Denaturing gradient gel electrophoresis (DGGE) and quantitative real-time PCR (qPCR) were successfully developed to monitor functional aoxB genes as markers of aerobic arsenite oxidizers. DGGE profiles showed a shift in the structure of the aoxB-carrying bacterial population, composed of members of the Alpha-, Beta-and Gammaproteobacteria, depending on arsenic (As) and E h levels in Upper Isle River Basin waters. The highest aoxB gene densities were found in the most As-polluted oxic surface waters but without any significant correlation with environmental factors. Arsenite oxidizers seem to play a key role in As mobility in As-impacted waters.Arsenic (As) occurs naturally as a local geological constituent of the soils surrounding the Upper Isle River Basin (Massif Central, France) due to natural geochemical anomalies but is also released from Au/As deposits of disused gold mines (4,11,12,33). Important variations in dissolved As concentrations are found in the Isle River and depend on the hydrogeological season, with maximum values in spring and summer generally detected during low-flow conditions (12,22), and probably on temperature-controlled microbial As(V) reduction and/or microbial dissolution of solid As carrier phases (22). Two toxic inorganic forms of As are usually detected in aquatic system: arsenite, As(III), which is found mainly under anaerobic conditions and is more mobile than arsenate, As(V), which typically occurs under aerobic conditions and tends to associate with oxyhydroxides and clay minerals (11,34). Although bacteria are known to play a key role in speciation, mobility, and bioavailability of As in the environment, they have never been considered in previous studies of As mobility in the Isle River system. Indeed, former investigations of As cycling were focused on geochemical studies (4,11,12,22,33).As(III)-oxidizing bacteria can contribute to a natural attenuation of As pollution by decreasing its bioavailability and can help remove As from mine wastewaters through bioprocessing (1, 2). Many As(III) oxidizers have been isolated from various environments, especially mesophilic ecosystems (3,5,8,16,25,27,32,38). They belong to more than 25 genera, mainly of the Proteobacteria phylum (3, 32, 38), and are related to organisms unable to oxidize As(III) based on 16S rRNA phylogeny. Diverse primer sets have been successfully developed to specifically target the functional aoxB gene (9,14,17,25,26), encoding the large molybdenum-bearing catalytic subunit of As(III)-oxidase (EC 1.20.98.1), an enzyme of the dimethyl sulfoxide (DMSO) reductase family. Using cloning-sequencing approaches, the aoxB gene has proven to be a reliable molecular marker for diversity studies of the polyphyletic aerobic As(III) oxidizers in As-impacted soil and water systems (17, 25). The genetic fingerprinting denaturing gradient gel electrophoresis (DGGE) technique is one useful tool for spatial, temporal, and geographical monitoring of complex bacterial population structure (23, 24). Quantitative real-time PCR (qPCR) p...