文摘
The potential for microbially catalyzed NO3--dependentoxidation of solid-phase Fe(II) compounds was examinedusing a previously described autotrophic, denitrifying, Fe(II)-oxidizing enrichment culture. The following solid-phase Fe(II)-bearing minerals were considered: microbiallyreduced synthetic goethite, two different end productsof microbially hydrous ferric oxide (HFO) reduction (biogenicFe3O4 and biogenic FeCO3), chemically precipitatedFeCO3, and two microbially reduced iron(III) oxide-richsubsoils. The microbially reduced goethite, subsoils, andchemically precipitated FeCO3 were subject to rapid NO3--dependent Fe(II) oxidation. Significant oxidation ofbiogenic Fe3O4 was observed. Very little biogenic FeCO3was oxidized. No reduction of NO3- or oxidation of Fe(II)occurred in pasteurized cultures. The molar ratio of NO3-reduced to Fe(II) oxidized in cultures containing chemicallyprecipitated FeCO3, and one of the microbially reducedsubsoils approximated the theoretical stoichiometry of 0.2:1. However, molar ratios obtained for oxidation ofmicrobially reduced goethite, the other subsoil, and theHFO reduction end products did not agree with this theoreticalvalue. These discrepancies may be related to heterotrophicNO3- reduction coupled to oxidation of dead Fe(III)-reducing bacterial biomass. Our findings demonstrate thatmicrobally catalyzed NO3--dependent Fe(II) oxidationhas the potential to significantly accelerate the oxidationof solid-phase Fe(II) compounds by oxidized N species. Thisprocess could have an important influence on themigration of contaminant metals and radionuclides insubsurface environments.