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Comparing Schwertmannite and Hydrobasaluminite Dissolution in Ammonium Oxalate (pH 3.0): Implications for Metal Speciation Studies by Sequential Extraction

机译:比较Schwertmannite和Hydrobasaluminite在草酸铵(pH 3.0)中的溶解度:通过顺序萃取对金属形态研究的意义

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The “poorly crystalline iron oxy-hydroxides” are one of the most reactive and environmentally important fractions in soils and sediments due to the association of many toxic elements associated with these minerals. The metal content of this fraction in sequential extraction procedures is usually evaluated by dissolution in ammonium oxalate ([NH 4 ] 2 C 2 O 4 ·H 2 O) at pH 3.0 and 25 °C. Such chemical treatment, however, may also dissolve other mineral phases of comparable reactivity, which can lead to wrong interpretations of mineral carriers for specific metals. In this study, we compare the dissolution kinetics of schwertmannite and hydrobasaluminite, two minerals of comparable crystallinity and reactivity that play a major role in the mobility of many trace metals in waters and sediments affected by acid mine drainage (AMD). We first synthesized these two minerals in the laboratory by partial neutralization of two different metal-rich mine waters, and then we applied the standard protocol of ammonium oxalate dissolution to different specimens; the solutions were periodically sampled at intervals of 2, 5, 10, 15, 30 and 60 min to compare (i) the kinetics of mineral dissolution, and (ii) the metals released during dissolution of these two minerals. The results indicate a very similar kinetics of mineral dissolution, though hydrobasaluminite exhibited a faster rate. Some toxic elements such as As, Cr or V were clearly bonded to schwertmannite, while many others such as Cu, Zn, Si, Co, Ni and Y were clearly linked to hydrobasaluminite. These results suggest that studies linking the mobility of many elements with the Fe cycle in AMD-affected soils and sediments could be inaccurate, since these elements could actually be associated with Al minerals of poor crystallinity. The step of ammonium oxalate dissolution in sequential extraction studies should be best described with a more general term such as “low-crystallinity oxy-hydroxides”.
机译:由于与这些矿物相关的许多有毒元素的结合,“结晶性较弱的羟基氧化铁”是土壤和沉积物中最具反应性和环境重要性的组分之一。通常通过在pH 3.0和25°C的草酸铵([NH 4] 2 C 2 O 4·H 2 O)中溶解来评估顺序萃取过程中该馏分的金属含量。然而,这种化学处理也可能溶解反应性相当的其他矿物相,这可能导致对特定金属的矿物载体的错误解释。在这项研究中,我们比较了Schwertmannite和Hydrobasaluminite的溶解动力学,这两种具有可比的结晶度和反应活性的矿物在受酸性矿山排水(AMD)影响的水和沉积物中许多微量金属的迁移中起主要作用。我们首先在实验室中通过部分中和两种不同的富含金属的矿泉水来合成这两种矿物,然后将草酸铵溶解的标准方案应用于不同的标本。定期以2、5、10、15、30和60分钟的间隔对溶液进行采样,以比较(i)矿物溶解的动力学和(ii)两种矿物溶解过程中释放的金属。结果表明,矿物溶解的动力学非常相似,尽管氢硅铝石显示出更快的速率。某些有毒元素(例如As,Cr或V)清楚地与Schwertmannite结合,而其他许多有毒元素(例如Cu,Zn,Si,Co,Ni和Y)清楚地与水铝矾石相连。这些结果表明,将许多元素的迁移率与受AMD影响的土壤和沉积物中的铁循环联系起来的研究可能是不准确的,因为这些元素实际上可能与结晶度较差的Al矿物有关。在顺序萃取研究中草酸铵溶解的步骤应以更通用的术语(例如“低结晶度的羟基氧化物”)来最好地描述。

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