Kumamoto Yuichiro, Aoyama Michio, Hamajima Yasunori, Murata Akihiko, Kawano Takeshi
Research and Development Center for Global Change, Japan Agency for Marine-Earth Science and Technology, 2-15 Natushima-cho, Yokosuka, Kanagawa 237-0061, Japan.
Institute of Environmental Radioactivity, Fukushima University, 1-1 Kanayagawa, Fukushima 960-1296, Japan.
J Environ Radioact. 2015 Feb;140:114-22. doi: 10.1016/j.jenvrad.2014.11.010. Epub 2014 Nov 27.
We measured vertical distributions of radiocesium ((134)Cs and (137)Cs) at stations along the 149°E meridian in the western North Pacific during winter 2012, about ten months after the Fukushima Dai-ichi Nuclear Power Plant (FNPP1) accident. The Fukushima-derived (134)Cs activity concentration and water-column inventory were largest in the transition region between 35 and 40°N approximately due to the directed discharge of the contaminated water from the FNPP1. The bomb-derived (137)Cs activity concentration just before the FNPP1 accident was derived from the excess (137)Cs activity concentration relative to the (134)Cs activity concentration. The water-column inventory of the bomb-derived (137)Cs was largest in the subtropical region south of 35°N, which implies that the Fukushima-derived (134)Cs will also be transported from the transition region to the subtropical region in the coming decades. Mean values of the water-column inventories decay-corrected for the Fukushima-derived (134)Cs and the bomb-derived (137)Cs were estimated to be 1020 ± 80 and 820 ± 120 Bq m(-2), respectively, suggesting that in winter 2012 the impact of the FNPP1 accident in the western North Pacific Ocean was nearly the same as that of nuclear weapons testing. Relationship between the water-column inventory and the activity concentration in surface water for the radiocesium is essential information for future evaluation of the total amount of Fukushima-derived radiocesium released into the North Pacific Ocean.
2012年冬季,在福岛第一核电站事故发生约十个月后,我们在北太平洋西部149°E经线上的各站点测量了放射性铯(¹³⁴Cs和¹³⁷Cs)的垂直分布。源自福岛的¹³⁴Cs活度浓度和水柱存量在北纬35°至40°之间的过渡区域最大,这大约是由于福岛第一核电站受污染水的定向排放。福岛第一核电站事故前源自核弹的¹³⁷Cs活度浓度是由相对于¹³⁴Cs活度浓度的过量¹³⁷Cs活度浓度得出的。源自核弹的¹³⁷Cs的水柱存量在北纬35°以南的亚热带区域最大,这意味着在未来几十年里,源自福岛的¹³⁴Cs也将从过渡区域输送到亚热带区域。对源自福岛的¹³⁴Cs和源自核弹的¹³⁷Cs进行衰变校正后的水柱存量平均值估计分别为1020±80和820±120 Bq m⁻²,这表明在2012年冬季,福岛第一核电站事故对北太平洋西部的影响与核武器试验的影响几乎相同。放射性铯的水柱存量与表层水活度浓度之间的关系是未来评估释放到北太平洋的源自福岛的放射性铯总量的重要信息。