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Radioactive fallout cesium in sewage sludge ash produced after the Fukushima Daiichi nuclear accident

机译:福岛第一核电站事故后产生的污水污泥灰中的放射性沉降铯

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The radioactive fallout cesium (Cs-137) in the sewage sludge ashes (SSAs) produced in Japan after the Fukushima Daiichi Nuclear Accident was tested. Five samples of SSAs produced in 2011 and 2012 were tested. Two of the samples contained Cs-137 (23 and 9.6 kBq/kg, respectively) above the radioactivity criterion (8 kBq of radioactive Cs/kg of solid) for controlled landfill disposal in Japan. The mineral components of SSA are roughly divided into two groups: an HCl-soluble phase mainly composed of phosphates and oxides; and silicates, including quartz, feldspar, and clay. Both phases contained Cs-137. The majority (up to 90%) of Cs-137 was contained in the HCl-soluble phase. Among the HCl-soluble sub-phases, Fe-bearing phases that were probably iron oxides were mainly responsible for Cs-137 retention. No positive evidence was obtained that showed that phosphate-bearing phases, which were included most in SSAs along with the silicate phase, retained Cs-137. Prepulverizing SSAs and heating them at 95 degrees C in a 6 M or a concentrated aqueous HCl was the most effective method of dissolving the HCl-soluble phase. The radioactivity concentrations of Cs-137 in all the HCl-treatment residues were below the radioactivity criterion. This residue was mostly composed of silicates. After static leaching tests of the residue at 60 degrees C for 28 days, no Cs-137 was detected in simulated environmental water leachates (pure water and synthetic seawater), demonstrating that Cs-137 in the residue is very stably immobilized in the silicates. (C) 2014 Elsevier Ltd. All rights reserved.
机译:在福岛第一核电站核事故后,日本生产的污水污泥灰(SSA)中的放射性沉降铯(Cs-137)被测试。测试了2011年和2012年生产的5个SSA样本。在日本,有两个样品的Cs-137(分别为23 kbq / kg和9.6 kBq / kg)高于放射线标准(放射性Cs / kg固体8 kBq / kg),用于受控的垃圾掩埋处置。 SSA的矿物成分大致分为两类:HCl可溶性相,主要由磷酸盐和氧化物组成;硅酸盐,包括石英,长石和粘土。两个阶段均包含Cs-137。大部分(最高90%)Cs-137包含在HCl可溶性相中。在HCl可溶性亚相中,可能是氧化铁的含Fe相主要负责Cs-137的保留。没有获得任何积极证据表明,SSA和硅酸盐相中大部分都包含有磷酸盐的相保留了Cs-137。将SSA进行预粉碎并将其在95°C的6 M或浓HCl水溶液中加热是溶解HCl可溶性相的最有效方法。所有HCl处理残渣中Cs-137的放射性浓度均低于放射性标准。该残余物主要由硅酸盐组成。在60摄氏度下对残留物进行静态浸出试验28天后,在模拟的环境水浸出液(纯水和合成海水)中未检测到Cs-137,表明残留物中的Cs-137非常稳定地固定在硅酸盐中。 (C)2014 Elsevier Ltd.保留所有权利。

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