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The Importance of Long and Short-Term Air-Soil Exchanges of Organic Contaminants.

Research output: Contribution to Journal/MagazineJournal article

Published

Standard

The Importance of Long and Short-Term Air-Soil Exchanges of Organic Contaminants. / Jones, K. C.; Johnston, A. E.; McGrath, S. P.
In: International Journal of Analytical Chemistry, Vol. 59, No. 2-4, 04.1995, p. 167-178.

Research output: Contribution to Journal/MagazineJournal article

Harvard

Jones, KC, Johnston, AE & McGrath, SP 1995, 'The Importance of Long and Short-Term Air-Soil Exchanges of Organic Contaminants.', International Journal of Analytical Chemistry, vol. 59, no. 2-4, pp. 167-178. https://doi.org/10.1080/03067319508041325

APA

Jones, K. C., Johnston, A. E., & McGrath, S. P. (1995). The Importance of Long and Short-Term Air-Soil Exchanges of Organic Contaminants. International Journal of Analytical Chemistry, 59(2-4), 167-178. https://doi.org/10.1080/03067319508041325

Vancouver

Jones KC, Johnston AE, McGrath SP. The Importance of Long and Short-Term Air-Soil Exchanges of Organic Contaminants. International Journal of Analytical Chemistry. 1995 Apr;59(2-4):167-178. doi: 10.1080/03067319508041325

Author

Jones, K. C. ; Johnston, A. E. ; McGrath, S. P. / The Importance of Long and Short-Term Air-Soil Exchanges of Organic Contaminants. In: International Journal of Analytical Chemistry. 1995 ; Vol. 59, No. 2-4. pp. 167-178.

Bibtex

@article{35c0f3fa32734585b3b81d455e27eed4,
title = "The Importance of Long and Short-Term Air-Soil Exchanges of Organic Contaminants.",
abstract = "Retrospective analysis of archived soil samples collected and stored from long-term agricultural experiments in the UK has shown how soil organic chemical composition has changed over time. High molecular weight polycyclic aromatic hydrocarbons (e.g. benzo[a]pyrene) and polychlorinated dibenzo-p-dioxins and -furans have increased in concentration through this century as a result of cumulative atmospheric depositional inputs. Concentrations of polychlorinated biphenyls and low molecular weight hydrocarbons (e.g. phenanthrene) peaked in the late 1960s/early 1970s, but have declined subsequently. This reflects declining atmospheric inputs of these compounds and losses from surface soils by volatilisation back to the atmosphere and biodegradation. PCBs and low molecular weight PAHs exist predominantly in the vapour phase in air, whilst heavy PAHs and PCDD/Fs are predominantly particulate-bound. Outgassing from soils is probably the most important contemporary source of PCBs to the atmosphere in the UK. Future UK PCB air concentrations will presumably therefore be influenced (controlled) by the rate of desorption and outgassing, as soil and air concentrations move towards a condition of equilibrium partitioning. Archived soils collected and stored before the commercial manufacture of PCBs contain no PCBs indicating that there is no 'natural production' of these compounds. However, within a few hours of exposure to contemporary air these samples contain detectable quantities of PCBs. Short-term air-soil exchange, such as during soil drying in the laboratory, can lead to contamination of samples which contain low concentrations of PCBs and loss from samples which contain high concentrations.",
keywords = "PAHs, PCBs, PCDDs, soil samples, atmospheric deposition",
author = "Jones, {K. C.} and Johnston, {A. E.} and McGrath, {S. P.}",
year = "1995",
month = apr,
doi = "10.1080/03067319508041325",
language = "English",
volume = "59",
pages = "167--178",
journal = "International Journal of Analytical Chemistry",
issn = "1687-8779",
publisher = "Hindawi Publishing Corporation",
number = "2-4",

}

RIS

TY - JOUR

T1 - The Importance of Long and Short-Term Air-Soil Exchanges of Organic Contaminants.

AU - Jones, K. C.

AU - Johnston, A. E.

AU - McGrath, S. P.

PY - 1995/4

Y1 - 1995/4

N2 - Retrospective analysis of archived soil samples collected and stored from long-term agricultural experiments in the UK has shown how soil organic chemical composition has changed over time. High molecular weight polycyclic aromatic hydrocarbons (e.g. benzo[a]pyrene) and polychlorinated dibenzo-p-dioxins and -furans have increased in concentration through this century as a result of cumulative atmospheric depositional inputs. Concentrations of polychlorinated biphenyls and low molecular weight hydrocarbons (e.g. phenanthrene) peaked in the late 1960s/early 1970s, but have declined subsequently. This reflects declining atmospheric inputs of these compounds and losses from surface soils by volatilisation back to the atmosphere and biodegradation. PCBs and low molecular weight PAHs exist predominantly in the vapour phase in air, whilst heavy PAHs and PCDD/Fs are predominantly particulate-bound. Outgassing from soils is probably the most important contemporary source of PCBs to the atmosphere in the UK. Future UK PCB air concentrations will presumably therefore be influenced (controlled) by the rate of desorption and outgassing, as soil and air concentrations move towards a condition of equilibrium partitioning. Archived soils collected and stored before the commercial manufacture of PCBs contain no PCBs indicating that there is no 'natural production' of these compounds. However, within a few hours of exposure to contemporary air these samples contain detectable quantities of PCBs. Short-term air-soil exchange, such as during soil drying in the laboratory, can lead to contamination of samples which contain low concentrations of PCBs and loss from samples which contain high concentrations.

AB - Retrospective analysis of archived soil samples collected and stored from long-term agricultural experiments in the UK has shown how soil organic chemical composition has changed over time. High molecular weight polycyclic aromatic hydrocarbons (e.g. benzo[a]pyrene) and polychlorinated dibenzo-p-dioxins and -furans have increased in concentration through this century as a result of cumulative atmospheric depositional inputs. Concentrations of polychlorinated biphenyls and low molecular weight hydrocarbons (e.g. phenanthrene) peaked in the late 1960s/early 1970s, but have declined subsequently. This reflects declining atmospheric inputs of these compounds and losses from surface soils by volatilisation back to the atmosphere and biodegradation. PCBs and low molecular weight PAHs exist predominantly in the vapour phase in air, whilst heavy PAHs and PCDD/Fs are predominantly particulate-bound. Outgassing from soils is probably the most important contemporary source of PCBs to the atmosphere in the UK. Future UK PCB air concentrations will presumably therefore be influenced (controlled) by the rate of desorption and outgassing, as soil and air concentrations move towards a condition of equilibrium partitioning. Archived soils collected and stored before the commercial manufacture of PCBs contain no PCBs indicating that there is no 'natural production' of these compounds. However, within a few hours of exposure to contemporary air these samples contain detectable quantities of PCBs. Short-term air-soil exchange, such as during soil drying in the laboratory, can lead to contamination of samples which contain low concentrations of PCBs and loss from samples which contain high concentrations.

KW - PAHs

KW - PCBs

KW - PCDDs

KW - soil samples

KW - atmospheric deposition

U2 - 10.1080/03067319508041325

DO - 10.1080/03067319508041325

M3 - Journal article

VL - 59

SP - 167

EP - 178

JO - International Journal of Analytical Chemistry

JF - International Journal of Analytical Chemistry

SN - 1687-8779

IS - 2-4

ER -