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首页> 外文期刊>Geochimica et Cosmochimica Acta: Journal of the Geochemical Society and the Meteoritical Society >Effect of arsenic concentration on microbial iron reductionand arsenic speciation in an iron-rich freshwater sediment
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Effect of arsenic concentration on microbial iron reductionand arsenic speciation in an iron-rich freshwater sediment

机译:砷浓度对富铁淡水沉积物中微生物铁还原和砷形态的影响

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摘要

Depth profiles in the sediment porewaters of the Chattahoochee River (Georgia, USA) show that iron oxides scavengearsenate in the water column and settle to the sediment—water interface (SWI) where they are reduced by iron-reducing bac-teria. During their reduction, these particles seem to release arsenic to the porewaters in the form of arsenate only. Sedimentslurry incubations were conducted to determine the effect of low concentrations of arsenic (iu10μM) on biogeochemical pro-cesses in these sediments. Experiments confirm that any arsenate (As(V)) added to these sediments is immediately adsorbed inoxic conditions and released in anoxic conditions during the microbial reduction of authigenic iron oxides. Incubations in thepresence ofiu 1 μMAs(V) reveal that arsenate is released but not concomitantly reduced during this process. Simultaneously,microbial iron reduction is enhanced significantly, spurring the simultaneous release of arsenate into porewaters and second- ary formation of crystalline iron oxides. Above 1 As(V), however, the microbial reductive dissolution of iron oxidesappears inhibited by arsenate, and arsenite is produced in excess in the porewaters. These incubations show that even lowinputs of arsenic to riverine sediments may affect microbial processes, the stability of iron oxides and, indirectly, the cyclingof arsenic. Possible mechanisms for such effects on iron reduction are proposed.
机译:查塔胡奇河(美国乔治亚州)的沉积物孔隙水中的深度剖面表明,氧化铁在水柱中清除并沉淀到沉积物-水界面(SWI),并通过还原铁细菌将其还原。在还原过程中,这些颗粒似乎仅以砷酸盐的形式将砷释放到孔隙水中。进行了泥浆培养,以确定低浓度砷(iu10μM)对这些沉积物中生物地球化学过程的影响。实验证实,添加到这些沉积物中的任何砷酸盐(As(V))都将在低氧条件下立即吸附,并在自生氧化铁的微生物还原过程中在低氧条件下释放。存在1μMAs(V)时的孵育表明,在此过程中释放了砷酸盐,但并未随之减少。同时,微生物中铁的还原显着增强,促使砷酸盐同时释放到孔隙水中并二次形成结晶氧化铁。但是,高于1 As(V)时,氧化铁的微生物还原性溶解会受到砷酸盐的抑制,并且在孔隙水中会过量生成砷酸盐。这些温育表明,即使向河流沉积物中的砷输入很少,也可能影响微生物过程,铁氧化物的稳定性,并间接影响砷的循环。提出了影响铁还原的可能机制。

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