Cr release from Cr-substituted goethite during the aqueous Fe(II)-induced recrystallization

Jian Hua, Manjia Chen, Chengshuai Liu, Fangbai Li, Jian Long, Ting Gao, Fei Wu, Jing Lei, Minghua Gu
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Abstract

The interaction between aqueous Fe(II) (Fe(II)aq) and iron minerals is an important reaction of the iron cycle, and it plays a critical role in impacting the environmental behavior of heavy metals in soils. Metal substitution into iron (hydr)oxides has been reported to reduce Fe atom exchange rates between Fe(II)aq and metal-substituted iron (hydr)oxides and inhibit the recrystallization of iron (hydr)oxides. However, the environmental behaviors of the substituted metal during these processes remain unclear. In this study, Fe(II)aq-induced recrystallization of Cr-substituted goethite (Cr-goethite) was investigated, along with the sequential release behavior of substituted Cr(III). Results from a stable Fe isotopic tracer and Mossbauer characterization studies show that Fe atom exchange occurred between Fe(II)aq and structural Fe(III) (Fe(III)oxide) in Cr-goethites, during which the Cr-goethites were recrystallized. The Cr substitution inhibited the rates of Fe atom exchange and Cr-goethite recrystallization. During the recrystallization of Cr-goethites induced by Fe(II)aq, Cr(III) was released from Cr-goethite. In addition, Cr-goethites with a higher level of Cr-substituted content released more Cr(III). The highest Fe atom exchange rate and the highest amount of released Cr(III) were observed at a pH of 7.5. Under reaction conditions involving a lower pH of 5.5 or a higher pH of 8.5, there were substantially lower rates of Fe atom exchange and Cr(III) release. This trend of Cr(III) release was similar with changes in Fe atom exchange, suggesting that Cr(III) release is driven by Fe atom exchange. The release and reincorporation of Cr(III) occurred simultaneously during the Fe(II)aq-induced recrystallization of Cr-goethites, especially during the late stage of the observed reactions. Our findings emphasize an important role for Fe(II)aq-induced recrystallization of iron minerals in changing soil metal characteristics, which is critical for the evaluation of soil metal activities, especially those in Fe-rich soils.
水Fe(II)诱导再结晶过程中Cr取代针铁矿的Cr释放
水中Fe(II) (Fe(II)aq)与铁矿物的相互作用是铁循环的一个重要反应,对影响土壤中重金属的环境行为起着关键作用。据报道,金属取代成铁(水合)氧化物可以降低铁(II)aq和金属取代的铁(水合)氧化物之间的铁原子交换速率,抑制铁(水合)氧化物的再结晶。然而,在这些过程中,替代金属的环境行为尚不清楚。在本研究中,研究了Fe(II)aq诱导的Cr-取代针铁矿(Cr-goethite)的再结晶,以及取代Cr(III)的顺序释放行为。稳定铁同位素示踪和穆斯堡尔表征结果表明,铁(II)aq和结构铁(III) (Fe(III)氧化物)之间发生了铁原子交换,在此过程中,cr -针铁矿发生了再结晶。Cr取代抑制了Fe原子交换速率和Cr-针铁矿再结晶速率。在Fe(II)aq诱导的Cr针铁矿再结晶过程中,Cr(III)从Cr针铁矿中释放出来。此外,Cr-取代含量越高的Cr-针铁矿释放出的Cr(III)越多。pH为7.5时,铁原子交换率最高,Cr(III)释放量最大。在较低pH为5.5或较高pH为8.5的反应条件下,Fe原子交换速率和Cr(III)释放速率显著降低。Cr(III)的释放趋势与Fe原子交换的变化趋势相似,表明Cr(III)的释放是由Fe原子交换驱动的。在Fe(II)aq诱导的Cr-针铁矿再结晶过程中,Cr(III)的释放和再合并同时发生,特别是在观察到的反应后期。我们的研究结果强调了铁(II)aq诱导的铁矿物再结晶在改变土壤金属特征中的重要作用,这对于评价土壤金属活性,特别是富铁土壤中的土壤金属活性至关重要。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
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