Abstract

Following the accident at the Chernobyl nuclear power plant in 1986, radioactive materials including Cs-137 were distributed over large parts of the former Soviet Union and Europe. Due to the relatively long physical half-life of Cs-137 (30.1 y) measurable activity concentrations can still be observed in the natural environment. We have determined the depth distribution of Cs-137 from the testing of nuclear weapons in the atmosphere and Chernobyl, in eight highly-organic soils along an approximately east to west transect across the Central Highlands of Scotland. The Cs-137 activity concentrations in the soil profiles, corrected for radioactive decay to May 1986, were between 2.8 and 14.4 kBq m(-2). There were differences in the pattern of distribution of Cs-137 in the soil profiles. The mean migration depth of Cs-137 in the soil profiles was 12.2 cm with a range between 8.2 and 17.4 cm. Quantitative mineralogical analysis of the ash obtained after heating the soil to 400 degrees C indicated that clay minerals alone did not have a prime role in controlling the migration of Cs-137 down the profile. (C) 2012 Elsevier Ltd. All rights reserved.

Keywords

Chernobyl; Clay minerals; Pollution; Radioactivity; X-ray diffraction; Cs-137

Published in

Journal of Environmental Radioactivity
2013, Volume: 115, pages: 124-133
Publisher: ELSEVIER SCI LTD

SLU Authors

• Rosén, Klas

  • Department of Soil and Environment, Swedish University of Agricultural Sciences
    

• Thored, Kristin

  • Department of Crop Production Ecology, Swedish University of Agricultural Sciences
    

• Hillier, Stephen

  • Department of Soil and Environment, Swedish University of Agricultural Sciences
    

UKÄ Subject classification

Soil Science
Environmental Sciences related to Agriculture and Land-use
Environmental Sciences


Publication identifier

DOI: https://doi.org/10.1016/j.jenvrad.2012.08.003

Permanent link to this page (URI)

https://res.slu.se/id/publ/53445