A novel acidophile community populating waste ore deposits at an acid mine drainage site

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Abstract

Waste ore samples (pH 3.0) were collected at an acid mine drainage (AMD) site in Anhui, China. The present acidophilic microbial community in the waste ore was studied with 16S rRNA gene clone library and denaturing gradient gel electrophoresis (DGGE). Eighteen different clones were identified and affiliated with Actinobacteria, low G + C Gram-positives, Thermomicrobia, Acidobacteria, Proteobacteria, candidate division TM7, and Planctomycetes. Phylogenetic analysis of 16S rRNA gene sequences revealed a diversity of acidophiles in the samples that were mostly novel. It is unexpected that the moderately thermophilic acidophiles were abundant in the acidic ecosystem and may play a great role in the generation of AMD. The result of DGGE was consistent with that of clone library analysis. These findings help in the better understanding of the generation mechanism of AMD and in developing a more efficient method to control AMD.

References (26)

  • GK Druschel et al.

    Acid mine drainage biogeochemistry at Iron Mountain, California[J]

    Geochem Trans

    (2004)
  • KJ Edwards et al.

    An archaeal iron-oxidizing extreme acidophilcarchaea is implicated in acid mine drainage generation[J]

    Science

    (2000)
  • JJ Godon et al.

    Molecular microbial diversity of an anaerobic digestor as determined by small-subunit rDNA sequence analysis[J]

    Appl Environ Microbiol

    (1997)
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      Species such as Acidithiobacillus ferrooxidans, Leptospirillum ferrooxidans and Ferroplasma acidiphilum are known to accelerate the rate-limiting step of pyrite oxidation, (Colmer and Hinkle, 1947; Dugan and Lundgren, 1965; Dugan, 1975; Apel et al., 1976; Schrenk et al., 1998; Rawlings et al., 1999; Golyshina and Timmis, 2005; Fredrickson and Gorby, 1996; Johnson, 1998; Mielke et al., 2003) and thus have been extensively studied. However, the overall diversity of microbial communities in AMD-impacted streams has only recently begun to be appreciated (Bond et al., 2000b; Kim et al., 2001; Brake et al., 2001; Brofft, et al., 2002; Johnson and Hallberg, 2003: Baker et al., 2004; Lopez-Archilla et al., 2004; Bruneel, et al., 2005; Hallberg et al., 2006; Hao et al., 2007; He et al., 2007; Neculita et al., 2007; Damme et al., 2008; Nicomrat et al., 2008; Yin et al., 2008; Das et al., 2009). Although it is likely that these communities play critical roles in processes such as the biogeochemical cycling of metals and sulfur that are central to the generation and remediation of AMD, (Johnson, 1998; Labrenz and Banfield, 2004; Kalin et al., 2006; Weber et al., 2006; Rowe et al., 2007; Wang, et al., 2008; Lu et al., 2010) their ecological roles in AMD-impacted environments remain largely unstudied.

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    Project supported by the National Basic Research Program of China (No. 2004CB719704)

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