Quantitative understanding of the impact of flooding durations on Cd variations in an acidic paddy soil during the flooding and drainage processes

Hanbing Meng , Shiwen Hu , Yang Yang , Guojun Chen , Wenting Chi , Kuan Cheng , Tongxu Liu
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Abstract

The solubility and transformation of cadmium (Cd) are controlled by paddy soil pH, whereas paddy soil pH varies during flooding and drainage and is significantly controlled by flooding durations. However, there is still a lack of modeling approaches for simulating the impact of flooding durations on pH fluctuation and concomitant Cd effectiveness in Cd-polluted acidic paddy soils. Herein, laboratory findings combined with a process-based numerical modeling method were used to quantify the observed key geochemical processes of Fe/C/N/S and the accompanying Cd partitioning dynamics during flooding and drainage. During flooding stage, the number of protons consumed by Fe(III), NO3, and SO42− reduction increased with flooding durations, resulting in an increase of pH, which enhanced Cd immobilization and reduced Cd potential risk. After entering drainage stage, the number of protons released from Fe(II), NH4+, and S2− oxidation increased with flooding time, leading to pH decrease, which increased Cd release. A process-based kinetic model fitting results showed that Fe(III) reduction and Fe(II) oxidation were key processes that increased and decreased pH, respectively, and that increasing flooding durations were not beneficial to Cd immobilization during flooding and drainage processes. The results of this study shed light on the impact of redox state of paddy soil on Cd dynamics under different flooding durations and provide a theoretical approach to quantify the contribution of key processes controlling changes in metal species, which can be used to simulate the dynamic behavior of heavy metals in paddy soil under different natural conditions by coupling other significant processes.

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定量了解在淹水和排水过程中,淹水持续时间对酸性水稻土Cd变化的影响
镉的溶解度和转化受水稻土pH值控制,而水稻土pH值在淹水和排水过程中发生变化,且受淹水持续时间的显著控制。然而,目前还缺乏模拟洪水持续时间对镉污染酸性水稻土pH波动和伴随Cd有效性影响的建模方法。本文采用实验室研究结果和基于过程的数值模拟方法,对观测到的Fe/C/N/S关键地球化学过程及其伴随的Cd分配动力学进行了量化。在浸水阶段,Fe(III)、NO3−和SO42−还原所消耗的质子数随着浸水时间的延长而增加,导致pH增加,从而增强了Cd的固定化,降低了Cd的潜在风险。进入排水阶段后,Fe(II)、NH4+和S2−氧化释放的质子数随着淹水时间的增加而增加,导致pH降低,Cd释放增加。基于过程的动力学模型拟合结果表明,Fe(III)还原和Fe(II)氧化分别是pH升高和降低的关键过程,并且在驱水和排水过程中,增加淹水时间不利于Cd的固定。研究结果揭示了不同淹水持续时间下水稻土氧化还原状态对镉动态的影响,为量化控制重金属种类变化的关键过程的贡献提供了理论途径,可通过耦合其他重要过程来模拟不同自然条件下水稻土中重金属的动态行为。
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来源期刊
Soil security
Soil security Soil Science
CiteScore
4.00
自引率
0.00%
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0
审稿时长
90 days
期刊最新文献
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