Abstract

Fe(II)-bearing minerals (magnetite, siderite, green rust, etc.) are common products of microbial Fe(III) reduction, and they provide a reservoir of reducing capacity in many subsurface environments that may contribute to the reduction of redox active elements such as vanadium; which can exist as V(V), V(IV), and V(III) under conditions typical of near-surface aquatic and terrestrial environments. To better understand the redox behavior of V under ferrugenic/sulfidogenic conditions, we examined the interactions of V(V) (1 mM) in aqueous suspensions containing 50 mM Fe(II) as magnetite, siderite, vivianite, green rust, or mackinawite, using X-ray absorption spectroscopy at the V K-edge to determine the valence state of V. Two additional systems of increased complexity were also examined, containing either 60 mM Fe(II) as biogenic green rust (BioGR) or 40 mM Fe(II) as a mixture of biogenic siderite, mackinawite, and magnetite (BioSMM). Within 48 h, total solution-phase V concentrations decreased to <20 µM in all but the vivianite and the biogenic BiSMM systems; however, >99.5% of V was removed from solution in the BioSMM and vivianite systems within 7 and 20 months, respectively. The most rapid reduction was observed in the mackinawite system, where V(V) was reduced to V(III) within 48 h. Complete reduction of V(V) to V(III) occurred within 4 months in the green rust system, 7 months in the siderite system, and 20 months in the BioGR system. Vanadium(V) was only partially reduced in the magnetite, vivianite, and BioSMM systems, where within 7 months the average V valence state stabilized at 3.7, 3.7, and 3.4, respectively. The reduction of V(V) in soils and sediments has been largely attributed to microbial activity, presumably involving direct enzymatic reduction of V(V); however the reduction of V(V) by Fe(II)-bearing minerals suggests that abiotic or coupled biotic–abiotic processes may also play a critical role in V redox chemistry, and thus need to be considered in modeling the global biogeochemical cycling of V.

Highlights

  • Vanadium (V) is a Group 5 transition metal found in a variety of aquatic and terrestrial environments [1,2,3,4,5] and is a relatively abundant trace metal (e.g., an average of 97 mg kg−1 within the Earth’s crust [6]; from

  • To better understand the redox behavior of V under ferrugenic/sulfidogenic conditions, we examined the interactions of V(V) (1 mM) in aqueous suspensions containing 50 mM Fe(II) as magnetite, siderite, vivianite, green rust, or mackinawite, and two additional systems containing either 60 mM Fe(II) as biogenic green rust or 40 mM Fe(II) as a mixture of biogenic siderite, mackinawite, and magnetite, using X-ray absorption spectroscopy to determine changes in the valence state of V

  • A mixed phase suspension containing biogenic siderite, mackinawite, and magnetite (BioSMM; each phase is 52, 26, and 22 mol% Fe, respectively, as determined by Fe X-ray absorption near edge spectra (XANES) analysis) was formed during the bioreduction of 50 mM Fe(III) as ferrihydrite in a system containing 10 mM sulfate that was inoculated with wetland sediment

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Summary

Introduction

Vanadium (V) is a Group 5 transition metal found in a variety of aquatic and terrestrial environments [1,2,3,4,5] and is a relatively abundant trace metal (e.g., an average of 97 mg kg−1 within the Earth’s crust [6]; from

Fe Minerals
Experimental Setup
X-ray Absorption Spectroscopy Analysis
V Standards
Findings
Environmental Implications
Full Text
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