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KINETICS OF METAL FIXATION IN SOILS: MEASUREMENT AND MODELING BY ISOTOPIC DILUTION

机译:土壤中金属固定的动力学:同位素稀释法的测量和模拟

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摘要

The bioavailability of metal contaminants in soils varies widely, depending on soil characteristics and the source of the contaminant. As a consequence, site-specific risk assessment requires accurate prediction of the bioavailable (or labile) fraction of soil metal. Moreover, metals in soil are subject to time-dependent processes, which affect their bioavailability and thereby complicate the prediction of future risk. The aim of the present study was to describe the development of simple, readily applicable models for the time-dependent changes in lability of Cd and Zn in soils. We present data showing the time-dependent behavior of radiolabile and soil solution concentrations of Cd and Zn during an incubation study over a period of 813 d in 23 diverse soils. The data are used to parameterize candidate models of metal fixation in soils designed to be readily applicable and therefore relevant to risk assessment. We conclude that the final extent of metal fixation increases with pH and generally is greater for Zn than for Cd; however, the rate of fixation is independent of pH and equivalent to a half-time to equilibrium of 29 and 89 d for Cd and Zn, respectively. It is possible that longer-term processes occur, especially for Zn, but these could not be detected in the present study.
机译:土壤中金属污染物的生物利用度差异很大,具体取决于土壤特性和污染物来源。因此,针对具体地点的风险评估需要准确预测土壤金属的生物利用度(或不稳定度)。此外,土壤中的金属会经历时间依赖性过程,这会影响其生物利用度,从而使对未来风险的预测变得复杂。本研究的目的是描述针对土壤中Cd和Zn的不稳定性随时间变化的简单易用模型的发展。我们提供的数据显示了在23种土壤中813 d的潜伏期研究过程中,镉和锌的放射性不稳定和土壤溶液浓度的时间依赖性行为。数据用于对土壤中金属固定的候选模型进行参数化,该模型设计为易于应用,因此与风险评估相关。我们得出的结论是,金属固定的最终程度随pH的增加而增加,通常锌比镉大。但是,固定速率与pH无关,并且分别等于Cd和Zn的平衡半衰期29和89 d。可能发生长期过程,尤其是对于锌,但是在本研究中无法检测到。

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