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基于福岛事故后野外观测结果对底栖鱼类中(137)Cs 长生态半衰期成分的思考。

Consideration on the Long Ecological Half-Life Component of (137)Cs in Demersal Fish Based on Field Observation Results Obtained after the Fukushima Accident.

机构信息

Office of Biospheric Assessment for Waste Disposal, National Institute of Radiological Sciences , Anagawa 4-9-1, Inage-ku, Chiba 263-8555, Japan.

出版信息

Environ Sci Technol. 2016 Feb 16;50(4):1804-11. doi: 10.1021/acs.est.5b04952. Epub 2016 Feb 1.

Abstract

Radiocesium concentrations in most marine fish collected off the coast of Fukushima and surrounding prefectures have decreased with time, and four years after the Fukushima Daiichi Nuclear Power Plant accident occurred, radiocesium concentrations have generally fallen below the detectable level (ca. < 10 Bq kg(-1)-raw). Only in some demersal fish species have detectable concentration levels still been found, and even these species have showed slow radiocesium decreases. The food web was considered as the major factor causing this phenomenon; however, slow elimination rates of radiocesium from these fish species also could be the cause. The latter effect was examined by considering that the (137)Cs concentration decreasing trend in fish could be fit with a set of three exponentially decreasing components; that is, having short, intermediate, and long biological half-lives. The long ecological half-life component was calculated using a 400-1500 d period of monitoring results for Japanese rockfish (Sebastes cheni) and compared with previous reported laboratory results for biological half-life. The obtained ecological half-lives ranged from 274-365 d, and these values agreed with the biological half-life of this fish species. This result implied that the long biological half-lives of radiocesium in some demersal fish species made their radiocesium contamination periods longer.

摘要

在福岛及周边地区海域捕捞的大多数海洋鱼类中的放射性铯浓度随时间推移而降低,福岛第一核电站事故发生四年后,放射性铯浓度通常已降至检测水平以下(约<10 Bq kg-1-鲜重)。只有在一些底栖鱼类中仍发现有可检测到的浓度水平,而即使是这些鱼类,其放射性铯的含量也在缓慢下降。食物网被认为是造成这种现象的主要因素;然而,这些鱼类中放射性铯的缓慢消除率也可能是原因之一。通过考虑鱼类体内(137)Cs 浓度的下降趋势可以拟合一组三个指数衰减分量,即具有短、中和长生物半衰期,来检验后一种效应。使用日本石斑鱼(Sebastes cheni)长达 400-1500 天的监测结果来计算长生态半衰期分量,并与之前报道的生物半衰期的实验室结果进行比较。得到的生态半衰期范围为 274-365 天,这些值与该鱼类的生物半衰期一致。这一结果表明,一些底栖鱼类中放射性铯的长生物半衰期导致其放射性铯污染期延长。

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