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首页> 外文期刊>Biogeosciences >Distribution of the Fukushima-derived radionuclides in seawater in the Pacific off the coast of Miyagi, Fukushima, and Ibaraki Prefectures, Japan
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Distribution of the Fukushima-derived radionuclides in seawater in the Pacific off the coast of Miyagi, Fukushima, and Ibaraki Prefectures, Japan

机译:日本宫城县,福岛县和茨城县沿岸的太平洋海水中福岛衍生的放射性核素的分布

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摘要

The activities of artificial radionuclides in seawater samples collected offthe coast of Miyagi, Fukushima, and Ibaraki Prefectures were measured as partof a monitoring program initiated by the Japanese Ministry of Education,Sports, Science and Technology immediately after the Fukushima Dai-ichiNuclear Power Plant accident. The spatial and temporal distributions of thoseactivities are summarized herein. The activities of strontium-90, iodine-131,cesium-134 and -137 (i.e. 90Sr, 131I, 134Cs, and 137Cs)derived from the accident were detected in seawater samples taken from areasof the coastal ocean adjacent to the power plant. No 131I was detectedin surface waters (≤ 5 m depth) or in intermediate and bottom watersafter 30 April 2011. Strontium-90 was found in surface waters collected froma few sampling stations in mid-August 2011 to mid-December 2011. Temporalchanges of 90Sr activity in surface waters were evident, although the90Sr activity at a given time varied widely between sampling stations.The activity of 90Sr in surface waters decreased slowly over time, andby the end of December 2011 had reached background levels recorded before theaccident. Radiocesium, 134Cs and 137Cs, was found in seawatersamples immediately after the accident. There was a remarkable change inradiocesium activities in surface waters during the first 7 months (Marchthrough September 2011) after the accident; the activity reached a maximum inthe middle of April and thereafter decreased exponentially with time.Qualitatively, the distribution patterns in surface waters suggested that inearly May radiocesium-polluted water was advected northward; some of thewater then detached and was transported to the south. Two water cores withhigh 137Cs activity persisted at least until July 2011. In subsurfacewaters radiocesium activity was first detected in the beginning of April2011, and the water masses were characterized by σt (an indicatorof density) values of 25.5–26.5. From 9–14 May to 5–16 December 2011, thedepths of the water masses increased with time, an indication that deepeningof the isopycnal surfaces with time can be an important mechanism for thetransport of radiocesium downward in coastal waters. During 4–21 February2012, the water column became vertically homogeneous, probably because ofconvective mixing during the winter; the result was nearly constant values ofradiocesium activity throughout the water column from the surface to thebottom (~200 m depth) at each station.
机译:在福岛第一核电站事故发生后,日本教育,体育,科学和技术部启动了一项监测计划,对在宫城县,福岛县和茨城县附近海岸采集的海水样本中的人造放射性核素进行了测量。这些活动的空间和时间分布在此概述。锶90,碘131,铯134和-137(即 90 Sr, 131 I, 134 Cs和在事故发源地的海水样本中检测到了来自事故的 137 Cs)。在2011年4月30日之后的地表水(≤5 m深度)或中层和底层水中均未检测到 131 I。在2011年8月中旬至中旬从几个采样站采集的地表水中未发现锶90。 -2011年12月。地表水中 90 Sr活性的时间变化是明显的,尽管在特定时间段内 90 Sr活性在采样站之间变化很大。随着时间的推移,地表水中的90 Sr逐渐降低,到2011年12月底已达到事故发生前的背景水平。事故发生后立即在海水样品中发现了放射性铯 134 Cs和 137 Cs。事故发生后的前7个月(2011年3月至2011年9月),地表水中的放射性铯活动发生了显着变化。从质量上看,地表水的分布规律表明,5月初放射性铯污染的水向北平流。然后一些水分离出来并运到南部。两个具有高 137 Cs活性的水核至少持续到2011年7月。在地下水中,放射性铯的活性在2011年4月开始被首次检测到,水团的特征是σ < sub> t (密度指标)的值为25.5–26.5。从2011年5月9日至14日至12月5日至16日,水团的深度随时间增加,这表明等深面随时间的加深可能是沿海地区放射性铯向下传播的重要机制。在2012年2月4日至21日,水柱在垂直方向上变得均匀,这可能是由于冬季对流混合造成的;结果是每个站点从地表到底部(约200 m深度)的整个水柱中的es活度值几乎恒定。

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