We focused on the use of abiotic MnO 2 to develop reactors for enriching manganese-oxidizing bacteria (MnOB), which may then be used to treat harmful heavy metal-containing wastewater and in the recovery of useful minor metals. Downflow hanging sponge (DHS) reactors were used under aerobic and open conditions to investigate the potential for MnOB enrichment. The results of an experiment that required a continuous supply of organic feed solution containing Mn(II) demonstrated that MnOB enrichment and Mn(II) removal were unsuccessful in the DHS reactor when plain sponge cubes were used. However, MnOB enrichment was successful within a very short operational period when sponge cubes initially containing abiotic MnO 2 were installed. The results of a microbial community analysis and MnOB isolation revealed that MnOB belonging to Comamonadaceae or Pseudomonas played a major role in Mn(II) oxidation. Successful MnOB enrichment was attributed to several unidentified species of Chitinophagaceae and Gemmataceae, which were estimated to be intolerant of MnO 2 , being unable to grow on sponge cubes containing MnO 2. The present results show that MnO 2 exerted anti-bacterial effects and inhibited the growth of certain non-MnOB groups that were intolerant of MnO 2 , thereby enabling enriched MnOB to competitively consume more substrate than MnO 2-intolerant bacteria.
The present study investigated bioelectrical methane production from CO
2
without organic substances. Even though microbial methane production has been reported at relatively high electric voltages, the amount of voltage required and the organisms contributing to the process currently remain unknown. Methane production using a biocathode was investigated in a microbial electrolysis cell coupled with an NH
4
+
oxidative reaction at an anode coated with platinum powder under a wide range of applied voltages and anaerobic conditions. A microbial community analysis revealed that methane production simultaneously occurred with biological denitrification at the biocathode. During denitrification, NO
3
–
was produced by chemical NH
4
+
oxidation at the anode and was provided to the biocathode chamber. H
2
was produced at the biocathode by the hydrogen-producing bacteria
Petrimonas
through the acceptance of electrons and protons. The H
2
produced was biologically consumed by hydrogenotrophic methanogens of
Methanobacterium
and
Methanobrevibacter
with CO
2
uptake and by hydrogenotrophic denitrifiers of
Azonexus
. This microbial community suggests that methane is indirectly produced without the use of electrons by methanogens. Furthermore, bioelectrical methane production occurred under experimental conditions even at a very low voltage of 0.05 V coupled with NH
4
+
oxidation, which was thermodynamically feasible.
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