Monitoring and modeling of PCB dry deposition in urban area

Dry deposition and air sampling were undertaken simultaneously in the ambient air of an urban site by using several dry deposition plates, two MOUDIs (micro-orifice uniform deposited impactors), one NRI (Noll rotary impactor) and several PS-1 (General Metal Work, PS-1) samplers from January to May 1...

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Published inJournal of hazardous materials Vol. 49; no. 1; pp. 57 - 88
Main Authors Lee, Wen-Jhy, Su, Chun-Ching, Sheu, Hwey-Lin, Fan, Yi-Chin, Chao, How-Ran, Fang, Guor-Cheng
Format Journal Article
LanguageEnglish
Published Amsterdam Elsevier B.V 1996
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Abstract Dry deposition and air sampling were undertaken simultaneously in the ambient air of an urban site by using several dry deposition plates, two MOUDIs (micro-orifice uniform deposited impactors), one NRI (Noll rotary impactor) and several PS-1 (General Metal Work, PS-1) samplers from January to May 1994 in Tainan City, Taiwan. The dry deposition plate, which had a smooth surface, was always pointed into the wind. The PCB (polychlorinated biphenyl) congeners were analyzed primarily by using a gas chromatograph with a 63Ni electron capture detector (ECD). The measured dry deposition flux of total PCBs varied between 3.48 and 6.79 μg m −2 per day and averaged ≈ 4.73 μg m −2 per day. This was up to three orders of magnitude higher than the fluxes measured at the Great Lake and remote areas and close to those measured at urban areas by previous studies. The particle-bound PCB homologue composition collected by the dry deposition plate varied between 0.76 μg g −1 (di-CBs) and 11.5 μg g −1 (hexa-CBs). This profile of PCB homologues is similar to the pattern of Aroclor 1260 which is dominant in hexa-CBs and hepta-CBs. Because of their higher vapor pressure, in general, the less-chlorinated PCB homologues have a greater PCB mass fraction in the gas phase. The mean dry deposition velocities of PCB homologues ranged between 0.09 and 0.58 cm s −1. In general, the more highly chlorinated PCB homologues have a higher dry deposition velocity. Particle size distributions ( dC d(log D p ) vs. D p) of total PCBs were found to be bimodal. The highest peak was localized in the particle size range between 5.6 and 10.0 μm and the second peak was localized in the particle size range between 0.31 and 0.52 μm. The particle MMD 0 of total PCBs was 1.68 μm and more than 85% of the PCB mass was found in the particles smaller than 10 μm. By using the particle size distribution data, the dry deposition model used in this study can provide a good prediction for the dry deposition flux of total particle mass, total PCBs and PCB homologues. For both total particle mass and total PCBs, more than 87.5% of the dry deposition flux is contributed by particles of size > 10 μm. This is because particles larger than 10 μm have a higher dry deposition velocity (> 2.60 cm s −1) and, therefore, control the majority of the dry deposition flux.
AbstractList Dry deposition and air sampling were undertaken simultaneously in the ambient air of an urban site by using several dry deposition plates, two MOUDIs (micro-orifice uniform deposited impactors), one NRI (Noll rotary impactor) and several PS-1 (General Metal Work, PS-1) samplers from January to May 1994 in Tainan City, Taiwan. The PCB (polychlorinated biphenyl) congeners were analyzed primarily by using a gas chromatograph with a super(63)Ni electron capture detector (ECD). The measured dry deposition flux of total PCBs varied between 3.48 and 6.79 mu g m super(-2) per day and averaged approximately 4.73 mu g m super(-2) per day. This was up to three orders of magnitude higher than the fluxes measured at the Great Lake and remote areas and close to those measured at urban areas by previous studies. The particle-bound PCB homologue composition collected by the dry deposition plate varied between 0.76 mu g g super(-1) (di-CBs) and 11.5 mu g g super(-1) (hexa-CBs). This profile of PCB homologues is similar to the pattern of Aroclor 1260 which is dominant in hexa-CBs and hepta-CBs. Meanwhile, the dry deposition model used in this study can provide a good prediction for the dry deposition flux of total particle mass, total PCBs and PCB homologues.
Dry deposition and air sampling were undertaken simultaneously in the ambient air of an urban site by using several dry deposition plates, two MOUDIs (micro-orifice uniform deposited impactors), one NRI (Noll rotary impactor) and several PS-1 (General Metal Work, PS-1) samplers from January to May 1994 in Tainan City, Taiwan. The dry deposition plate, which had a smooth surface, was always pointed into the wind. The PCB (polychlorinated biphenyl) congeners were analyzed primarily by using a gas chromatograph with a super(63)Ni electron capture detector (ECD). The measured dry deposition flux of total PCBs varied between 3.48 and 6.79 mu g m super(-2) per day and averaged approximately 4.73 mu g m super(-2) per day. The particle-bound PCB homologue composition collected by the dry deposition plate varied between 0.76 mu g g super(-1) (di-CBs) and 11.5 mu g g super(-1) (hexa-CBs). This profile of PCB homologues is similar to the pattern of Aroclor 1260 which is dominant in hexa-CBs and hepta-CBs. Because of their higher vapor pressure, in general, the less-chlorinated PCB homologues have a greater PCB mass fraction in the gas phase. The mean dry deposition velocities of PCB homologues ranged between 0.09 and 0.58 cm s super(-1). In general, the more highly chlorinated PCB homologues have a higher dry deposition velocity. Particle size distributions (dC/d(log D sub(p)) vs. D sub(p)) of total PCBs were found to be bimodal. By using the particle size distribution data, the dry deposition model used in this study can provide a good prediction for the dry deposition flux of total particle mass, total PCBs and PCB homologues.
Dry deposition and air sampling were undertaken simultaneously in the ambient air of an urban site by using several dry deposition plates, two MOUDIs (micro-orifice uniform deposited impactors), one NRI (Noll rotary impactor) and several PS-1 (General Metal Work, PS-1) samplers from January to May 1994 in Tainan City, Taiwan. The dry deposition plate, which had a smooth surface, was always pointed into the wind. The PCB (polychlorinated biphenyl) congeners were analyzed primarily by using a gas chromatograph with a 63Ni electron capture detector (ECD). The measured dry deposition flux of total PCBs varied between 3.48 and 6.79 μg m −2 per day and averaged ≈ 4.73 μg m −2 per day. This was up to three orders of magnitude higher than the fluxes measured at the Great Lake and remote areas and close to those measured at urban areas by previous studies. The particle-bound PCB homologue composition collected by the dry deposition plate varied between 0.76 μg g −1 (di-CBs) and 11.5 μg g −1 (hexa-CBs). This profile of PCB homologues is similar to the pattern of Aroclor 1260 which is dominant in hexa-CBs and hepta-CBs. Because of their higher vapor pressure, in general, the less-chlorinated PCB homologues have a greater PCB mass fraction in the gas phase. The mean dry deposition velocities of PCB homologues ranged between 0.09 and 0.58 cm s −1. In general, the more highly chlorinated PCB homologues have a higher dry deposition velocity. Particle size distributions ( dC d(log D p ) vs. D p) of total PCBs were found to be bimodal. The highest peak was localized in the particle size range between 5.6 and 10.0 μm and the second peak was localized in the particle size range between 0.31 and 0.52 μm. The particle MMD 0 of total PCBs was 1.68 μm and more than 85% of the PCB mass was found in the particles smaller than 10 μm. By using the particle size distribution data, the dry deposition model used in this study can provide a good prediction for the dry deposition flux of total particle mass, total PCBs and PCB homologues. For both total particle mass and total PCBs, more than 87.5% of the dry deposition flux is contributed by particles of size > 10 μm. This is because particles larger than 10 μm have a higher dry deposition velocity (> 2.60 cm s −1) and, therefore, control the majority of the dry deposition flux.
Author Chao, How-Ran
Fan, Yi-Chin
Lee, Wen-Jhy
Su, Chun-Ching
Fang, Guor-Cheng
Sheu, Hwey-Lin
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  fullname: Fang, Guor-Cheng
  organization: Department of Industrial Safety and Hygiene, Hungkuang Institute of Medical and Nursing Technology, Taichung 43309, Taiwan
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Issue 1
Keywords Urban
Particle size distribution
Ambient air
Dry deposition
Modeling
Polychlorinated biphenyl
Suspended particle
Atmospheric fallout
Chlorocarbon
Check
Air pollution
Urban area
Polychlorobiphenyl
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Snippet Dry deposition and air sampling were undertaken simultaneously in the ambient air of an urban site by using several dry deposition plates, two MOUDIs...
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SubjectTerms Ambient air
Applied sciences
Atmospheric pollution
Chlorination
Dry deposition
Exact sciences and technology
Gas chromatography
Mathematical models
Modeling
Particle size distribution
Pollutants physicochemistry study: properties, effects, reactions, transport and distribution
Pollution
Polychlorinated biphenyl
Q1
Rural areas
Urban
Velocity
Title Monitoring and modeling of PCB dry deposition in urban area
URI https://dx.doi.org/10.1016/0304-3894(95)00159-X
https://www.proquest.com/docview/14421149
https://www.proquest.com/docview/15747153
https://www.proquest.com/docview/15757291
Volume 49
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