlation analysis
Organochlorine compounds
Chlorine Organic compounds
Sampler
Aerosols
Air pollution
Phase partition
Sampling
Organic compounds
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References Harner T. (ref17/cit17) 2003; 37
ref3/cit3
Harner T. (ref21/cit21) 2006; 144
Cupr P. (ref12/cit12) 2006; 144
Bidleman T. F. (ref36/cit36) 2000
Harner T. (ref20/cit20) 2006; 40
Shoeib M. (ref26/cit26) 2005; 39
Tuduri L. (ref28/cit28) 2006; 144
ref32/cit32
Lee S. C. (ref29/cit29) 2007; 41
Jaward F. M. (ref6/cit6) 2004; 23
ref2/cit2
Farrar N. J. (ref14/cit14) 2006; 144
Harner T. (ref18/cit18) 2004; 38
Holoubek I. (ref33/cit33) 2007; 9
Gouin T. (ref15/cit15) 2005; 39
Jaward F. M. (ref7/cit7) 2004; 38
Harner T. (ref19/cit19) 2006; 64
Bartkow M. E. (ref9/cit9) 2004; 38
Klánová J. (ref31/cit31) 2007
Wania F. (ref5/cit5) 2003; 37
Klanova J. (ref11/cit11) 2006; 144
Gouin T. (ref16/cit16) 2005; 39
Thomas J. (ref27/cit27) 2006; 144
Bartkow M. E. (ref10/cit10) 2004; 38
Klánová J. (ref30/cit30) 2007
Pozo K. (ref25/cit25) 2006; 40
Motelay-Massei A. (ref23/cit23) 2005; 39
Harner T. (ref22/cit22) 2006; 144
ref1/cit1
Jaward F. M. (ref8/cit8) 2004; 38
Wilford B. H. (ref35/cit35) 2004; 38
Lei Y. D. (ref37/cit37) 2002; 47
Shoeib M. (ref4/cit4) 2002; 36
Pozo K. (ref24/cit24) 2004; 38
Holoubek I. (ref34/cit34) 2007; 9
Farrar N. J. (ref13/cit13) 2005; 39
References_xml – volume: 38
  start-page: 2523
  year: 2004
  ident: ref7/cit7
  publication-title: Environ. Sci. Technol.
  doi: 10.1021/es035292t
– volume: 144
  start-page: 377
  year: 2006
  ident: ref28/cit28
  publication-title: Environ. Pollut.
  doi: 10.1016/j.envpol.2005.12.047
– ident: ref2/cit2
– volume: 38
  start-page: 4474
  year: 2004
  ident: ref18/cit18
  publication-title: Environ. Sci. Technol.
  doi: 10.1021/es040302r
– volume: 144
  start-page: 393
  year: 2006
  ident: ref11/cit11
  publication-title: Environ. Pollut.
  doi: 10.1016/j.envpol.2005.12.048
– volume: 144
  start-page: 406
  year: 2006
  ident: ref12/cit12
  publication-title: Environ. Pollut.
  doi: 10.1016/j.envpol.2005.12.045
– volume: 40
  start-page: 5333
  year: 2006
  ident: ref20/cit20
  publication-title: Environ. Sci. Technol.
  doi: 10.1021/es060872m
– volume-title: Property Estimation Methods for Chemicals: Handbook of Environmental and Health Sciences
  year: 2000
  ident: ref36/cit36
– volume: 144
  start-page: 423
  year: 2006
  ident: ref14/cit14
  publication-title: Environ. Pollut.
  doi: 10.1016/j.envpol.2005.12.057
– volume: 9
  start-page: 557
  year: 2007
  ident: ref34/cit34
  publication-title: J. Environ. Monit.
  doi: 10.1039/B700750G
– volume: 47
  start-page: 801
  year: 2002
  ident: ref37/cit37
  publication-title: J. Chem. Eng. Data
  doi: 10.1021/je0155148
– volume: 37
  start-page: 1352
  year: 2003
  ident: ref5/cit5
  publication-title: Environ. Sci. Technol.
  doi: 10.1021/es026166c
– ident: ref32/cit32
– volume: 9
  start-page: 564
  year: 2007
  ident: ref33/cit33
  publication-title: J. Environ. Monit.
  doi: 10.1039/B701096F
– volume: 38
  start-page: 34
  year: 2004
  ident: ref8/cit8
  publication-title: Environ. Sci. Technol.
  doi: 10.1021/es034705n
– volume: 39
  start-page: 6599
  year: 2005
  ident: ref26/cit26
  publication-title: Environ. Sci. Technol.
  doi: 10.1021/es048340y
– volume: 38
  start-page: 5312
  year: 2004
  ident: ref35/cit35
  publication-title: Environ. Sci. Technol.
  doi: 10.1021/es049260x
– volume: 38
  start-page: 2701
  year: 2004
  ident: ref10/cit10
  publication-title: Environ. Sci. Technol.
  doi: 10.1021/es0348849
– volume: 39
  start-page: 9115
  year: 2005
  ident: ref15/cit15
  publication-title: Environ. Sci. Technol.
  doi: 10.1021/es051397f
– volume: 36
  start-page: 4142
  year: 2002
  ident: ref4/cit4
  publication-title: Environ. Sci. Technol.
  doi: 10.1021/es020635t
– volume: 144
  start-page: 384
  year: 2006
  ident: ref27/cit27
  publication-title: Environ. Pollut.
  doi: 10.1016/j.envpol.2005.12.042
– ident: ref1/cit1
– volume-title: POPs concentrations in the ambient air of the Central and Eastern Europe (CEE): Application of the passive air sampling technique as a tool for trend determination and effectiveness evaluation of international conventions. Part II: Pilot study for development of the monitoring network in the Central and Eastern Europe (MONET_CEEC)
  year: 2007
  ident: ref31/cit31
– volume-title: POPs concentrations in the ambient air of the Central and Eastern Europe (CEE): Application of the passive air sampling technique as a tool for trend determination and effectiveness evaluation of international conventions. Part I: Model monitoring network in the Czech Republic (MONET_CZ)
  year: 2007
  ident: ref30/cit30
– volume: 64
  start-page: 262
  year: 2006
  ident: ref19/cit19
  publication-title: Chemosphere
  doi: 10.1016/j.chemosphere.2005.12.018
– volume: 144
  start-page: 445
  year: 2006
  ident: ref22/cit22
  publication-title: Environ. Pollut.
  doi: 10.1016/j.envpol.2005.12.053
– volume: 39
  start-page: 42
  year: 2005
  ident: ref13/cit13
  publication-title: Environ. Sci. Technol.
  doi: 10.1021/es048907a
– volume: 39
  start-page: 151
  year: 2005
  ident: ref16/cit16
  publication-title: Atmos. Environ.
  doi: 10.1016/j.atmosenv.2004.09.022
– volume: 37
  start-page: 2486
  year: 2003
  ident: ref17/cit17
  publication-title: Environ. Sci. Technol.
  doi: 10.1021/es0209215
– ident: ref3/cit3
– volume: 41
  start-page: 2680
  year: 2007
  ident: ref29/cit29
  publication-title: Environ. Sci. Technol.
  doi: 10.1021/es062352x
– volume: 38
  start-page: 6529
  year: 2004
  ident: ref24/cit24
  publication-title: Environ. Sci. Technol.
  doi: 10.1021/es049065i
– volume: 23
  start-page: 1355
  year: 2004
  ident: ref6/cit6
  publication-title: Environ. Toxicol. Chem.
  doi: 10.1897/03-420
– volume: 39
  start-page: 5763
  year: 2005
  ident: ref23/cit23
  publication-title: Environ. Sci. Technol.
  doi: 10.1021/es0504183
– volume: 38
  start-page: 5983
  year: 2004
  ident: ref9/cit9
  publication-title: Atmos. Environ.
  doi: 10.1016/j.atmosenv.2004.06.036
– volume: 144
  start-page: 361
  year: 2006
  ident: ref21/cit21
  publication-title: Environ. Pollut.
  doi: 10.1016/j.envpol.2005.12.044
– volume: 40
  start-page: 4867
  year: 2006
  ident: ref25/cit25
  publication-title: Environ. Sci. Technol.
  doi: 10.1021/es060447t
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Snippet Polyurethane foam (PUF) disk passive air samplers were evaluated under field conditions to assess the effect of temperature and wind speed on the sampling rate...
Polyurethane foam (PUF) disk passive air samplers were evaluated under field conditionsto assessthe effect of temperature and wind speed on the sampling rate...
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SubjectTerms Air Pollutants - analysis
Applied sciences
Czech Republic
Environmental Measurements Methods
Environmental Monitoring - instrumentation
Environmental Monitoring - methods
Exact sciences and technology
Hydrocarbons, Chlorinated - analysis
Meteorology
Molecular weight
PCB
Plastic foams
Pollution
Polychlorinated biphenyls
Polycyclic Aromatic Hydrocarbons - analysis
Polyurethane
Polyurethanes
Temperature
Temperature effects
Wind
Title Assessing the Influence of Meteorological Parameters on the Performance of Polyurethane Foam-Based Passive Air Samplers
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