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溶解态有机质的硫化作用增加了 Hg-硫化物-溶解态有机质对 Hg 甲基化细菌的生物可利用性。

Sulfurization of Dissolved Organic Matter Increases Hg-Sulfide-Dissolved Organic Matter Bioavailability to a Hg-Methylating Bacterium.

机构信息

Department of Chemistry, Grinnell College , 1116 Eighth Avenue, Grinnell, Iowa 50112, United States.

Smithsonian Environmental Research Center , 647 Contees Wharf Road, Edgewater, Maryland 21037, United States.

出版信息

Environ Sci Technol. 2017 Aug 15;51(16):9080-9088. doi: 10.1021/acs.est.7b02781. Epub 2017 Jul 27.

Abstract

Reactions of dissolved organic matter (DOM) with aqueous sulfide (termed sulfurization) in anoxic environments can substantially increase DOM's reduced sulfur functional group content. Sulfurization may affect DOM-trace metal interactions, including complexation and metal-containing particle precipitation, aggregation, and dissolution. Using a diverse suite of DOM samples, we found that susceptibility to additional sulfur incorporation via reaction with aqueous sulfide increased with increasing DOM aromatic-, carbonyl-, and carboxyl-C content. The role of DOM sulfurization in enhancing Hg bioavailability for microbial methylation was evaluated under conditions typical of Hg methylation environments (μM sulfide concentrations and low Hg-to-DOM molar ratios). Under the conditions of predicted metacinnabar supersaturation, microbial Hg methylation increased with increasing DOM sulfurization, likely reflecting either effective inhibition of metacinnabar growth and aggregation or the formation of Hg(II)-DOM thiol complexes with high bioavailability. Remarkably, Hg methylation efficiencies with the most sulfurized DOM samples were similar (>85% of total Hg methylated) to that observed in the presence of l-cysteine, a ligand facilitating rapid Hg(II) biouptake and methylation. This suggests that complexes of Hg(II) with DOM thiols have similar bioavailability to Hg(II) complexes with low-molecular-weight thiols. Overall, our results are a demonstration of the importance of DOM sulfurization to trace metal and metalloid (especially mercury) fate in the environment. DOM sulfurization likely represents another link between anthropogenic sulfate enrichment and MeHg production in the environment.

摘要

溶解有机质(DOM)与缺氧环境中的水合硫化物(称为硫化作用)的反应可大大增加 DOM 中还原态硫官能团的含量。硫化作用可能会影响 DOM-痕量金属相互作用,包括络合以及含金属颗粒的沉淀、聚集和溶解。我们使用多种 DOM 样本发现,与水合硫化物反应以增加额外硫掺入的易感性随着 DOM 芳族碳、羰基碳和羧基碳含量的增加而增加。在典型的 Hg 甲基化环境条件下(μM 硫化物浓度和低 Hg 与 DOM 的摩尔比),评估了 DOM 硫化作用在增强 Hg 微生物甲基化生物利用度方面的作用。在预测的辰砂过饱和条件下,随着 DOM 硫化作用的增加,微生物 Hg 甲基化作用增加,这可能反映出有效地抑制了辰砂的生长和聚集,或者形成了具有高生物利用度的 Hg(II)-DOM 硫醇配合物。值得注意的是,与最硫化 DOM 样本的 Hg 甲基化效率相似(>总 Hg 甲基化的 85%),与 l-半胱氨酸存在时观察到的效率相似,l-半胱氨酸是一种促进快速 Hg(II)生物吸收和甲基化的配体。这表明 Hg(II)与 DOM 硫醇的配合物具有与低分子量硫醇的 Hg(II)配合物相似的生物利用度。总的来说,我们的结果证明了 DOM 硫化作用对痕量金属和类金属(尤其是汞)在环境中的命运的重要性。DOM 硫化作用可能代表人为硫酸盐富集与环境中 MeHg 生成之间的另一个联系。

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