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Relevance and use of the $^{110m}$: $^{137}$Cs activity ratio for tracking the dispersion of radioactive sediment within Fukushima coastal catchments

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HAL Id: cea-02641020

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Submitted on 28 May 2020

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Relevance and use of the

110m

:

137

Cs activity ratio for

tracking the dispersion of radioactive sediment within

Fukushima coastal catchments

Hugo Lepage, Olivier Evrard, Yuichi Onda, Caroline Chartin, Irène Lefèvre,

Philippe Bonté, Sophie Ayrault

To cite this version:

Hugo Lepage, Olivier Evrard, Yuichi Onda, Caroline Chartin, Irène Lefèvre, et al.. Relevance and use

of the

110m

:

137

Cs activity ratio for tracking the dispersion of radioactive sediment within Fukushima

coastal catchments. EGU General Assembly 2014, Apr 2014, Vienne, Austria. pp.EGU2014-2050.

�cea-02641020�

(2)

Geophysical Research Abstracts Vol. 16, EGU2014-2050, 2014 EGU General Assembly 2014

© Author(s) 2014. CC Attribution 3.0 License.

Relevance and use of the Ag-110m: Cs-137 activity ratio for tracking the

dispersion of radioactive sediment within Fukushima coastal catchments

Hugo Lepage (1), Olivier Evrard (1), Yuichi Onda (2), Caroline Chartin (1), Irène Lefèvre (1), Philippe Bonté (1), and Sophie Ayrault (1)

(1) Laboratoire des Sciences du Climat et de l’Environnement (LSCE/IPSL), Unité Mixte de Recherche 8212 (CEA, CNRS, UVSQ), 91198 Gif-sur-Yvette Cedex, France, (2) Center for Research in Isotopes and Environmental Dynamics (CRIED), University of Tsukuba, 1-1-1 Tennodai, Tsukuba, Ibaraki 305-8572, Japan

Large quantities of fallout radionuclides emitted during the Fukushima Dai-ichi Nuclear Power Plant (FDNPP) accident were deposited on Japanese soils, thereby leading to the formation of a 3000 km2 contamination plume. Because they are strongly sorbed by fine particles, those radionuclides are likely to be redistributed by hydrosed-imentary processes across catchments. As Ag-110m: Cs-137 activity ratio showed a variation in soils across the main plume, we investigated the behaviour of Silver-110 metastable (Ag-110m) and compared it to the one of the more documented radiocesium (Cs-137) to check whether this ratio may be used to track the dispersion of contaminated sediment. We analysed soil and sediment drape deposits (i.e. mud drapes deposited on channel bed sand in rivers) collected in Nov 2011, April 2012, Nov 2012 and May 2013 within coastal catchments draining the main radioactive pollution plume of Fukushima Prefecture (Japan). Several field experiments were also conducted to document radiosilver behaviour in the terrestrial environment. Results show a similar and low mobility for both elements in soils and a strong affinity with the clay fraction. Measurements conducted on sediment sequences accu-mulated in reservoirs tend to confirm a comparable migration and deposition of both radionuclides even after their redistribution due to erosion and deposition processes. Use of a simple mixing model based on Ag-110m: Cs-137 activity ratio values in both soil and sediment demonstrated the strong reactivity of catchments to the succession of summer typhoons and spring snowmelt. We identified a two stage sediment export cycle with (1) a partial export of contaminated sediment from inland mountain ranges – exposed initially to the highest radionuclide fallout – to the coastal plains in summer and autumn after the occurrence of violent typhoons, and (2) an amplification of the sediment flush during the spring snowmelt. Our results suggest that this contamination export cycle will continue during the next years or decades as large quantities of contaminated material are being stored in reservoirs of the region.

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