Abstract

For acceleration of removing toxic metals from acid mine drainage (AMD), the effects of hydraulic retention time (HRT) and pH on the reactor performance and microbial community structure in the depth direction of a laboratory-scale packed-bed bioreactor containing rice bran as waste organic material were investigated. The HRT was shortened stepwise from 25 to 12 h, 8 h, and 6 to 5 h under the neutral condition using AMD neutralized with limestone (pH 6.3), and from 25 to 20 h, 12 h, and 8 to 7 h under the acid condition using AMD (pH 3.0). Under the neutral condition, the bioreactor stably operated up to 6 h HRT, which was shorter than under the acid condition (up to 20 h HRT). During stable sulfate reduction, both the organic matter-remaining condition and the low oxidation–reduction potential condition in lower parts of the reactor were observed. Principal coordinate analysis of Illumina sequencing data of 16S rRNA genes revealed a dynamic transition of the microbial communities at the boundary between stable and unstable operation in response to reductions in HRT. During stable operation under both the neutral and acid conditions, several fermentative operational taxonomic units (OTUs) from the phyla Firmicutes and Bacteroidetes dominated in lower parts of the bioreactor, suggesting that co-existence of these OTUs might lead to metabolic activation of sulfate-reducing bacteria. In contrast, during unstable operation at shorter HRTs, an OTU from the candidate phylum OP11 were found under both conditions. This study demonstrated that these microorganisms can be used to monitor the treatment of AMD, which suggests stable or deteriorated performance of the system.

Highlights

  • Acid mine drainage (AMD) is the major effluent generated from metal and coal mines, and contains a variety of dissolved metals and sulfate

  • Oxidationreduction potential (ORP) values for the 25 and 6 h hydraulic retention time (HRT) ranged from −200 to −350 mV at sampling ports (Fig. 2a), indicating that the reducing condition was maintained throughout the reactor

  • In this study, the effects of HRT and pH on the reactor performance and microbial community structure according to depth of the JOGMEC process for the treatment of AMD were investigated

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Summary

Introduction

Acid mine drainage (AMD) is the major effluent generated from metal and coal mines, and contains a variety of dissolved metals and sulfate. SRB reduce sulfate (electron acceptor) in AMD to hydrogen sulfide during oxidation of low molecular carbon sources (electron donor). SRB utilize volatile fatty acids (VFAs; e.g., acetate, propionate, butyrate and lactate) and sugars (e.g., glucose and maltose) as main carbon sources (Hiibel et al 2011). To provide such low-molecular-weight organic substrates for SRB, local organic wastes such as compost, sawdust, wood chips, and rice straw have been used and are gradually hydrolyzed and fermented to small molecules in the bioreactor (Zagury et al 2006; Chang et al 2000). Very short HRT may not allow adequate degradation of rice bran or metabolic activation of SRB, resulting in insufficient metal removal

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