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U(VI) Reduction by Biogenic and Abiotic Hydroxycarbonate Green Rusts: Impacts on U(IV) Speciation and Stability Over Time
Author(s) -
Sen Yan,
Maxim I. Boyanov,
Bhoopesh Mishra,
Kenneth Kemner,
Edward J. O’Loughlin
Publication year - 2018
Publication title -
environmental science and technology
Language(s) - English
Resource type - Journals
SCImago Journal Rank - 2.851
H-Index - 397
eISSN - 1520-5851
pISSN - 0013-936X
DOI - 10.1021/acs.est.7b06405
Subject(s) - carbonate , chemistry , abiotic component , groundwater , uranium , environmental chemistry , anoxic waters , redox , uraninite , environmental remediation , genetic algorithm , inorganic chemistry , geology , contamination , metallurgy , ecology , materials science , geotechnical engineering , organic chemistry , biology , paleontology
Green rusts (GRs) are redox active Fe II -Fe III minerals that form in the environment via various biotic and abiotic processes. Although both biogenic (BioGR) and abiotic (ChemGR) GRs have been shown to reduce U VI , the dynamics of the transformations and the speciation and stability of the resulting U IV phases are poorly understood. We used carbonate extraction and XAFS spectroscopy to investigate the products of U VI reduction by BioGR and ChemGR. The results show that both GRs can rapidly remove U VI from synthetic groundwater via reduction to U IV . The initial products in the ChemGR system are solids-associated U IV -carbonate complexes that gradually transform to nanocrystalline uraninite over time, leading to a decrease in the proportion of carbonate-extractable U from ∼95% to ∼10%. In contrast, solid-phase U IV atoms in the BioGR system remain relatively extractable, nonuraninite U IV species over the same reaction period. The presence of calcium and carbonate in groundwater significantly increase the extractability of U IV in the BioGR system. These data provide new insights into the transformations of U under anoxic conditions in groundwater that contains calcium and carbonate, and have major implications for predicting uranium stability within redox dynamic environments and designing approaches for the remediation of uranium-contaminated groundwater.

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