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Development of a new model simulating contaminations of forest resources with radiocesium in Fukushima

Ota, Masakazu  ; Koarashi, Jun   

In forests affected by the Fukushima Daiichi Nuclear Power Plant accident, trees became contaminated with $$^{137}$$Cs. However, $$^{137}$$Cs transfer processes determining the tree contamination (particularly for stem wood, a prominent commercial resource) remain insufficiently understood. We propose a model (SOLVEG-R) for simulating dynamic behavior of $$^{137}$$Cs in a forest tree-litter-soil system and applied it to contaminated forests of cedar plantation and natural oak stand in Fukushima to elucidate relative impact of distinct $$^{137}$$Cs transfer processes determining the tree contamination. The transfer of $$^{137}$$Cs to the trees occurred mostly ($$>$$99%) through surface uptake of $$^{137}$$Cs trapped by needles and bark during the fallout. Root uptake of soil $$^{137}$$Cs was several orders of magnitude lower than the surface uptake over a 50-year period following the accident. As a result, internal contamination of the trees proceeded through an enduring recycling (translocation) of $$^{137}$$Cs absorbed on the tree surface. A significant surface uptake of $$^{137}$$Cs through bark was suggested, contributing to 100% (leafless oak tree) and 30% (foliated cedar tree; the remaining uptake occurred at needles) of the total uptake by the trees. It was suggested that the activity concentration of $$^{137}$$Cs in stem wood of the trees at these sites are currently (as of 2021) decreasing by 3% per year, mainly through radioactive decay of $$^{137}$$Cs and partly through dilution effect from tree growth.

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