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水热处理从粘土矿物中解吸铯:有机酸的作用及其对土壤去污的意义。

Hydrothermal-treatment desorption of cesium from clay minerals: The roles of organic acids and implications for soil decontamination.

机构信息

Laboratory for Advanced Nuclear Energy, Tokyo Institute of Technology, 2-12-1, Ookayama, Meguro-ku, Tokyo, 152-8550, Japan; Collaborative Laboratories for Advanced Decommissioning Science (CLADS), Japan Atomic Energy Agency, 790-1 Otsuka, Motooka, Tomioka, Fukushima, 979-1195, Japan.

Laboratory for Advanced Nuclear Energy, Tokyo Institute of Technology, 2-12-1, Ookayama, Meguro-ku, Tokyo, 152-8550, Japan.

出版信息

Water Res. 2020 Jun 15;177:115804. doi: 10.1016/j.watres.2020.115804. Epub 2020 Apr 8.

Abstract

The adsorption and desorption of cesium (Cs) on clays of contaminated soil in a rhizosphere zone can be greatly affected by various biogeochemical processes, the timespans of which are usually months to years. Herein, we present several representative scenarios of the binding of Cs on diverse sites of vermiculitized biotite by controlled Cs adsorption to particles of different sizes. We investigated whether and how the fixed Cs in the different scenarios is desorbed by ambient and hydrothermal treatments with several low-molecular-weight organic acids (LMWOAs). The results showed that the sorbed Cs was discriminatively retained in the un-collapsed, partially collapsed, and thoroughly collapsed structures of vermiculites. The desorption of the sorbed Cs by hydrothermal LMWOAs extractions was easily realized in the un-collapsed structure, but was limited or minimal in the partially collapsed and thoroughly collapsed structures. The Cs desorption varied in accord with the LMWOA species applied and increased with the acid concentration, temperature, and number of treating cycles. The analysis of Cs-desorbed specimens confirmed their partial destruction and interlayer expansion, suggesting that the underlying mechanism of Cs removal by LMWOAs involves not only acid dissolution and complexation but also the accelerated weathering of clays within a short time under hydrothermal conditions. Our findings contribute novel insights into the mobility, bioavailability, and fate of Cs in contaminated soils and its removal from these soils for environmental restorations.

摘要

受各种生物地球化学过程的影响,放射性核素铯(Cs)在污染土壤根际带粘土层中的吸附和解吸作用的时间跨度通常为数月至数年。在此,我们通过控制 Cs 在不同粒径颗粒上的吸附,展示了 Cs 结合到蛭石化黑云母不同位点的几种有代表性的情况。我们研究了在不同情况下,固定在不同位置的 Cs 能否以及如何通过环境和热液处理被几种低分子量有机酸(LMWOAs)解吸。结果表明,被吸附的 Cs 可在未坍塌、部分坍塌和完全坍塌的蛭石结构中被有区别地保留。在未坍塌结构中,热液 LMWOA 萃取很容易实现对吸附 Cs 的解吸,但在部分坍塌和完全坍塌结构中受到限制或最小。Cs 的解吸随应用的 LMWOA 种类而变化,并随酸浓度、温度和处理循环次数的增加而增加。对解吸样品的 Cs 分析证实了它们的部分破坏和层间膨胀,表明 LMWOAs 去除 Cs 的潜在机制不仅涉及酸溶解和络合,还涉及在短时间内热液条件下粘土的加速风化。我们的发现为污染土壤中 Cs 的迁移性、生物可利用性和归宿以及这些土壤中 Cs 的去除提供了新的见解,有助于环境修复。

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