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Radiocaesium partitioning in Japanese cedar forests following the “early” phase of Fukushima fallout redistribution
Our study focused on radiocaesium ((137)Cs) partitioning in forests, three vegetation periods after the Fukushima Daiichi nuclear power plant accident. (137)Cs distribution in forest components (organic and mineral soil layers as well as tree compartments: stem, bark, needles, branches and roots) wa...
Autores principales: | , , , , , , , , |
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Formato: | Online Artículo Texto |
Lenguaje: | English |
Publicado: |
Nature Publishing Group
2016
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Materias: | |
Acceso en línea: | https://www.ncbi.nlm.nih.gov/pmc/articles/PMC5120304/ https://www.ncbi.nlm.nih.gov/pubmed/27876870 http://dx.doi.org/10.1038/srep37618 |
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author | Coppin, Frederic Hurtevent, Pierre Loffredo, Nicolas Simonucci, Caroline Julien, Anthony Gonze, Marc-Andre Nanba, Kenji Onda, Yuichi Thiry, Yves |
author_facet | Coppin, Frederic Hurtevent, Pierre Loffredo, Nicolas Simonucci, Caroline Julien, Anthony Gonze, Marc-Andre Nanba, Kenji Onda, Yuichi Thiry, Yves |
author_sort | Coppin, Frederic |
collection | PubMed |
description | Our study focused on radiocaesium ((137)Cs) partitioning in forests, three vegetation periods after the Fukushima Daiichi nuclear power plant accident. (137)Cs distribution in forest components (organic and mineral soil layers as well as tree compartments: stem, bark, needles, branches and roots) was measured for two Japanese cedar stand ages (17 and 33 years old). The results showed that around 85% of the initial deposit was found in the forest floor and topsoil. For the youngest stand almost 70% of the deposit is present in the forest floor, whereas for the oldest stand 50% is present in the 0–3 cm mineral soil layer. For trees, old and perennial organs (including dead and living needles and branches, litter fall and outer bark) directly exposed to the fallout remained the most contaminated. The crown concentrated 61–69% of the total tree contamination. Surprisingly the dead organs concentrated 25 ± 9% (young cedars) to 36 ± 20% (mature cedar) of the trees’ residual activity, highlighting the importance of that specific compartment in the early post-accident phase for Japanese cedar forests. Although the stem (including bark) represents the highest biomass pool, it only concentrates 3.3% and 4.6% of the initial (137)Cs deposit for mature and young cedars, respectively. |
format | Online Article Text |
id | pubmed-5120304 |
institution | National Center for Biotechnology Information |
language | English |
publishDate | 2016 |
publisher | Nature Publishing Group |
record_format | MEDLINE/PubMed |
spelling | pubmed-51203042016-11-28 Radiocaesium partitioning in Japanese cedar forests following the “early” phase of Fukushima fallout redistribution Coppin, Frederic Hurtevent, Pierre Loffredo, Nicolas Simonucci, Caroline Julien, Anthony Gonze, Marc-Andre Nanba, Kenji Onda, Yuichi Thiry, Yves Sci Rep Article Our study focused on radiocaesium ((137)Cs) partitioning in forests, three vegetation periods after the Fukushima Daiichi nuclear power plant accident. (137)Cs distribution in forest components (organic and mineral soil layers as well as tree compartments: stem, bark, needles, branches and roots) was measured for two Japanese cedar stand ages (17 and 33 years old). The results showed that around 85% of the initial deposit was found in the forest floor and topsoil. For the youngest stand almost 70% of the deposit is present in the forest floor, whereas for the oldest stand 50% is present in the 0–3 cm mineral soil layer. For trees, old and perennial organs (including dead and living needles and branches, litter fall and outer bark) directly exposed to the fallout remained the most contaminated. The crown concentrated 61–69% of the total tree contamination. Surprisingly the dead organs concentrated 25 ± 9% (young cedars) to 36 ± 20% (mature cedar) of the trees’ residual activity, highlighting the importance of that specific compartment in the early post-accident phase for Japanese cedar forests. Although the stem (including bark) represents the highest biomass pool, it only concentrates 3.3% and 4.6% of the initial (137)Cs deposit for mature and young cedars, respectively. Nature Publishing Group 2016-11-23 /pmc/articles/PMC5120304/ /pubmed/27876870 http://dx.doi.org/10.1038/srep37618 Text en Copyright © 2016, The Author(s) http://creativecommons.org/licenses/by/4.0/ This work is licensed under a Creative Commons Attribution 4.0 International License. The images or other third party material in this article are included in the article’s Creative Commons license, unless indicated otherwise in the credit line; if the material is not included under the Creative Commons license, users will need to obtain permission from the license holder to reproduce the material. To view a copy of this license, visit http://creativecommons.org/licenses/by/4.0/ |
spellingShingle | Article Coppin, Frederic Hurtevent, Pierre Loffredo, Nicolas Simonucci, Caroline Julien, Anthony Gonze, Marc-Andre Nanba, Kenji Onda, Yuichi Thiry, Yves Radiocaesium partitioning in Japanese cedar forests following the “early” phase of Fukushima fallout redistribution |
title | Radiocaesium partitioning in Japanese cedar forests following the “early” phase of Fukushima fallout redistribution |
title_full | Radiocaesium partitioning in Japanese cedar forests following the “early” phase of Fukushima fallout redistribution |
title_fullStr | Radiocaesium partitioning in Japanese cedar forests following the “early” phase of Fukushima fallout redistribution |
title_full_unstemmed | Radiocaesium partitioning in Japanese cedar forests following the “early” phase of Fukushima fallout redistribution |
title_short | Radiocaesium partitioning in Japanese cedar forests following the “early” phase of Fukushima fallout redistribution |
title_sort | radiocaesium partitioning in japanese cedar forests following the “early” phase of fukushima fallout redistribution |
topic | Article |
url | https://www.ncbi.nlm.nih.gov/pmc/articles/PMC5120304/ https://www.ncbi.nlm.nih.gov/pubmed/27876870 http://dx.doi.org/10.1038/srep37618 |
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