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Molybdenum Availability Is Key to Nitrate Removal in Contaminated Groundwater Environments
Authors:Michael P. Thorgersen  W. Andrew Lancaster  Brian J. Vaccaro  Farris L. Poole  Andrea M. Rocha  Tonia Mehlhorn  Angelica Pettenato  Jayashree Ray  R. Jordan Waters  Ryan A. Melnyk  Romy Chakraborty  Terry C. Hazen  Adam M. Deutschbauer  Adam P. Arkin  Michael W. W. Adams
Affiliation:aDepartment of Biochemistry and Molecular Biology, University of Georgia, Athens, Georgia, USA;bBiosciences Division, Oak Ridge National Laboratory, Oak Ridge, Tennessee, USA;cLawrence Berkeley National Laboratory, Berkeley, California, USA
Abstract:The concentrations of molybdenum (Mo) and 25 other metals were measured in groundwater samples from 80 wells on the Oak Ridge Reservation (ORR) (Oak Ridge, TN), many of which are contaminated with nitrate, as well as uranium and various other metals. The concentrations of nitrate and uranium were in the ranges of 0.1 μM to 230 mM and <0.2 nM to 580 μM, respectively. Almost all metals examined had significantly greater median concentrations in a subset of wells that were highly contaminated with uranium (≥126 nM). They included cadmium, manganese, and cobalt, which were 1,300- to 2,700-fold higher. A notable exception, however, was Mo, which had a lower median concentration in the uranium-contaminated wells. This is significant, because Mo is essential in the dissimilatory nitrate reduction branch of the global nitrogen cycle. It is required at the catalytic site of nitrate reductase, the enzyme that reduces nitrate to nitrite. Moreover, more than 85% of the groundwater samples contained less than 10 nM Mo, whereas concentrations of 10 to 100 nM Mo were required for efficient growth by nitrate reduction for two Pseudomonas strains isolated from ORR wells and by a model denitrifier, Pseudomonas stutzeri RCH2. Higher concentrations of Mo tended to inhibit the growth of these strains due to the accumulation of toxic concentrations of nitrite, and this effect was exacerbated at high nitrate concentrations. The relevance of these results to a Mo-based nitrate removal strategy and the potential community-driving role that Mo plays in contaminated environments are discussed.
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