Passivation of metal sulfides by a marine bacterium for acid mine drainage control.

J Hazard Mater

Key Laboratory of Advanced Marine Materials, Key Laboratory of Marine Environmental Corrosion and Bio-fouling, Institute of Oceanology, Chinese Academy of Sciences, Qingdao 266071, China; Biofilm Centre, Aquatische Biotechnologie, Universität Duisburg-Essen, Universitätsstraße 5, Essen 45141, Germany.

Published: December 2024

AI Article Synopsis

  • Acid mine drainage is caused by the oxidation of metal sulfides, leading to harmful acidic and metal-rich runoff, but a new method using marine bacteria can help mitigate this issue.
  • This method involves creating biofilms from the bacterium Qipengyuania flava S1, which can biomineralize and effectively isolate harmful metal sulfides from environmental exposure.
  • The study showed that after using bio-passivation, the release of harmful metals from pyrite and lead-zinc tailings dropped significantly, and the bio-passivated leachates no longer inhibited the growth of plants like Brassica chinensis and Allium cepa, indicating a promising environmental solution.

Article Abstract

Acid mine drainage originates from metal sulfides oxidation, which results in acidic metal-rich leachate. In this study, a novel and environmentally friendly approach was demonstrated to passivate pyrite and lead-zinc tailings, respectively. The key to this approach is to develop biofilms of the marine bacterium Qipengyuania flava S1. Biofilms can induce biomineralization, thereby isolating metal sulfides from air and water. The stability and biological toxicity of the bio-passivation layers were evaluated by leaching bio-passivated pyrite or tailings in initially acidic HO solutions with shaking for 180 days and then cultivating Brassica chinensis and Allium cepa with the leachates. Our results showed that after passivation, the amount of iron released by pyrite decreased by at least 99.2 ± 0.2 (in wt%). For lead-zinc tailings after passivation, the released metal ions (Fe+Al+Pb+Zn) decreased by at least 52.0 ± 3.2 (in wt%). The bio-passivation layers also maintained the pH of the leachate in the range of 7.5-8.0. Before bio-passivation, compared with mineral water, the pyrite leachate significantly inhibited the growth of the two plants, and the tailings leachate significantly inhibited the growth of A. cepa, whereas the bio-passivated pyrite or tailings leachate did not show any inhibitory effect.

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Source
http://dx.doi.org/10.1016/j.jhazmat.2024.136065DOI Listing

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