School of Environment and Energy, South China University of Technology, Guangzhou 510006, China.
School of Environment and Energy, South China University of Technology, Guangzhou 510006, China; The Key Laboratory of Pollution Control and Ecosystem Restoration in Industry Clusters, Ministry of Education, Guangzhou 510006, China.
J Environ Sci (China). 2019 Jun;80:218-228. doi: 10.1016/j.jes.2018.12.015. Epub 2018 Dec 29.
Schwertmannite is an amorphous iron(III)-oxyhydroxysulfate that forms in acid mine drainage (AMD) environments. The characteristic of high heavy metal adsorption capability makes schwertmannite a potentially useful, environmentally friendly material in wastewater treatment. Unstable schwertmannite is prone to recrystallization. Understanding the mechanisms that induce schwertmannite labilization and affect its capacity to remove heavy metals are of great environmental and geochemical significance. Thiocyanate (SCN¯) is a hazardous pseudohalide that is also normally found in AMD. However, little is known about the impact of Fe(III)-binding ligand SCN¯ on schwertmannite stability and its subsequent capacity to bind trace elements. Here, we investigated the adsorption of SCN¯ on schwertmannite and subsequent mineral transformation to characterize this little-known process. The appearance of Fe indicated that the interactions between schwertmannite and SCN¯ may involve complexation and reduction reactions. Results showed that the majority of the adsorbed-SCN¯ was immobilized on schwertmannite during the 60-days transformation. The transformation rates of schwertmannite increased with increasing concentrations of SCN¯. Goethite was detected as the dominant transformation product with or without SCN¯. The mechanisms of SCN¯-promoted dissolution of schwertmannite can be described as follows: (1) formation of Fe(III)-NCS complexes on the schwertmannite surface and in solution, a process which increases the reactivity of solid phase Fe(III); (2) the extraction of Fe(III) from schwertmannite by SCN¯ and subsequent schwertmannite dissolution; and (3) the formation of secondary minerals from extracted Fe(III). These findings may improve AMD treatment strategies and provide insight into the use and potential reuse of schwertmannite as a trace element sorbent.
纤铁矿是一种在酸性矿山排水 (AMD) 环境中形成的无定形三价铁-氧羟硫酸盐。其高重金属吸附能力的特点使其成为废水处理中一种潜在有用的环保材料。不稳定的纤铁矿容易重结晶。了解诱导纤铁矿不稳定的机制及其对去除重金属能力的影响,具有重要的环境和地球化学意义。硫氰酸根 (SCN¯) 是一种危险的类卤化物,通常也存在于 AMD 中。然而,人们对 Fe(III)结合配体 SCN¯对纤铁矿稳定性及其随后结合痕量元素能力的影响知之甚少。在这里,我们研究了 SCN¯在纤铁矿上的吸附及其随后的矿物转化,以表征这一鲜为人知的过程。Fe 的出现表明纤铁矿和 SCN¯之间的相互作用可能涉及络合和还原反应。结果表明,在 60 天的转化过程中,大部分吸附的 SCN¯被固定在纤铁矿上。随着 SCN¯浓度的增加,纤铁矿的转化速率增加。有无 SCN¯存在时,都检测到针铁矿是主要的转化产物。SCN¯促进纤铁矿溶解的机制可以描述如下:(1)在纤铁矿表面和溶液中形成 Fe(III)-NCS 络合物,这一过程增加了固相 Fe(III)的反应性;(2)SCN¯从纤铁矿中提取 Fe(III),随后纤铁矿溶解;(3)从提取的 Fe(III)形成次生矿物。这些发现可能会改善 AMD 处理策略,并深入了解将纤铁矿用作痕量元素吸附剂的使用和潜在再利用。