Guangzhou Institute of Geochemistry, Chinese Academy of Sciences, Guangzhou 510640, China; National-Regional Joint Engineering Research Center for Soil Pollution Control and Remediation in South China, Guangdong Key Laboratory of Integrated Agro-environmental Pollution Control and Management, Institute of Eco-environmental and Soil Sciences, Guangdong Academy of Sciences, Guangzhou 510650, China; University of Chinese Academy of Sciences, Beijing 100049, China.
National-Regional Joint Engineering Research Center for Soil Pollution Control and Remediation in South China, Guangdong Key Laboratory of Integrated Agro-environmental Pollution Control and Management, Institute of Eco-environmental and Soil Sciences, Guangdong Academy of Sciences, Guangzhou 510650, China.
J Environ Sci (China). 2022 Mar;113:269-280. doi: 10.1016/j.jes.2021.06.009. Epub 2021 Jul 3.
While the transformation of antimony (Sb) in paddy soil has been previously investigated, the biogeochemical processes of highly chemical active Sb in the soil remain poorly understood. In addition, there is a lack of quantitative understanding of Sb transformation in soil. Therefore, in this study, the kinetics of exogenous Sb in paddy soils were investigated under anaerobic and aerobic incubation conditions. The dissolved Sb(V) and the Sb(V) extracted by diffusive gradient technique decreased under anaerobic conditions and then increased under aerobic conditions. The redox reaction of Sb occurred, and Sb bioavailability significantly decreased after 55 days of incubation. The kinetics of Fe and the scanning transmission electron microscopy analysis revealed that the Fe oxides were reduced and became dispersed under anaerobic conditions, whereas they were oxidized and re-aggregated during the aerobic stage. In addition, the redox processes of sulfur and nitrogen were detected under both anaerobic and aerobic conditions. Based on these observations, a simplified kinetic model was established to distinguish the relative contributions of the transformation processes. The bioavailability of Sb was controlled by immobilization as a result of S reduction and by mobilization as a result of Fe reductive dissolution and S oxidation, rather than the pH. These processes coupled with the redox reaction of Sb jointly resulted in the complex behavior of Sb transformation under anaerobic and aerobic conditions. The model-based method and findings of this study provide a comprehensive understanding of the Sb transformation in a complex soil biogeochemical system under changing redox conditions.
虽然之前已经研究了锑(Sb)在稻田土壤中的转化,但土壤中高化学活性 Sb 的生物地球化学过程仍知之甚少。此外,对土壤中 Sb 转化的定量理解也很缺乏。因此,在这项研究中,在厌氧和好氧培养条件下研究了外源 Sb 在稻田土壤中的动力学。在厌氧条件下,溶解的 Sb(V) 和扩散梯度技术提取的 Sb(V) 减少,然后在好氧条件下增加。发生了 Sb 的氧化还原反应,在培养 55 天后 Sb 的生物利用度显著降低。Fe 的动力学和扫描透射电子显微镜分析表明,Fe 氧化物在厌氧条件下被还原并分散,而在好氧阶段则被氧化并重新聚集。此外,在厌氧和好氧条件下都检测到了硫和氮的氧化还原过程。基于这些观察,建立了一个简化的动力学模型来区分转化过程的相对贡献。Sb 的生物利用度受 S 还原导致的固定和 Fe 还原溶解和 S 氧化导致的移动的控制,而不是 pH 值。这些过程与 Sb 的氧化还原反应共同导致了厌氧和好氧条件下 Sb 转化的复杂行为。本研究基于模型的方法和结果提供了对复杂土壤生物地球化学系统中 Sb 在不断变化的氧化还原条件下转化的综合理解。