Department of Forest Soils, Forestry and Forest Products Research Institute, 1 Matsunosato, Tsukuba, Ibaraki, 305-8687, Japan.
Department of Mushroom Science and Forest Microbiology, Forestry and Forest Products Research Institute, 1 Matsunosato, Tsukuba, Ibaraki, 305-8687, Japan.
J Environ Radioact. 2020 Dec;225:106422. doi: 10.1016/j.jenvrad.2020.106422. Epub 2020 Sep 24.
This study investigated the temporal change in vertical distributions of radiocesium inventories in Japanese forest soils during the early phase (from 2011 to 2017) following the Fukushima Daiichi Nuclear Power Plant (FDNPP) accident, using three simple parameters. We calculated the fraction in the organic layer (F), the migration center (X) and the relaxation depth (α) using 99 soil inventory data sets. F decreased significantly from 2011 to 2017 (logistic analysis, p < 0.001). In addition, F in the FDNPP zone rapidly decreased compared to that in the Chernobyl Nuclear Power Plant (ChNPP) zone from the first year to the second year. Different migration rates from organic to mineral soil layers between previous studies in the ChNPP and this study have several possible causes such as organic litter features, climate and physico-chemical forms of initial deposition. In mineral soil layers in the FDNPP zone, only X increased significantly with time according to generalized mixed model analysis (p < 0.01). However, X and α in the ChNPP zone decreased from two to five years after the accident in 1986, which shows a high Cs retention in the organic layer even in the fifth year after the accident. The vertical migration of Cs in the mineral soil layer in the FDNPP zone appears to be due to low input of Cs from organic to surface mineral soil layer after the second year. These results indicate that Cs retention capacity of the organic layer can affect the apparent vertical migration of Cs in the underlying mineral soil layer.
本研究使用三个简单参数,调查了福岛第一核电站(FDNPP)事故后早期(2011 年至 2017 年)日本森林土壤中放射性铯蓄积量的垂直分布的时间变化。我们使用 99 个土壤存量数据集计算了有机层中的分数(F)、迁移中心(X)和弛豫深度(α)。F 从 2011 年到 2017 年显著下降(逻辑分析,p<0.001)。此外,与切尔诺贝利核电站(ChNPP)区相比,FDNPP 区的 F 在第一年到第二年迅速下降。先前在 ChNPP 区和本研究中从有机层到矿物质土壤层的不同迁移率可能有几个原因,例如有机碎屑的特征、气候和初始沉积的物理化学形式。在 FDNPP 区的矿物质土壤层中,只有 X 根据广义混合模型分析随时间显著增加(p<0.01)。然而,ChNPP 区的 X 和 α 在 1986 年事故发生后的两到五年内下降,这表明即使在事故发生后的第五年,有机层中仍保留有高浓度的 Cs。FDNPP 区矿物质土壤层中 Cs 的垂直迁移似乎是由于第二年以后有机层向表层矿物质土壤层输入的 Cs 量减少所致。这些结果表明,有机层的 Cs 保留能力会影响下部矿物质土壤层中 Cs 的明显垂直迁移。