4.7 Article

Isotopic Labeling Reveals Microbial Methane Oxidation Coupled to Fe(III) Mineral Reduction in Sediments from an As-Contaminated Aquifer

Journal

ENVIRONMENTAL SCIENCE & TECHNOLOGY LETTERS
Volume 8, Issue 9, Pages 832-837

Publisher

AMER CHEMICAL SOC
DOI: 10.1021/acs.estlett.1c00553

Keywords

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Funding

  1. Deutsche Forschungsgemeinschaft (DFG) [KA 1736/41-1, INST 37/935-1 FUGG]
  2. Institutional Strategy of the University of Tubingen (DFG) [ZUK 63]
  3. Collaborative Research Center CAMPOS [SFB 1253/1 2017]
  4. EmmyNoether fellowship (DFG) [326028733]
  5. High Performance and Cloud Computing Group at the Zentrum fur Datenverarbeitung of the University of Tubingen
  6. state of BadenWurttemberg through bwHPC

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This study reveals the potential contribution of methanotrophs to the dissolution of As-bearing Fe(III) minerals, leading to the release of arsenic into groundwater.
Although arsenic (As) groundwater contamination in South and Southeast Asia is a threat to human health, mechanisms of its release from sediment to groundwater are still not fully understood. In many aquifers, Fe(III) minerals are often the main hosting phases for As and their stability is crucial for As mobility. Recently, a new mechanism for As mobilization into groundwater was proposed with methane (CH4) serving as an electron donor for microbially mediated reductive dissolution of As-bearing Fe(III) minerals. To provide unequivocal evidence for the occurrence of Fe(III)-coupled methanotrophy, we incubated sediments from an As-contaminated aquifer in Hanoi (Vietnam) anoxically with isotopically labeled (CH4)-C-13. Up to 35% of the available Fe(III) was reduced within 232 days with simultaneous production of (CO2)-C-13 demonstrating anaerobic oxidation of (CH4)-C-13 with Fe(III) as the electron acceptor. The microbial community at the end of the incubation was dominated by archaea affiliating with Candidatus Methanoperedens, implying its involvement in Fe(III)-dependent CH4 oxidation. These results suggest that methanotrophs can contribute to dissolution of As-bearing Fe(III) minerals, which eventually leads to As-release into groundwater.

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