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氯离子和二价铁含量对磁铁矿还原汞(II)的影响。

Influence of chloride and Fe(II) content on the reduction of Hg(II) by magnetite.

机构信息

Department of Civil and Environmental Engineering, The University of Iowa, Iowa City, Iowa 52242, United States.

出版信息

Environ Sci Technol. 2013 Jul 2;47(13):6987-94. doi: 10.1021/es304761u. Epub 2013 Apr 26.

Abstract

Abiotic reduction of inorganic mercury by natural organic matter and native soils is well-known, and recently there is evidence that reduced iron (Fe) species, such as magnetite, green rust, and Fe sulfides, can also reduce Hg(II). Here, we evaluated the reduction of Hg(II) by magnetites with varying Fe(II) content in both the absence and presence of chloride. Specifically, we evaluated whether magnetite stoichiometry (x = Fe(II)/Fe(III)) influences the rate of Hg(II) reduction and formation of products. In the absence of chloride, reduction of Hg(II) to Hg(0) is observed over a range of magnetite stoichiometries (0.29 < x < 0.50) in purged headspace reactors and unpurged low headspace reactors, as evidenced by Hg recovery in a volatile product trap solution and Hg L(III)-edge X-ray absorption near edge spectroscopy (XANES). In the presence of chloride, however, XANES spectra indicate the formation of a metastable Hg(I) calomel species (Hg2Cl2) from the reduction of Hg(II). Interestingly, Hg(I) species are only observed for the more oxidized magnetite particles that contain lower Fe(II) content (x < 0.42). For the more reduced magnetite particles (x ≥ 0.42), Hg(II) is reduced to Hg(0) even in the presence of high chloride concentrations. As previously observed for nitroaromatic compounds and uranium, magnetite stoichiometry appears to influence the rate of Hg(II) reduction (both in the presence and absence of chloride) confirming that it is important to consider magnetite stoichiometry when assessing the fate of contaminants in Fe-rich subsurface environments.

摘要

无机汞的非生物还原由天然有机质和原生土壤是众所周知的,最近有证据表明,还原态铁(Fe)物种,如磁铁矿、绿锈和 Fe 硫化物,也可以还原 Hg(II)。在这里,我们评估了在没有和存在氯化物的情况下,具有不同 Fe(II)含量的磁铁矿对 Hg(II)的还原作用。具体来说,我们评估了磁铁矿化学计量(x = Fe(II)/Fe(III))是否会影响 Hg(II)还原的速率和产物的形成。在没有氯化物的情况下,Hg(II)在吹扫顶空反应器和未吹扫低顶空反应器中,在一系列磁铁矿化学计量范围内(0.29 < x < 0.50)被还原为 Hg(0),这一点从挥发性产物捕集溶液中 Hg 的回收和 Hg L(III)-边 X 射线吸收近边光谱(XANES)中得到证实。然而,在存在氯化物的情况下,XANES 谱表明,Hg(II)被还原为不稳定的 Hg(I)甘汞物种(Hg2Cl2)。有趣的是,仅观察到更氧化的磁铁矿颗粒(含较低的 Fe(II)含量(x < 0.42))形成 Hg(I)物种。对于更还原的磁铁矿颗粒(x ≥ 0.42),即使在高氯化物浓度存在的情况下,Hg(II)也被还原为 Hg(0)。与先前观察到的硝基芳香族化合物和铀一样,磁铁矿化学计量似乎会影响 Hg(II)还原的速率(在存在和不存在氯化物的情况下),这证实了在评估富含铁的地下环境中污染物的命运时,考虑磁铁矿化学计量是很重要的。

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