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铁还原对砷保留的混杂影响。

Confounding impacts of iron reduction on arsenic retention.

作者信息

Tufano Katharine J, Fendorf Scott

机构信息

School of Earth Sciences, Stanford University, Stanford, California 94305, USA.

出版信息

Environ Sci Technol. 2008 Jul 1;42(13):4777-83. doi: 10.1021/es702625e.

Abstract

A transition from oxidizing to reducing conditions has long been implicated to increase aqueous As concentrations, for which reductive dissolution of iron (hydr)oxides is commonly implicated as the primary culprit. Confounding our understanding of processes controlling As retention, however, is that reductive transformation of ferrihydrite has recently been shown to promote As retention rather than release. To resolve the role iron phases have in regulating arsenic concentrations, here we examine As desorption from ferrihydrite-coated sands presorbed with As(III); experiments were performed at circumneutral pH under Fe-reducing conditions with the dissimilatory iron reducing bacterium Shewanella putrefaciens strain CN-32 over extended time periods. We reveal that with the initial phase of iron reduction, ferrihydrite undergoes transformation to secondary phases and increases As(III) retention (relative to abiotic controls). However, with increased reaction time, cessation of the phase transitions and ensuing reductive dissolution result in prolonged release of As(III) to the aqueous phase. Our results suggest that As(III) retention during iron reduction is temporally dependent on secondary precipitation of iron phases; during transformation to secondary phases, particularly magnetite, As(III) retention is enhanced even relative to oxidized systems. However, conditions that retard secondary transformation (more stable iron oxides or limited iron reducing bacterial activity), or prolonged anaerobiosis, will lead to both the dissolution of ferric (hydr)oxides and release of As(III) to the aqueous phase.

摘要

长期以来,氧化条件向还原条件的转变一直被认为会增加水中砷的浓度,其中铁(氢)氧化物的还原溶解通常被认为是主要原因。然而,使我们对控制砷保留过程的理解变得复杂的是,最近研究表明水铁矿的还原转化会促进砷的保留而不是释放。为了确定铁相在调节砷浓度中所起的作用,我们在此研究了预先吸附了As(III)的水铁矿包覆砂中砷的解吸情况;实验是在中性pH值、铁还原条件下,使用异化铁还原细菌腐败希瓦氏菌菌株CN-32在较长时间内进行的。我们发现,在铁还原的初始阶段,水铁矿会转化为次生相并增加As(III)的保留量(相对于非生物对照)。然而,随着反应时间的增加,相变停止以及随之而来的还原溶解导致As(III)向水相的长时间释放。我们的结果表明,铁还原过程中As(III)的保留在时间上取决于铁相的次生沉淀;在向次生相,特别是磁铁矿转化的过程中,即使相对于氧化体系,As(III)的保留也会增强。然而,阻碍次生转化的条件(更稳定的铁氧化物或有限的铁还原细菌活性)或长时间的厌氧状态,将导致铁(氢)氧化物的溶解以及As(III)向水相的释放。

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