Symbiotic Systems Science and Technology, Fukushima University, Fukushima, Fukushima City, Kanayagawa, 960-1248, Japan.
UK Centre for Ecology & Hydrology, Lancaster Environment Center, Library Av., Bailrigg, Lancaster, LA1 4AP, UK.
J Environ Radioact. 2021 Jan;226:106457. doi: 10.1016/j.jenvrad.2020.106457. Epub 2020 Nov 20.
Radiocesium was dispersed from the Fukushima Dai-ichi disaster in March 2011, causing comparatively high radioactive contamination in nearby environments. Radionuclide concentrations in wild rodents (Apodemus argenteus, and Apodemus speciosus) within these areas were monitored from 2012 to 2016. However, whole-organism to soil transfer parameters (i.e., concentration ratio, CR) for wild rodents at Fukushima were not determined and hence were lacking from the international transfer databases. We augmented the 2012-2016 data by collecting soil activity concentrations (Bq kg, dry mass) from five rodent sampling sites in Fukushima Prefecture, and developed corresponding CR values for radiocesium (Cs and Cs) based on rodent radioactivity concentrations (Bq kg, fresh mass). The CR were added to the Wildlife Transfer Database (WTD; http://www.wildlifetransferdatabase.org/), supporting the development of the International Commission on Radiological Protection's (ICRP) environmental protection framework, and increasing the WTD from 84 to 477 entries for cesium and Muridae ('Reference Rat'). Significant variation occurred in CR values between study sites within Fukushima Prefecture. The geometric mean CR, in this paper, was higher than that reported for Muridae species for Chernobyl. Radiocaesium absorbed dose rates were also estimated for wild rodents inhabiting the five Fukushima study sites and ranged from 1.3 to 33 μGy h. Absorbed dose rates decreased by a factor of two from 2012 to 2016. Dose rates in highly contaminated areas were within the ICRP derived consideration reference level for Reference Rat (0.1-1 mGy d), suggesting the possible occurrence of deleterious effects and need for radiological effect studies in the Fukushima area.
2011 年 3 月福岛第一核电站灾难释放了放射性铯,导致附近环境受到相对较高的放射性污染。从 2012 年到 2016 年,监测了这些地区内野生啮齿动物(银狐和日本姬鼠)的放射性核素浓度。然而,福岛野生啮齿动物的整体-土壤转移参数(即浓度比,CR)尚未确定,因此在国际转移数据库中缺失。我们通过收集福岛县五个啮齿动物采样点的土壤活度浓度(Bq kg,干质量),对 2012-2016 年的数据进行了扩充,并根据啮齿动物放射性浓度(Bq kg,鲜质量)得出了放射性铯(Cs 和 Cs)的相应 CR 值。这些 CR 值被添加到野生动物转移数据库(WTD;http://www.wildlifetransferdatabase.org/)中,支持了国际辐射防护委员会(ICRP)环境保护框架的发展,并使 WTD 中铯和 Muridae(“参考鼠”)的条目从 84 增加到 477。福岛县内各研究点的 CR 值存在显著差异。本文中的几何平均 CR 值高于切尔诺贝利报告的 Muridae 种。还估计了栖息在五个福岛研究点的野生啮齿动物的放射性铯吸收剂量率,范围为 1.3 至 33 μGy h。从 2012 年到 2016 年,吸收剂量率下降了一个数量级。高污染地区的剂量率在 ICRP 为参考鼠设定的考虑参考水平(0.1-1 mGy d)范围内,表明在福岛地区可能发生有害影响,需要进行放射性效应研究。