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Air-pasture transfer of PCBs.

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Air-pasture transfer of PCBs. / Thomas, Gareth O.; Sweetman, Andrew J.; Ockenden, Wendy A. et al.
In: Environmental Science and Technology, Vol. 32, No. 7, 01.04.1998, p. 936-942.

Research output: Contribution to Journal/MagazineJournal articlepeer-review

Harvard

Thomas, GO, Sweetman, AJ, Ockenden, WA, Mackay, D & Jones, KC 1998, 'Air-pasture transfer of PCBs.', Environmental Science and Technology, vol. 32, no. 7, pp. 936-942. https://doi.org/10.1021/es970761a

APA

Thomas, G. O., Sweetman, A. J., Ockenden, W. A., Mackay, D., & Jones, K. C. (1998). Air-pasture transfer of PCBs. Environmental Science and Technology, 32(7), 936-942. https://doi.org/10.1021/es970761a

Vancouver

Thomas GO, Sweetman AJ, Ockenden WA, Mackay D, Jones KC. Air-pasture transfer of PCBs. Environmental Science and Technology. 1998 Apr 1;32(7):936-942. doi: 10.1021/es970761a

Author

Thomas, Gareth O. ; Sweetman, Andrew J. ; Ockenden, Wendy A. et al. / Air-pasture transfer of PCBs. In: Environmental Science and Technology. 1998 ; Vol. 32, No. 7. pp. 936-942.

Bibtex

@article{bac441cc9cf3487ab37ec4a6e97cf504,
title = "Air-pasture transfer of PCBs.",
abstract = "A field experiment was conducted to study the air to pasture transfer of PCBs at a rural site in northwest England. Strong positive linear correlations were obtained between the log plant−air partition coefficients (m3 of air g-1 of plant dry weightdefined here as the scavenging coefficient) and log octanol−air (Koa) partition coefficients. Pasture typically retained amounts of PCB per g dry weight equivalent to that in 7 m3 of air for congener 18 and ranging up to 64 m3 for congener 170, regardless of whether the pasture growth (exposure) time had been 2, 6, or 12 weeks. This indicates that airborne PCBs partition onto freshly grown pasture and approach plant surface−air gas-phase equilibrium rather rapidly at this site, i.e., within 2 weeks of exposure. In late April−June, when grassland production is at a maximum, sequestering rates could approach 1.2 ng of PCB-18, 0.17 ng of PCB-170, and 12 ng of ∑PCB m-2 day-1. With 7 million ha of managed and rough grassland in the U.K., fresh pasture production in the spring and summer is estimated to remove an average of 0.8 kg of ∑PCB day-1 from the air during these times (80 kg of ∑PCB per growing season). Some buffering influence may be exerted on surface air concentrations during the most active periods of plant biomass production, while the incorporation of PCBs into pasture following air−pasture transfer processes controls the supply of PCBs to grazing animals and the human food chain.",
author = "Thomas, {Gareth O.} and Sweetman, {Andrew J.} and Ockenden, {Wendy A.} and Donald Mackay and Jones, {Kevin C.}",
year = "1998",
month = apr,
day = "1",
doi = "10.1021/es970761a",
language = "English",
volume = "32",
pages = "936--942",
journal = "Environmental Science and Technology",
issn = "0013-936X",
publisher = "American Chemical Society",
number = "7",

}

RIS

TY - JOUR

T1 - Air-pasture transfer of PCBs.

AU - Thomas, Gareth O.

AU - Sweetman, Andrew J.

AU - Ockenden, Wendy A.

AU - Mackay, Donald

AU - Jones, Kevin C.

PY - 1998/4/1

Y1 - 1998/4/1

N2 - A field experiment was conducted to study the air to pasture transfer of PCBs at a rural site in northwest England. Strong positive linear correlations were obtained between the log plant−air partition coefficients (m3 of air g-1 of plant dry weightdefined here as the scavenging coefficient) and log octanol−air (Koa) partition coefficients. Pasture typically retained amounts of PCB per g dry weight equivalent to that in 7 m3 of air for congener 18 and ranging up to 64 m3 for congener 170, regardless of whether the pasture growth (exposure) time had been 2, 6, or 12 weeks. This indicates that airborne PCBs partition onto freshly grown pasture and approach plant surface−air gas-phase equilibrium rather rapidly at this site, i.e., within 2 weeks of exposure. In late April−June, when grassland production is at a maximum, sequestering rates could approach 1.2 ng of PCB-18, 0.17 ng of PCB-170, and 12 ng of ∑PCB m-2 day-1. With 7 million ha of managed and rough grassland in the U.K., fresh pasture production in the spring and summer is estimated to remove an average of 0.8 kg of ∑PCB day-1 from the air during these times (80 kg of ∑PCB per growing season). Some buffering influence may be exerted on surface air concentrations during the most active periods of plant biomass production, while the incorporation of PCBs into pasture following air−pasture transfer processes controls the supply of PCBs to grazing animals and the human food chain.

AB - A field experiment was conducted to study the air to pasture transfer of PCBs at a rural site in northwest England. Strong positive linear correlations were obtained between the log plant−air partition coefficients (m3 of air g-1 of plant dry weightdefined here as the scavenging coefficient) and log octanol−air (Koa) partition coefficients. Pasture typically retained amounts of PCB per g dry weight equivalent to that in 7 m3 of air for congener 18 and ranging up to 64 m3 for congener 170, regardless of whether the pasture growth (exposure) time had been 2, 6, or 12 weeks. This indicates that airborne PCBs partition onto freshly grown pasture and approach plant surface−air gas-phase equilibrium rather rapidly at this site, i.e., within 2 weeks of exposure. In late April−June, when grassland production is at a maximum, sequestering rates could approach 1.2 ng of PCB-18, 0.17 ng of PCB-170, and 12 ng of ∑PCB m-2 day-1. With 7 million ha of managed and rough grassland in the U.K., fresh pasture production in the spring and summer is estimated to remove an average of 0.8 kg of ∑PCB day-1 from the air during these times (80 kg of ∑PCB per growing season). Some buffering influence may be exerted on surface air concentrations during the most active periods of plant biomass production, while the incorporation of PCBs into pasture following air−pasture transfer processes controls the supply of PCBs to grazing animals and the human food chain.

U2 - 10.1021/es970761a

DO - 10.1021/es970761a

M3 - Journal article

VL - 32

SP - 936

EP - 942

JO - Environmental Science and Technology

JF - Environmental Science and Technology

SN - 0013-936X

IS - 7

ER -