School of Environment and Energy, South China University of Technology, Guangzhou, 510006, People's Republic of China.
The Key Laboratory of Pollution Control and Ecosystem Restoration in Industry Clusters, Ministry of Education, South China University of Technology, Guangzhou, 510006, People's Republic of China.
Environ Sci Pollut Res Int. 2019 Jan;26(1):617-627. doi: 10.1007/s11356-018-3441-9. Epub 2018 Nov 8.
Schwertmannite is an important sink for cadmium (Cd) in acid mine drainage (AMD) environments and is unstable when environmental conditions change. However, the release and redistribution of Cd during schwertmannite transformation with respect to pre-bound Cd are poorly understood. In this work, the transformation of cadmium-associated schwertmannite and subsequent Cd repartitioning behaviors were investigated. The way of schwertmannite associated with Cd was predominant by absorption, and the diffuse layer model (DLM) showed that Cd existed as monodentate complexes ≡FeOCd and ≡FeOCd on schwertmannite surfaces. Kinetics of SO release and mineralogical characterization both showed that the mineral transformation rates decreased and more lepidocrocite aggregated with increasing adsorbed Cd levels. The shrinking core model revealed that Fe(II)-induced process would affect mineral dissolution by changing surface reaction-controlled step to internal diffusion-controlled step, and significantly promote the dissolution rate of Cd-adsorbed schwertmannite. Adsorbed Cd blocked the surface sites for later Fe(II) adsorption and the Fe(II)-Fe(III) electron transfer, then resulted in the decelerated transformation and the accumulation of intermediate phase lepidocrocite. The maximum release of aqueous Cd occurred after 1 mM Fe addition, then over 69% of initial added Cd re-bound to solid-phase accompanying with mineral transformation, and finally, Cd was mainly associated with the secondary minerals by complexation with surficial OH groups. These findings are useful for developing the strategies for treating Cd contamination in AMD affected areas.
纤铁矿是酸性矿山排水(AMD)环境中镉(Cd)的重要汇,并且当环境条件发生变化时不稳定。然而,对于与预结合 Cd 有关的纤铁矿转化过程中 Cd 的释放和再分配仍了解甚少。在这项工作中,研究了与 Cd 相关的纤铁矿的转化以及随后 Cd 的再分配行为。Cd 与纤铁矿结合的方式主要是通过吸附,扩散层模型(DLM)表明 Cd 以单齿络合物≡FeOCd 和≡FeOCd 的形式存在于纤铁矿表面。SO42-的释放动力学和矿物学特征均表明,随着吸附 Cd 水平的增加,矿物转化速率降低,并且更多的水铁矿聚集。收缩核模型表明,Fe(II)诱导的过程会通过改变表面反应控制步骤为内部扩散控制步骤来影响矿物溶解,并显著促进吸附 Cd 的纤铁矿的溶解速率。吸附 Cd 会阻止表面的 Fe(II)吸附和 Fe(II)-Fe(III)电子转移的位点,从而导致转化速度减慢和中间相水铁矿的积累。在添加 1mM Fe 后,水溶液中 Cd 的最大释放量发生,然后超过 69%的初始添加 Cd 与矿物转化一起重新结合到固相上,最终 Cd 主要通过与表面 OH 基团的络合与次生矿物结合。这些发现有助于制定处理 AMD 影响区 Cd 污染的策略。