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Inhibition Of Fe(III) Reduction By Nitrate: Impact Of Anoxic Chemical and Biological Fe(II) Oxidation
C. J. Matocha, M.S. Coyne, A.F. Miller
Department of Plant and Soil Sciences
Non-Technical Summary
Elevated levels of nitrate in water supplies are undesirable because of the potential impacts on aquatic life and human health. Nitrate-dependent, iron(II) oxidation is an important process in the removal of elevated nitrate from water and the inhibition of soil iron(III) reduction, yet, the mechanisms are poorly understood. The purpose of this study is to investigate the contribution of chemical and biological Fe(II) oxidation by nitrite and nitrate.
2010 Project Description
Addition of nitrate fertilizer to soil under iron(III)-reducing conditions can lead to reoxidation of iron(II) coupled to nitrate reduction, however, the mechanisms involved are unclear. This inspired us to characterize nitrate-dependent, iron(II) oxidation in an agricultural soil by following relevant iron, nitrogen, and carbon fractions.
This past year, activities have included conducting laboratory and field experiments to investigate the contribution of chemical and biological iron(II) oxidation by nitrite and nitrate to the overall process of nitrate-dependent, iron(II) oxidation. The results derived from these activities have been disseminated via one invited presentation at a symposium at the annual Soil Science Society of America meetings in Long Beach, CA, one volunteered presentation by the Ph.D. student on the project at the Geological Society of America meeting in Denver, CO, and a USDA-NRI project director meeting in Washington, DC. These results have also been incorporated into an undergraduate soil science class in the section dealing with the nitrogen and iron cycles. One Ph.D. graduate student, one M.S. graduate student, and one undergraduate research assistant have contributed to the project..
2010 Impact
In laboratory activities, soil slurries were incubated in an anaerobic chamber to reduce all indigenous soil Fe(III) to Fe(II) prior to nitrate addition which required 28 d. Acetate was the predominant water-soluble organic carbon species which emerged during the anoxic incubation, ranging from 190 to 350 micromolar. This represented only a small fraction of the total dissolved organic carbon in the anoxic soil slurries.
Nitrate was added under anoxic conditions and relevant redox-active species were followed. At early times (5 min- 6 h), water and acid-extractable fractions of iron(II) decreased with concomitant nitrate reduction and there was little change in acetate concentrations. The rate of dissolved Fe(II) oxidation was 7.26 micromolar/hr and the rate of nitrate reduction was 3.5 micromolar/hr during the first 6 h of reaction. Nitrite was not detected in the soil slurries as an intermediate product of nitrate reduction. Nitrous oxide accumulated during the first 6 h of the reaction and decreased to negligible levels at longer time periods (>24 h). Dinitrogen was measured as the predominant product of nitrate reduction. At longer reaction times (24 h-72 h), acetate concentrations decreased drastically with a steady oxidation of iron(II) in the acid-extractable fraction as nitrate was reduced.
We are currently utilizing 15N stable isotope analysis to tease out chemical from biological iron(II) oxidation. It is plausible that chemical and biological iron(II) oxidation coupled to nitrate reduction operate simultaneously at early time periods, whereas biological pathways may predominate at longer times. These results will help predict the fate of fertilizer nitrate in soils under iron(III)-reducing conditions.
2010 Publications
Matocha, C.J., J.H. Grove, and A.D. Karathanasis. 2010. Nitrogen Fertilizer Effects on Soil Mineralogy in an Agroecosystem. International symposium "Soil Minerals in Natural and Agroecosystems", ASA-CSSA-SSSA International Annual Meetings, Long Beach, CA (Abstract No. 245-1).
Dhakal, P., C.J. Matocha, S. Pyzola, M. Vandiviere, and J.H. Grove. 2010. Changes in soil chemical properties during short-term reducing conditions followed by nitrogen fertilizer application. Geological Society of America Program and Abstract, Denver, CO (Abstract No. 228-5).