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铁锰(氧)氢氧化物而非硫化物决定了水稻土系统排水过程中 Cd 的迁移。

Iron-Manganese (Oxyhydro)oxides, Rather than Oxidation of Sulfides, Determine Mobilization of Cd during Soil Drainage in Paddy Soil Systems.

机构信息

Nanjing Agricultural University , College of Resources and Environmental Sciences , Nanjing 210095 , China.

The University of Queensland , School of Agriculture and Food Sciences , St Lucia , Queensland 4072 , Australia.

出版信息

Environ Sci Technol. 2019 Mar 5;53(5):2500-2508. doi: 10.1021/acs.est.8b06863. Epub 2019 Feb 21.

Abstract

The preharvest drainage of rice paddy fields during the grain filling stage can result in a substantial mobilization of Cd in soil and, consequently, elevated grain Cd concentration. However, the processes controlling the mobilization of Cd remains poorly understood. Using 12 field-contaminated paddy soils, we investigated the factors controlling the temporal changes in Cd solubility in paddy soils that were incubated anaerobically for 40 d followed by a 20 d oxidation period. Soluble and extractable Cd concentrations decreased rapidly upon flooding but increased during the oxidation phase, with Cd solubility (aqueous Cd/soil Cd) largely depending upon porewater pH. Furthermore, inhibiting sulfate reduction or inhibiting oxidation dissolution of Cd-sulfides had little or no effect on the mobilization of Cd in the subsequent oxidation phase. Both sequential extraction and X-ray absorption spectroscopy (XAS) analyses revealed that changes in Cd solubility were largely dependent upon the transformation of Cd between the Fe-Mn (oxyhydro)oxide fraction and exchangeable fraction. Mobilization of Cd upon soil drainage was caused by a decrease in soil pH resulting in the release of Cd from Fe-Mn (oxyhydro)oxides. Taken together, Fe-Mn (oxyhydro)oxides play a critical (and prevalent) role in controlling the mobilization of Cd upon soil drainage in paddy systems.

摘要

在稻谷灌浆期排干稻田中的水会导致土壤中大量的镉被迁移,从而使稻谷中的镉浓度升高。然而,控制镉迁移的过程仍不甚清楚。本研究采用 12 个田间污染的稻田土壤,在厌氧条件下培养 40 天后,再进行 20 天的氧化期,研究了控制稻田土壤中镉溶解性随时间变化的因素。在淹水期间,可溶态和可提取态镉浓度迅速下降,但在氧化阶段增加,镉的溶解性(水溶态镉/土壤镉)很大程度上取决于孔隙水 pH 值。此外,抑制硫酸盐还原或抑制 Cd-硫化物的氧化溶解对随后氧化阶段镉的迁移几乎没有影响。连续提取和 X 射线吸收光谱(XAS)分析表明,镉溶解性的变化主要取决于 Cd 在 Fe-Mn(氢氧化物)氧化物部分和可交换部分之间的转化。土壤排水时镉的迁移是由于土壤 pH 值降低,导致 Fe-Mn(氢氧化物)氧化物中 Cd 的释放。总之,Fe-Mn(氢氧化物)在控制稻田系统土壤排水时镉的迁移中起着关键(和普遍)的作用。

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