In situ bioreduction of uranium (VI) to submicromolar levels and reoxidation by dissolved oxygen

被引:156
作者
Wu, Wei-Min
Carley, Jack
Luo, Jian
Ginder-Vogel, Matthew A.
Cardenas, Erick
Leigh, Mary Beth
Hwang, Chiachi
Kelly, Shelly D.
Ruan, Chuanmin
Wu, Liyou
Van Nostrand, Joy
Gentry, Terry
Lowe, Kenneth
Mehlhorn, Tonia
Carroll, Sue
Luo, Wensui
Fields, Matthew W.
Gu, Baohua
Watson, David
Kemner, Kenneth M.
Marsh, Terence
Tiedje, James
Zhou, Jizhong
Fendorf, Scott
Kitanidis, Peter K.
Jardine, Philip M.
Criddle, Craig S. [1 ]
机构
[1] Stanford Univ, Dept Civil & Environm Engn, Stanford, CA 94305 USA
[2] Oak Ridge Natl Lab, Div Environm Sci, Oak Ridge, TN 37831 USA
[3] Stanford Univ, Dept Geol & Environm Sci, Stanford, CA 94305 USA
[4] Michigan State Univ, Ctr Microbial Ecol, E Lansing, MI 48824 USA
[5] Miami Univ, Dept Microbiol, Oxford, OH 45056 USA
[6] Argonne Natl Lab, Biosci Div, Argonne, IL 60439 USA
[7] Univ Oklahoma, Dept Bot & Microbiol, Norman, OK 73019 USA
关键词
D O I
10.1021/es062657b
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Groundwater within Area 3 of the U.S. Department of Energy (DOE) Environmental Remediation Sciences Program (ERSP) Field Research Center at Oak Ridge, TN (ORFRC) contains up to 135 mu M uranium as U(VI). Through a series of experiments at a pilot scale test facility, we explored the lower limits of groundwater U(VI) that can be achieved by in-situ biostimulation and the effects of dissolved oxygen on immobilized uranium. Weekly 2 day additions of ethanol over a 2-year period stimulated growth of denitrifying, Fe(Ill)-reducing, and sulfate-reducing bacteria, and immobilization of uranium as U(N), with dissolved uranium concentrations decreasing to low levels. Following sulfite addition to remove dissolved oxygen, aqueous U(Vl) concentrations fell below the U.S. Environmental Protection Agengy maximum contaminant limit(MCL)for drinking water (<30,mu g L-1 or0.126 mu M). Under anaerobic conditions, these low concentrations were stable, even in the absence of added ethanol. However, when sulfite additions stopped, and dissolved oxygen (4.0-5.5 mg L-1) entered the injection well, spatially variable changes in aqueous U(VI) occurred over a 60 day period, with concentrations increasing rapidly from <0.13 to 2.0 mu M at a multilevel sampling (MLS) well located close to the injection well, but changing little at an MLS well located further away. Resumption of ethanol addition restored reduction of Fe(110, sulfate, and U(V0 within 36 h. After 2 years of ethanol addition, X-ray absorption near-edge structure spectroscopy (XANES) analyses indicated that U(N) comprised 60-80% of the total uranium in sediment samples. Atthe completion ofthe project(day 1260), U concentrations in MLS wells were less than 0.1 mu M. The microbial community at MLS wells with low U(V0 contained bacteria that are known to reduce uranium, including Desulfovibrio spp. and Geobacterspp., in both sedimentand groundwater. The dominant Fe(Ill)-reducing species were Geothrix spp.
引用
收藏
页码:5716 / 5723
页数:8
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