Green rusts, ferrous-ferric iron oxides, occur in many anaerobic soils and sediments and are highly reactive, making them important phases impacting the fate and transport of environmental contaminants. Despite their potential importance in environmental settings, reactions involving green rusts remain rather poorly described. Chromate is a widespread contaminant having deleterious impacts on plant and animal health; its fate may in part be controlled by green rust. Here we examine chromate reduction by a series of green rust phases and resolve the reaction kinetics at pH 7. The overall kinetics of the reactions are well described by the expression dCr(VI)/dt = -kCr(VI){GR}, and this model was successfully used to predict rates of reaction at varying chromium concentrations. The rates of reduction are controlled by the concentration of ferrous iron, surface area, and chemical structure of the green rust including layer spacing. On a mass basis, green rust (GR) chloride is the most rapid reductant of Cr(VI) followed by GRCO{sub}3 and GRSO{sub}4, with pseudo-first-order rate coefficients (k{sub}(obs)) (with respect to Cr(VI) concentration) ranging from 1.22 × 10{sup}(-3) to 3.7 × 10{sup}(-2) s{sup}(-1). Chromium(III)-substituted magnetite and lepidocrocite were identified as the major oxidation products. The nature of the oxidation products appears to be independent of the anionic class of green rust, but their respective concentrations display a dependence on the initial GR. The mole fraction of Fe(III) in the Cr{sub}x,Fe{sub}(1-x)(OH){sub}3·nH{sub}2O reaction product ranged from 17 to 68, leading to a highly stabilized (low solubility) phase.
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