A pilot-scale field experiment demonstrated that a one-time amendment of emulsified vegetable oil (EVO) reduced groundwater U(VI) concentrations for 1 year in a fast-flowing aquifer. However, little is known about how EVO amendment stimulates the functional gene composition, structure, and dynamics of groundwater microbial communities toward prolonged U(VI) reduction. In this study, we hypothesized that EVO amendment would shift the functional gene composition and structure of groundwater microbial communities and stimulate key functional genes/groups involved in EVO biodegradation and reduction of electron acceptors in the aquifer. To test these hypotheses, groundwater microbial communities after EVO amendment were analyzed using a comprehensive functional gene microarray. Our results showed that EVO amendment stimulated sequential shifts in the functional composition and structure of groundwater microbial communities. Particularly, the relative abundance of key functional genes/groups involved in EVO biodegradation and the reduction of NO 3 ؊ , Mn(IV), Fe(III), U(VI), and SO 4 2؊ significantly increased, especially during the active U(VI) reduction period. The relative abundance for some of these key functional genes/groups remained elevated over 9 months. Montel tests suggested that the dynamics in the abundance, composition, and structure of these key functional genes/groups were significantly correlated with groundwater concentrations of acetate, NO 3 ؊ , Mn(II), Fe(II), U(VI), and SO 4 2؊ . Our results suggest that EVO amendment stimulated dynamic succession of key functional microbial communities. This study improves our understanding of the composition, structure, and function changes needed for groundwater microbial communities to sustain a long-term U(VI) reduction.
Mining, ore processing, and weapons and fuel production have left many sites around the world contaminated with uranium (U) (1). Groundwater contamination in particular is a critical public concern because the transport of highly soluble and toxic U(VI) within groundwater threatens drinking water resources. Bioreduction of U(VI) to insoluble U(IV) has been recognized as an effective approach to immobilize U in situ (2). However, while microorganisms capable of U(VI) reduction are present in aquifers, U(VI) still persists because of the lack of available electron donors and, in some cases, the presence of excess competing electron acceptors (e.g., NO 3 Ϫ ) (3). Injection of a substrate that would provide electron donors is essential to stimulate indigenous microbial communities toward U(VI) reduction (4, 5).Some U.S. Department of Energy (DOE) sites, for example, the Oak Ridge Integrated Field Research Challenge (ORIFRC) and the Old Rifle uranium mill tailing remedial action sites, are contaminated with U(VI). To remediate these sites, various fast-degrading substrates (e.g., acetate, ethanol, and lactate) have been used. The substrate injection stimulated microbial populations important to U(VI) reduction, resulting in distinct microbial co...