3 research outputs found

    Enhancement of Arsenic Adsorption during Mineral Transformation from Siderite to Goethite: Mechanism and Application

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    Synthesized siderite was used to remove AsĀ­(III) and AsĀ­(V) from water solutions under anoxic conditions and oxic conditions. Results showed that As adsorption on synthetic siderite under anoxic conditions was around 10 mg/g calculated with Langmuir isotherm. However, the calculated As adsorption on synthetic siderite under oxic conditions ranged between 115 and 121 mg/g, which was around 11 times higher than that under anoxic conditions. It was found that 75% siderite was transformed into goethite during oxic adsorption. However, synthetic goethite had lower As adsorption capacity than siderite under oxic conditions, although its adsorption capacity was a little higher than siderite under anoxic conditions. It suggested that the coexistence of goethite and siderite bimineral during mineral transformation probably contributed to the robust adsorption capacity of siderite under oxic conditions. Results of extended X-ray absorption fine structure (EXAF) spectroscopy indicated both AsĀ­(III) and AsĀ­(V) formed inner-sphere complexes on the surface of As-treated solid regardless of substrates, including the bidentate binuclear corner-sharing (<sup>2</sup>C) complexes and the monodentate mononuclear corner-sharing (<sup>1</sup>V) complexes. Monodenate (<sup>1</sup>V) and bidentate (<sup>2</sup>C) complexes would be related to high As adsorption capacity of siderite under oxic conditions. It showed that more Fe atoms were coordinated with As atom in the monodentate complexes and the bidentate complexes of AsĀ­(V)/AsĀ­(III)-treated siderite under oxic conditions, in comparison with AsĀ­(V)/AsĀ­(III)-treated siderite under anoxic conditions and AsĀ­(V)/AsĀ­(III)-treated goethite. Calcinations of natural siderite resulting in the coexistence of goethite and siderite greatly increased As adsorption on the solid, which confirmed that the coexistence of bimineral during mineral transformation from siderite to goethite greatly enhanced As adsorption capacity of siderite adsorbent. The observation can be applied for modification of natural siderite for As removal from high As waters

    Stimulation of Fe(II) Oxidation, Biogenic Lepidocrocite Formation, and Arsenic Immobilization by <i>Pseudogulbenkiania</i> Sp. Strain 2002

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    An anaerobic nitrate-reducing FeĀ­(II)-oxidizing bacterium, <i>Pseudogulbenkiania</i> sp. strain 2002, was used to investigate As immobilization by biogenic Fe oxyhydroxides under different initial molar ratios of Fe/As in solutions. Results showed that FeĀ­(II) was effectively oxidized, mainly forming lepidocrocite, which immobilized more AsĀ­(III) than AsĀ­(V) without changing the redox state of As. When the initial Fe/As ratios were kept constant, higher initial FeĀ­(II) concentrations immobilized more As with higher As<sub>immobilized</sub>/Fe<sub>precipitated</sub> in biogenic lepidocrocite. EXAFS analysis showed that variations of initial FeĀ­(II) concentrations did not change the Asā€“Fe complexes (bidentate binuclear complexes (<sup>2</sup><i>C</i>)) with a fixed AsĀ­(III) or AsĀ­(V) initial concentration of 13.3 Ī¼M. On the other hand, variations in initial As concentrations but fixed FeĀ­(II) initial concentration induced the co-occurrence of bidentate binuclear and bidentate mononuclear complexes (<sup>2</sup><i>E</i>) and bidentate binuclear and monodentate mononuclear complexes (<sup>1</sup><i>V</i>) for AsĀ­(III) and AsĀ­(V)-treated series, respectively. The coexistence of <sup>2</sup><i>C</i> and <sup>2</sup><i>E</i> complexes (or <sup>2</sup><i>C</i> and <sup>1</sup><i>V</i> complexes) could contribute to higher As removal in experimental series with higher initial FeĀ­(II) concentrations at the same initial Fe/As ratio. Simultaneous removal of soluble As and nitrate by anaerobic nitrate-reducing FeĀ­(II)-oxidizing bacteria provides a feasible approach for in situ remediation of As-nitrate cocontaminated groundwater

    Sulfur Cycling-Related Biogeochemical Processes of Arsenic Mobilization in the Western Hetao Basin, China: Evidence from Multiple Isotope Approaches

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    The role of sulfur cycling in arsenic behavior under reducing conditions is not well-understood in previous investigations. This study provides observations of sulfur and oxygen isotope fractionation in sulfate and evaluation of sulfur cycling-related biogeochemical processes controlling dissolved arsenic groundwater concentrations using multiple isotope approaches. As a typical basin hosting high arsenic groundwater, the western Hetao basin was selected as the study area. Results showed that, along the groundwater flow paths, groundwater Ī“<sup>34</sup>S<sub>SO4</sub>, Ī“<sup>18</sup>O<sub>SO4</sub>, and Ī“<sup>13</sup>C<sub>DOC</sub> increased with increases in arsenic, dissolved iron, hydrogen sulfide and ammonium concentrations, while Ī“<sup>13</sup>C<sub>DIC</sub> decreased with decreasing Eh and sulfate/chloride. Bacterial sulfate reduction (BSR) was responsible for many of these observed changes. The Ī“<sup>34</sup>S<sub>SO4</sub> indicated that dissolved sulfate was mainly sourced from oxidative weathering of sulfides in upgradient alluvial fans. The high oxygenā€“sulfur isotope fractionation ratio (0.60) may result from both slow sulfate reduction rates and bacterial disproportionation of sulfur intermediates (BDSI). Data indicate that both the sulfide produced by BSR and the overall BDSI reduce arsenic-bearing ironĀ­(III) oxyhydroxides, leading to the release of arsenic into groundwater. These results suggest that sulfur-related biogeochemical processes are important in mobilizing arsenic in aquifer systems
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