Tateda Yutaka, Tsumune Daisuke, Tsubono Takaki, Misumi Kazuhiro, Yamada Masatoshi, Kanda Jota, Ishimaru Takashi
Environmental Science Research Laboratory, Central Research Institute of Electric Power Industry, 1646 Abiko, Abiko-shi, Chiba-ken 270-1194, Japan.
Environmental Science Research Laboratory, Central Research Institute of Electric Power Industry, 1646 Abiko, Abiko-shi, Chiba-ken 270-1194, Japan.
J Environ Radioact. 2016 Jan;151 Pt 2:495-501. doi: 10.1016/j.jenvrad.2015.05.013. Epub 2015 Jun 10.
Radiocesium ((134)Cs and (137)Cs) released into the Fukushima coastal environment was transferred to marine biota inhabiting the Pacific Ocean coastal waters of eastern Japan. Though the levels in most of the edible marine species decreased overtime, radiocesium concentrations in some fishes were still remained higher than the Japanese regulatory limit for seafood products. In this study, a dynamic food chain transfer model was applied to reconstruct (137)Cs levels in olive flounder by adopting the radiocesium concentrations in small demersal fish which constitute an important fraction of the diet of the olive flounder particularly inhabiting area near Fukushima. In addition, (137)Cs levels in slime flounder were also simulated using reported radiocesium concentrations in some prey organisms. The simulated results from Onahama on the southern border of the Fukushima coastline, and at Choshi the southernmost point where the contaminated water mass was transported by the Oyashio current, were assessed in order to identify what can be explained from present information, and what remains to be clarified three years after the Fukushima Dai-ichi nuclear power plant (1FNPP) accident. As a result, the observed (137)Cs concentrations in planktivorous fish and their predator fish could be explained by the theoretically-derived simulated levels. On the other hand, the slow (137)Cs depuration in slime flounder can be attributed to uptake from unknown sources for which the uptake fluxes were of a similar magnitude as the excretion fluxes. Since the reported (137)Cs concentrations in benthic invertebrates off Onahama were higher than the simulated values, radiocesium transfer from these benthic detritivorous invertebrates to slime flounder via ingestion was suggested as a cause for the observed slow depuration of (137)Cs in demersal fish off southern Fukushima. Furthermore, the slower depuration in the demersal fish likely required an additional source of (137)Cs, i.e. contaminated detritus or sediment which was entrained with the prey during the active sediment feeding of this fish species.
释放到福岛沿海环境中的放射性铯((134)Cs和(137)Cs)转移到了栖息在日本东部太平洋沿海水域的海洋生物群中。尽管大多数可食用海洋物种中的放射性铯含量随时间下降,但一些鱼类中的放射性铯浓度仍高于日本海产品的监管限值。在本研究中,应用动态食物链转移模型,通过采用小型底栖鱼类中的放射性铯浓度来重建牙鲆体内的(137)Cs水平,小型底栖鱼类是牙鲆(特别是栖息在福岛附近地区的牙鲆)食物的重要组成部分。此外,还利用一些猎物生物中报告的放射性铯浓度对星康吉鳗体内的(137)Cs水平进行了模拟。对福岛海岸线南部边界的小名滨以及被亲潮输送的污染水体最南端的铫子的模拟结果进行了评估,以便确定根据现有信息可以解释的内容,以及在福岛第一核电站(1FNPP)事故三年后仍有待澄清的内容。结果表明,浮游性鱼类及其捕食性鱼类中观测到的(137)Cs浓度可以由理论推导的模拟水平来解释。另一方面,星康吉鳗体内(137)Cs的缓慢净化可归因于来自未知来源的摄取,其摄取通量与排泄通量大小相似。由于小名滨附近底栖无脊椎动物中报告的(137)Cs浓度高于模拟值,因此有人认为这些底栖食碎屑无脊椎动物通过摄食将放射性铯转移到星康吉鳗体内是福岛南部底栖鱼类中观测到的(137)Cs缓慢净化的一个原因。此外,底栖鱼类中较慢的净化可能需要额外的(137)Cs来源,即受污染的碎屑或沉积物,在这种鱼类积极摄食沉积物的过程中,这些物质会与猎物一起被摄取。