Johnson Clayton R, Antonopoulos Dionysios A, Boyanov Maxim I, Flynn Theodore M, Koval Jason C, Kemner Kenneth M, O'Loughlin Edward J
Biosciences Division, Argonne National Laboratory, Lemont, IL 60439-4843.
Bulgarian Academy of Sciences, Institute of Chemical Engineering, Sofia, 1113, Bulgaria.
Heliyon. 2021 Feb 26;7(2):e06275. doi: 10.1016/j.heliyon.2021.e06275. eCollection 2021 Feb.
Increasing use and mining of antimony (Sb) has resulted in greater concern involving its fate and transport in the environment. Antimony(V) and (III) are the two most environmentally relevant oxidation states, but little is known about the redox transitions between the two in natural systems. To better understand the behavior of antimony in anoxic environments, the redox transformations of Sb(V) were studied in biotic and abiotic reactors. The biotic reactors contained Sb(V) (2 mM as KSb(OH)), ferrihydrite (50 mM Fe(III)), sulfate (10 mM), and lactate (10 mM), that were inoculated with sediment from a wetland. In the abiotic reactors, The interaction of Sb(V) with green rust, magnetite, siderite, vivianite or mackinawite was examined under abiotic conditions. Changes in the concentrations of Sb, Fe(II), sulfate, and lactate, as well as the microbial community composition were monitored over time. Lactate was rapidly fermented to acetate and propionate in the bioreactors, with the latter serving as the primary electron donor for dissimilatory sulfate reduction (DSR). The reduction of ferrihydrite was primarily abiotic, being driven by biogenic sulfide. Sb and Fe K-edge X-ray absorption near edge structure (XANES) analysis showed reduction of Sb(V) to Sb(III) within 4 weeks, concurrent with DSR and the formation of FeS. Sb K-edge extended X-ray absorption fine structure (EXAFS) spectroscopy analysis indicated that the reduced phase was a mixture of S- and O-coordinated Sb(III). Reduction of Sb(V) was not observed in the presence of magnetite, siderite, or green rust, and limited reduction occurred with vivianite. However, reduction of Sb(V) to amorphous Sb(III) sulfide occurred with mackinawite. These results are consistent with abiotic reduction of Sb(V) by biogenic sulfide and reveal a substantial influence of Fe oxides on the speciation of Sb(III), which illustrates the tight coupling of Sb speciation with the biogeochemical cycling of S and Fe.
锑(Sb)使用和开采量的增加,引发了人们对其在环境中归宿和迁移的更多关注。五价锑和三价锑是与环境最相关的两种氧化态,但对于自然系统中两者之间的氧化还原转变却知之甚少。为了更好地理解锑在缺氧环境中的行为,研究了生物和非生物反应器中五价锑的氧化还原转化。生物反应器中含有五价锑(以KSb(OH)计为2 mM)、水铁矿(50 mM Fe(III))、硫酸盐(10 mM)和乳酸盐(10 mM),并接种了湿地沉积物。在非生物反应器中,研究了五价锑在非生物条件下与绿锈、磁铁矿、菱铁矿、蓝铁矿或马基诺矿的相互作用。随着时间的推移,监测了锑、亚铁、硫酸盐和乳酸盐浓度的变化以及微生物群落组成。乳酸盐在生物反应器中迅速发酵为乙酸盐和丙酸盐,后者作为异化硫酸盐还原(DSR)的主要电子供体。水铁矿的还原主要是非生物过程,由生物成因硫化物驱动。锑和铁的K边X射线吸收近边结构(XANES)分析表明,在4周内五价锑还原为三价锑,同时伴随着DSR和FeS的形成。锑的K边扩展X射线吸收精细结构(EXAFS)光谱分析表明,还原相是S配位和O配位的三价锑的混合物。在磁铁矿、菱铁矿或绿锈存在的情况下未观察到五价锑的还原,蓝铁矿的还原作用有限。然而,马基诺矿可将五价锑还原为无定形三价硫化锑。这些结果与生物成因硫化物对五价锑的非生物还原一致,并揭示了铁氧化物对三价锑形态的重大影响,这说明了锑形态与硫和铁的生物地球化学循环紧密耦合。