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溶解态有机质通过动力学控制汞对细菌的生物可利用性。

Dissolved organic matter kinetically controls mercury bioavailability to bacteria.

机构信息

Department of Biology, University of Ottawa , 30 Marie-Curie, Ottawa, Ontario, K1N 6N5, Canada.

出版信息

Environ Sci Technol. 2014 Mar 18;48(6):3153-61. doi: 10.1021/es4038484. Epub 2014 Feb 28.

DOI:10.1021/es4038484
PMID:24524696
Abstract

Predicting the bioavailability of inorganic mercury (Hg) to bacteria that produce the potent bioaccumulative neurotoxin monomethylmercury remains one of the greatest challenges in predicting the environmental fate and transport of Hg. Dissolved organic matter (DOM) affects mercury methylation due to its influence on cell physiology (as a potential nutrient) and its influence on Hg(II) speciation in solution (as a complexing agent), therefore controlling Hg bioavailability. We assessed the role of DOM on Hg(II) bioavailability to a gram-negative bacterium bioreporter under oxic pseudo- and nonequilibrium conditions, using defined media and field samples spanning a wide range of DOM levels. Our results showed that Hg(II) was considerably more bioavailable under nonequilibrium conditions than when DOM was absent or when Hg(II) and DOM had reached pseudoequilibrium (24 h) prior to cell exposure. Under these enhanced uptake conditions, Hg(II) bioavailability followed a bell shaped curve as DOM concentrations increased, both for defined media and natural water samples, consistent with bioaccumulation results in a companion paper (this issue) observed for amphipods. Experiments also suggest that DOM may not only provide shuttle molecules facilitating Hg uptake, but also alter cell wall properties to facilitate the first steps toward Hg(II) internalization. We propose the existence of a short-lived yet critical time window (<24 h) during which DOM facilitates the entry of newly deposited Hg(II) into aquatic food webs, suggesting that the bulk of mercury incorporation in aquatic food webs would occur within hours following its deposition from the atmosphere.

摘要

预测产生强生物蓄积性神经毒素甲基汞的细菌对无机汞 (Hg) 的生物利用度仍然是预测 Hg 环境归宿和迁移的最大挑战之一。由于溶解有机质 (DOM) 对细胞生理学的影响(作为一种潜在的营养物质)及其对溶液中 Hg(II) 形态的影响(作为一种络合剂),溶解有机质会影响汞的甲基化作用,因此控制着 Hg 的生物利用度。我们在有氧假平衡和非平衡条件下,使用定义明确的培养基和涵盖广泛 DOM 水平的现场样本,评估了 DOM 对革兰氏阴性细菌生物报告器中 Hg(II) 生物利用度的作用。我们的研究结果表明,在非平衡条件下,Hg(II) 的生物利用度明显高于没有 DOM 存在的情况,或者当 Hg(II) 和 DOM 在细胞暴露之前达到假平衡(24 小时)的情况。在这些增强的吸收条件下,Hg(II) 的生物利用度随着 DOM 浓度的增加呈钟形曲线,这对于定义明确的培养基和天然水样都是如此,这与本研究(本期)中观察到的对片脚类动物的生物累积结果一致。实验还表明,DOM 不仅可以提供促进 Hg 吸收的穿梭分子,还可以改变细胞壁特性,从而促进 Hg(II) 内化的第一步。我们提出了在一个短暂但关键的时间窗口(<24 小时)内,DOM 促进新沉积的 Hg(II) 进入水生食物网,这表明在大气中沉积后的数小时内,大部分 Hg 将被纳入水生食物网。

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