Environmental Science Research Laboratory, Central Research Institute of Electric Power Industry, 1646 Abiko, Abiko-shi, Chiba-ken 270-1194, Japan.
J Environ Radioact. 2013 Oct;124:1-12. doi: 10.1016/j.jenvrad.2013.03.007. Epub 2013 Apr 29.
The Fukushima Dai-ichi Nuclear Power Plant (1F NPP) accident occurred on 11 March 2011. The accident introduced (137)Cs into the coastal waters which was subsequently transferred to the local coastal biota thereby elevating the concentration of this radionuclide in coastal organisms. In this study, the radioactive cesium levels in coastal biota from the southern Fukushima area were simulated using a dynamic biological compartment model. The simulation derived the possible maximum radioactive cesium levels in organisms, indicating that the maximum (137)Cs concentrations in invertebrates, benthic fish and predator fish occurred during late April, late May and late July, respectively in the studied area where the source was mainly the direct leakage of (137)Cs effluent from the 1F NPP. The delay of a (137)Cs increase in fish was explained by the gradual food chain transfer of (137)Cs introduced to the ecosystem from the initial contamination of the seawater. The model also provided the degree of radionuclide depuration in organisms, and it demonstrated the latest start of the decontamination phase in benthic fish. The ecological half-lives, derived both from model simulation and observation, were 1-4 months in invertebrates, and 2-9 months in plankton feeding fish and coastal predator fish from the studied area. In contrast, it was not possible to similarly calculate these parameters in benthic fish because of an unidentified additional radionuclide source which was deduced from the biological compartment model. To adequately reconstruct the in-situ depuration of radiocesium in benthic fish in the natural ecosystem, a contamination source associated with the bottom sediments is necessary.
福岛第一核电站(1F NPP)事故于 2011 年 3 月 11 日发生。事故将(137)Cs 引入沿海水域,随后转移到当地沿海生物群,从而提高了沿海生物体内这种放射性核素的浓度。在这项研究中,使用动态生物区室模型模拟了来自福岛南部地区沿海生物群的放射性铯水平。该模拟得出了生物体中放射性铯的可能最大水平,表明在研究区域中,最大(137)Cs 浓度分别出现在无脊椎动物、底栖鱼类和掠食性鱼类中,发生时间分别为 4 月底、5 月底和 7 月底,而这些放射性核素的主要来源是 1F NPP 中(137)Cs 流出物的直接泄漏。鱼类中(137)Cs 增加的延迟是由于从海水初始污染开始,(137)Cs 逐渐向生态系统中食物链转移所导致的。该模型还提供了生物体中放射性核素净化的程度,并证明了底栖鱼类中净化阶段的最新开始。从模型模拟和观察中得出的生态半衰期分别为 1-4 个月的无脊椎动物,以及 2-9 个月的浮游生物食性鱼类和沿海掠食性鱼类。相比之下,由于从生物区室模型推断出的一个未知的额外放射性核素来源,底栖鱼类的这些参数无法进行类似的计算。为了充分重建自然生态系统中底栖鱼类放射性铯的现场净化,需要与底泥有关的污染来源。