Analysis of the genome of Geobacter sulfurreducens revealed four genes encoding putative symporters with homology to ActP, an acetate transporter in Escherichia coli. Three of these genes, aplA, aplB and aplC, are highly similar (over 90 % identical) and fell within a tight phylogenetic cluster (Group I) consisting entirely of Geobacter homologues. Transcript levels for all three genes increased in response to acetate limitation. The fourth gene, aplD, is phylogenetically distinct (Group II) and its expression was not influenced by acetate availability. Deletion of any one of the three genes in Group I did not significantly affect acetate-dependent growth, suggesting functional redundancy. Attempts to recover mutants in which various combinations of two of these genes were deleted were unsuccessful, suggesting that at least two of these three transporter genes are required to support growth. Closely related Group I apl genes were found in the genomes of other Geobacter species whose genome sequences are available. Furthermore, related genes could be detected in genomic DNA extracted from a subsurface environment undergoing in situ uranium bioremediation. The transporter genes recovered from the subsurface were most closely related to Group I apl genes found in the genomes of cultured Geobacter species that were isolated from contaminated subsurface environments. The increased expression of these genes in response to acetate limitation, their high degree of conservation among Geobacter species and the ease with which they can be detected in environmental samples suggest that Group I apl genes of the Geobacteraceae may be suitable biomarkers for acetate limitation. Monitoring the expression of these genes could aid in the design of strategies for acetate-mediated in situ bioremediation of uranium-contaminated groundwater.
INTRODUCTIONRational design of groundwater bioremediation strategies requires information on the in situ physiological status of the micro-organisms in the subsurface (Lovley, 2003;Lovley et al., 2008). Such knowledge will make it possible to tailor amendments to groundwater to optimize bioremediation processes of interest. For example, the addition of electron donors, such as acetate, to stimulate dissimilatory metal reduction has proven to be an effective strategy for promoting the reductive precipitation of toxic metals, thereby immobilizing them and preventing their further migration through the subsurface. In the case of uranium, soluble U(VI) is microbially reduced to insoluble U(IV) Anderson et al., 2003;Cummings et al., 2003;Istok et al., 2004; Luo et al., 2007;N'Guessan et al., 2008; North et al., 2004;Petrie et al., 2003;Sanford et al., 2007;Vrionis et al., 2005). In most instances, Geobacter species have been identified as the primary U(VI)-reducing micro-organisms during active uranium precipitation (Anderson et al., 2003;Holmes et al., 2002Holmes et al., , 2007Sanford et al., 2007). While in some cases adding limiting nutrients to optimize maximum growth rates is the preferred option...