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Transfers of airborne PCDD/Fs to bulk deposition collectors and herbage.

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Transfers of airborne PCDD/Fs to bulk deposition collectors and herbage. / Jones, Kevin C.; Duarte-Davidson, Raquel.
In: Environmental Science and Technology, Vol. 31, No. 10, 10.1997, p. 2937-2943.

Research output: Contribution to Journal/MagazineJournal articlepeer-review

Harvard

Jones, KC & Duarte-Davidson, R 1997, 'Transfers of airborne PCDD/Fs to bulk deposition collectors and herbage.', Environmental Science and Technology, vol. 31, no. 10, pp. 2937-2943. https://doi.org/10.1021/es970133t

APA

Jones, K. C., & Duarte-Davidson, R. (1997). Transfers of airborne PCDD/Fs to bulk deposition collectors and herbage. Environmental Science and Technology, 31(10), 2937-2943. https://doi.org/10.1021/es970133t

Vancouver

Jones KC, Duarte-Davidson R. Transfers of airborne PCDD/Fs to bulk deposition collectors and herbage. Environmental Science and Technology. 1997 Oct;31(10):2937-2943. doi: 10.1021/es970133t

Author

Jones, Kevin C. ; Duarte-Davidson, Raquel. / Transfers of airborne PCDD/Fs to bulk deposition collectors and herbage. In: Environmental Science and Technology. 1997 ; Vol. 31, No. 10. pp. 2937-2943.

Bibtex

@article{3d005fe5cf5749389ccdb712b02f55eb,
title = "Transfers of airborne PCDD/Fs to bulk deposition collectors and herbage.",
abstract = "PCDD/F air concentrations, deposition fluxes, and grass concentrations/offtakes (pg m-2 day-1) were measured concurrently in Bolsover, Derbyshire, England over 1 year during 1992−1993. The data are used here to discuss spatial and temporal differences in atmospheric PCDD/F concentrations and how the airborne PCDD/Fs transferred to the bulk deposition collectors and grass. Three sample sites are discussed, namely, a regional background site (RBS), an urban site (US), and a site close to an industrial complex (IS) that has been a suspected source of selected PCDD/F homologs. Generally, the mixture of PCDD/F 2,3,7,8-substituted congeners and homologs was the same in the air, in the bulk deposition, and in the grass over a given sampling period and site. This suggests that PCDD/Fs of different levels of chlorination were transferring with similar efficiencies from the air to the collectors and grass, despite different gas−particle partitioning in the air. Deposition or transfer velocities for individual congeners/homologs to the bulk collectors throughout the whole study ranged between 0.034 and 0.82 cm s-1 at the sites, averaging 0.27 cm s-1 for PCDD/Fs at the RBS. An experiment conducted to assess potential volatilization of soil-borne PCDD/Fs from contaminated areas near the IS showed that all the compounds had a strong affinity for the soil and that volatilization is not likely to significantly contaminate herbage growing in the contaminated soil or the overlying atmosphere near this site. Herbage PCDD/Fs were therefore derived almost exclusively from the atmosphere in this study. The similarities in the PCDD/F mixture in air and grass suggest that the different PCDD/Fs are scavenged by the grass sward from the atmosphere with similar efficiencies; the implications of this are discussed.",
author = "Jones, {Kevin C.} and Raquel Duarte-Davidson",
year = "1997",
month = oct,
doi = "10.1021/es970133t",
language = "English",
volume = "31",
pages = "2937--2943",
journal = "Environmental Science and Technology",
issn = "0013-936X",
publisher = "American Chemical Society",
number = "10",

}

RIS

TY - JOUR

T1 - Transfers of airborne PCDD/Fs to bulk deposition collectors and herbage.

AU - Jones, Kevin C.

AU - Duarte-Davidson, Raquel

PY - 1997/10

Y1 - 1997/10

N2 - PCDD/F air concentrations, deposition fluxes, and grass concentrations/offtakes (pg m-2 day-1) were measured concurrently in Bolsover, Derbyshire, England over 1 year during 1992−1993. The data are used here to discuss spatial and temporal differences in atmospheric PCDD/F concentrations and how the airborne PCDD/Fs transferred to the bulk deposition collectors and grass. Three sample sites are discussed, namely, a regional background site (RBS), an urban site (US), and a site close to an industrial complex (IS) that has been a suspected source of selected PCDD/F homologs. Generally, the mixture of PCDD/F 2,3,7,8-substituted congeners and homologs was the same in the air, in the bulk deposition, and in the grass over a given sampling period and site. This suggests that PCDD/Fs of different levels of chlorination were transferring with similar efficiencies from the air to the collectors and grass, despite different gas−particle partitioning in the air. Deposition or transfer velocities for individual congeners/homologs to the bulk collectors throughout the whole study ranged between 0.034 and 0.82 cm s-1 at the sites, averaging 0.27 cm s-1 for PCDD/Fs at the RBS. An experiment conducted to assess potential volatilization of soil-borne PCDD/Fs from contaminated areas near the IS showed that all the compounds had a strong affinity for the soil and that volatilization is not likely to significantly contaminate herbage growing in the contaminated soil or the overlying atmosphere near this site. Herbage PCDD/Fs were therefore derived almost exclusively from the atmosphere in this study. The similarities in the PCDD/F mixture in air and grass suggest that the different PCDD/Fs are scavenged by the grass sward from the atmosphere with similar efficiencies; the implications of this are discussed.

AB - PCDD/F air concentrations, deposition fluxes, and grass concentrations/offtakes (pg m-2 day-1) were measured concurrently in Bolsover, Derbyshire, England over 1 year during 1992−1993. The data are used here to discuss spatial and temporal differences in atmospheric PCDD/F concentrations and how the airborne PCDD/Fs transferred to the bulk deposition collectors and grass. Three sample sites are discussed, namely, a regional background site (RBS), an urban site (US), and a site close to an industrial complex (IS) that has been a suspected source of selected PCDD/F homologs. Generally, the mixture of PCDD/F 2,3,7,8-substituted congeners and homologs was the same in the air, in the bulk deposition, and in the grass over a given sampling period and site. This suggests that PCDD/Fs of different levels of chlorination were transferring with similar efficiencies from the air to the collectors and grass, despite different gas−particle partitioning in the air. Deposition or transfer velocities for individual congeners/homologs to the bulk collectors throughout the whole study ranged between 0.034 and 0.82 cm s-1 at the sites, averaging 0.27 cm s-1 for PCDD/Fs at the RBS. An experiment conducted to assess potential volatilization of soil-borne PCDD/Fs from contaminated areas near the IS showed that all the compounds had a strong affinity for the soil and that volatilization is not likely to significantly contaminate herbage growing in the contaminated soil or the overlying atmosphere near this site. Herbage PCDD/Fs were therefore derived almost exclusively from the atmosphere in this study. The similarities in the PCDD/F mixture in air and grass suggest that the different PCDD/Fs are scavenged by the grass sward from the atmosphere with similar efficiencies; the implications of this are discussed.

U2 - 10.1021/es970133t

DO - 10.1021/es970133t

M3 - Journal article

VL - 31

SP - 2937

EP - 2943

JO - Environmental Science and Technology

JF - Environmental Science and Technology

SN - 0013-936X

IS - 10

ER -