期刊
JOURNAL OF ENVIRONMENTAL QUALITY
卷 34, 期 4, 页码 1286-1292出版社
AMER SOC AGRONOMY
DOI: 10.2134/jeq2004.0459
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Recent strategies to reduce elevated nitrate (NO3-) concentrations employ metallic Fe-0 as a reductant. Secondary Products of Fe-0 corrosion include magnetite (Fe3O4), green rust [Fe-6(OH)(12)SO4], and wustite [FeO(s)]. To our knowledge, no studies have been reported on the reactivity of NO3- with FeO(s). This project was initiated to evaluate the reactivity of FeO(s) with NO3- under abiotic conditions. Stirred batch reactions were performed in an anaerobic chamber over a range of pH values (5.45, 6.45, and 7.45), initial FeO(s) concentrations (1, 5, and 10 g L-1), initial NO3- concentrations (1, 10, and 15 niM), and temperatures (3, 21, 31, and 41 degrees C) for kinetic and thermodynamic determinations. Suspensions were periodically removed and filtered to measure dissolved nitrogen and iron species. Solid phases were characterized using X-ray diffraction (XRD) and scanning electron microscopy (SEM). Nitrate reduction by FeO was rapid and character. ized by nearly stoichiometric conversion of NO3- to NH4+. Transient NO2- formation also occurred. The XRD and SEM results indicated the formation of Fe3O4 as a reaction product of the heterogeneous redox reaction. Kinetics of NO3- reduction suggested a rate equation of the type: -d[NO3-]/dt = k[FeO](0.57)[H+](0.22)[NO3-](1.12) where k 3.46 X 10(-3) +/- 0.38 X 10(-3) M-1 s(-1), at 25 degrees C. Arrhenius and Eyring plots indicate that the reaction is surface chemical-controlled and proceeds by an associative mechanism involving a step where both NO3- and FeO(s) bind together in an intermediate complex.
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