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Effects of Cellular Sorption on Mercury Bioavailability and Methylmercury Production by Desulfovibrio desulfuricans ND132

机译:细胞吸附对脱硫脱硫弧菌ND132汞生物利用度和甲基汞生产的影响

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摘要

Microbial conversion of inorganic mercury (IHg) to methyl mercury (MeHg) is a significant environmental concern because of the bioaccumulation and biomagnification of toxic MeHg in the food web. Laboratory incubation studies have shown that, despite the presence of large quantities of IHg in cell cultures, MeHg biosynthesis often reaches a plateau or a maximum within hours or a day by an as yet unexplained mechanism. Here we report that mercuric Hg(II) can be taken up rapidly by cells of Desulfovibrio desulfuricans ND132, but a large fraction of the Hg(II) is unavailable for methylation because of strong cellular sorption. Thiols, such as cysteine, glutathione, and penicillamine, added either simultaneously with Hg(II) or after cells have been exposed to Hg(II), effectively desorb or mobilize the bound Hg(II), leading to a substantial increase in MeHg production. The amount of thiol-desorbed Hg(II) is strongly correlated to the amount of MeHg produced (r = 0.98). However, cells do not preferentially take up Hg(II)-thiol complexes, but Hg(II)-ligand exchange between these complexes and the cell-associated proteins likely constrains Hg(II) uptake and methylation. We suggest that, aside from aqueous chemical speciation of Hg(II), binding and exchange of Hg(II) between cells and complexing ligands such as thiols and naturally dissolved organics in solution is an important controlling mechanism of Hg(II) bioavailability, which should be considered when predicting MeHg production in the environment.
机译:无机汞(IHg)向甲基汞(MeHg)的微生物转化是一个重大的环境问题,因为食物网中有毒的MeHg的生物积累和生物放大作用。实验室培养研究表明,尽管细胞培养物中存在大量的IHg,但MeHg的生物合成通常仍在数小时或一天之内达到平稳状态或达到最大值,其机制尚不清楚。在这里我们报告汞可以被脱硫脱硫弧菌ND132的细胞迅速吸收,但是由于强大的细胞吸附作用,大部分汞(II)无法用于甲基化。与Hg(II)同时或在细胞暴露于Hg(II)之后添加的半胱氨酸,谷胱甘肽和青霉素等硫醇可有效地解吸或动员结合的Hg(II),从而导致MeHg产量大幅增加。硫醇脱附的Hg(II)的量与生成的MeHg的量密切相关(r = 0.98)。但是,细胞不会优先吸收Hg(II)-硫醇复合物,但是这些复合物与细胞相关蛋白之间的Hg(II)-配体交换可能会限制Hg(II)的吸收和甲基化。我们建议,除了Hg(II)的水溶液化学形态外,细胞与溶液中的复杂配体(例如硫醇和自然溶解的有机物)之间的Hg(II)结合和交换是Hg(II)生物利用度的重要控制机制,预测环境中的甲基汞产量时应考虑到这一点。

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