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重金属对从矿山尾矿中富集的自养微生物群落生物降解硫氰酸盐的影响。

The effect of heavy metals on thiocyanate biodegradation by an autotrophic microbial consortium enriched from mine tailings.

机构信息

School of Earth Sciences, The University of Melbourne, Parkville, VIC, 3010, Australia.

School of Geographical & Earth Sciences, University of Glasgow, Glasgow, G12 8QQ, UK.

出版信息

Appl Microbiol Biotechnol. 2021 Jan;105(1):417-427. doi: 10.1007/s00253-020-10983-4. Epub 2020 Dec 2.

Abstract

Bioremediation systems represent an environmentally sustainable approach to degrading industrially generated thiocyanate (SCN), with low energy demand and operational costs and high efficiency and substrate specificity. However, heavy metals present in mine tailings effluent may hamper process efficiency by poisoning thiocyanate-degrading microbial consortia. Here, we experimentally tested the tolerance of an autotrophic SCN-degrading bacterial consortium enriched from gold mine tailings for Zn, Cu, Ni, Cr, and As. All of the selected metals inhibited SCN biodegradation to different extents, depending on concentration. At pH of 7.8 and 30 °C, complete inhibition of SCN biodegradation by Zn, Cu, Ni, and Cr occurred at 20, 5, 10, and 6 mg L, respectively. Lower concentrations of these metals decreased the rate of SCN biodegradation, with relatively long lag times. Interestingly, the microbial consortium tolerated As even at 500 mg L, although both the rate and extent of SCN biodegradation were affected. Potentially, the observed As tolerance could be explained by the origin of our microbial consortium in tailings derived from As-enriched gold ore (arsenopyrite). This study highlights the importance of considering metal co-contamination in bioreactor design and operation for SCN bioremediation at mine sites. KEY POINTS: • Both the efficiency and rate of SCN biodegradation were inhibited by heavy metals, to different degrees depending on type and concentration of metal. • The autotrophic microbial consortium was capable of tolerating high concentrations of As, potential having adapted to higher As levels derived from the tailings source.

摘要

生物修复系统是一种环境可持续的方法,可用于降解工业产生的硫氰酸盐 (SCN),其具有低能耗和运营成本、高效率和底物特异性。然而,矿山尾矿废水中存在的重金属可能通过毒害硫氰酸盐降解微生物群落而阻碍处理效率。在这里,我们通过实验测试了从金矿尾矿中富集的自养 SCN 降解细菌群落对 Zn、Cu、Ni、Cr 和 As 的耐受性。所有选定的金属都在不同程度上抑制了 SCN 的生物降解,这取决于浓度。在 pH 值为 7.8 和 30°C 的条件下,Zn、Cu、Ni 和 Cr 分别在 20、5、10 和 6 mg/L 的浓度下完全抑制了 SCN 的生物降解。这些金属的较低浓度会降低 SCN 生物降解的速率,同时具有较长的滞后时间。有趣的是,即使在 500mg/L 的浓度下,微生物群落也能耐受 As,尽管 SCN 的生物降解速率和程度都受到了影响。可能,我们的微生物群落起源于富含砷的金矿尾矿(毒砂),这可以解释观察到的砷耐受性。本研究强调了在矿山场地进行 SCN 生物修复时,在生物反应器设计和操作中考虑重金属的共污染的重要性。关键点:

  1. 重金属对 SCN 生物降解的效率和速率都有抑制作用,其抑制程度取决于金属的类型和浓度。

  2. 自养微生物群落能够耐受高浓度的 As,可能已经适应了源自尾矿源的更高的 As 水平。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/7849/7778618/89ca1703ec7a/253_2020_10983_Fig1_HTML.jpg

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