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 in | Journal of hazardous materials Vol. 49; no. 1; pp. 57 - 88 |
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Main Authors | , , , , , |
Format | Journal Article |
Language | English |
Published |
Amsterdam
Elsevier B.V
1996
Elsevier |
Subjects | |
Online Access | Get full text |
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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. |
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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 |
Author_xml | – sequence: 1 givenname: Wen-Jhy surname: Lee fullname: Lee, Wen-Jhy organization: Department of Environmental Engineering, National Cheng Kung University, Tainan 70101, Taiwan – sequence: 2 givenname: Chun-Ching surname: Su fullname: Su, Chun-Ching organization: Department of Environmental Engineering, National Cheng Kung University, Tainan 70101, Taiwan – sequence: 3 givenname: Hwey-Lin surname: Sheu fullname: Sheu, Hwey-Lin organization: Department of Environmental Engineering, National Cheng Kung University, Tainan 70101, Taiwan – sequence: 4 givenname: Yi-Chin surname: Fan fullname: Fan, Yi-Chin organization: Department of Environmental Engineering, National Cheng Kung University, Tainan 70101, Taiwan – sequence: 5 givenname: How-Ran surname: Chao fullname: Chao, How-Ran organization: Department of Environmental Engineering, National Cheng Kung University, Tainan 70101, Taiwan – sequence: 6 givenname: Guor-Cheng surname: Fang 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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Cites_doi | 10.1021/es00140a009 10.1021/es00088a011 10.1016/0004-6981(89)90007-3 10.1016/S0380-1330(81)72018-5 10.1021/es60123a007 10.1021/es00083a002 10.1021/es00171a008 10.1021/es00099a010 10.1021/es00073a009 10.1021/es00018a009 10.1016/1352-2310(94)90210-0 10.1021/es00031a015 10.1021/es00151a005 10.1021/es00067a012 10.1029/JC084iC12p07857 10.1080/02786828608959095 10.1016/0004-6981(79)90186-0 10.1016/0004-6981(85)90019-8 10.1021/es00124a014 10.1016/0004-6981(80)90031-1 10.1029/JD090iD01p02123 10.1016/0004-6981(88)90196-5 |
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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 |
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