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福岛核事故后爆炸引发的东日本大地震对核电站水净化过程中放射性碘和铯的去除。

Removal of radioactive iodine and cesium in water purification processes after an explosion at a nuclear power plant due to the Great East Japan Earthquake.

机构信息

Department of Environmental Health, National Institute of Public Health, 2-3-6 Minami, Wako, Saitama 351-0197, Japan.

出版信息

Water Res. 2012 Sep 15;46(14):4397-404. doi: 10.1016/j.watres.2012.05.055. Epub 2012 Jun 7.

DOI:10.1016/j.watres.2012.05.055
PMID:22717151
Abstract

The presence of radionuclides at five water purification plants was investigated after an explosion at a nuclear power plant hit by the Great East Japan Earthquake on 11 March 2011. Radioactive iodine (¹³¹I) and cesium (¹³⁴Cs and ¹³⁷Cs) were detected in raw water in Fukushima and neighboring prefectures. ¹³¹I was not removed by coagulation-flocculation-sedimentation. ¹³¹I was removed by granular activated carbon (GAC) and powdered activated carbon (PAC) at a level of about 30%-40%, although ¹³¹I was not removed in some cases. This was also confirmed by laboratory-scale experiments using PAC. The removal percentages of ¹³¹I in river and pond waters by 25 mg dry/L of PAC increased from 36% to 59% and from 41% to 48%, respectively, with chlorine dosing before PAC. ¹³⁴Cs and ¹³⁷Cs were effectively removed by coagulation at both a water purification plant and in laboratory-scale experiments when turbidity was relatively high. In contrast, ¹³⁴Cs and ¹³⁷Cs in pond water with low turbidity were not removed by coagulation. This was because ¹³⁴Cs and ¹³⁷Cs in river water were present mainly in particulate form, while in pond water they were present mainly as cesium ions (¹³⁴Cs+ and ¹³⁷Cs+). However, the removal of ¹³⁴Cs and ¹³⁷Cs in pond water by coagulation increased markedly when ¹³⁴Cs and ¹³⁷Cs were mixed with sediment 24 h before coagulation.

摘要

2011 年 3 月 11 日,日本东海岸发生大地震,福岛核电站发生爆炸后,对 5 家自来水厂进行了放射性核素调查。在福岛县及周边地区的原水中检测到放射性碘(¹³¹I)和铯(¹³⁴Cs 和 ¹³⁷Cs)。¹³¹I 不能通过混凝-絮凝-沉淀去除。¹³¹I 可通过颗粒活性炭(GAC)和粉末活性炭(PAC)去除约 30%-40%,但在某些情况下无法去除。这也通过使用 PAC 的实验室规模实验得到了证实。在 PAC 之前投加氯,PAC 对河流和池塘水中 ¹³¹I 的去除率分别从 36%增加到 59%和从 41%增加到 48%。当浊度较高时,¹³⁴Cs 和 ¹³⁷Cs 在自来水厂和实验室规模实验中均可通过混凝有效去除。相比之下,浊度较低的池塘水中的 ¹³⁴Cs 和 ¹³⁷Cs 不能通过混凝去除。这是因为河流水中的 ¹³⁴Cs 和 ¹³⁷Cs 主要以颗粒形式存在,而池塘水中的 ¹³⁴Cs 和 ¹³⁷Cs 主要以铯离子(¹³⁴Cs+和 ¹³⁷Cs+)形式存在。然而,当 ¹³⁴Cs 和 ¹³⁷Cs 与沉积物混合 24 小时后再进行混凝时,池塘水中 ¹³⁴Cs 和 ¹³⁷Cs 的去除率显著增加。

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