Department of Civil and Environmental Engineering , Northwestern University , 2145 Sheridan Road , Evanston , Illinois 60208 , United States.
Department of Materials Science and Engineering, NU ANCE Center , Northwestern University , Evanston , Illinois 60208 , United States.
Environ Sci Technol. 2018 Sep 4;52(17):10030-10039. doi: 10.1021/acs.est.8b01305. Epub 2018 Aug 22.
We investigated the chemistry of Hg(II) during exposure of exponentially growing bacteria ( Escherichia coli, Bacillus subtilis, and Geobacter sulfurreducens) to 50 nM, 500 nM, and 5 μM total Hg(II) with and without added cysteine. With X-ray absorption spectroscopy, we provide direct evidence of the formation of cell-associated HgS for all tested bacteria. The addition of cysteine (100-1000 μM) promotes HgS formation (>70% of total cell-associated Hg(II)) as a result of the biodegradation of added cysteine to sulfide. Cell-associated HgS species are also detected when cysteine is not added as a sulfide source. Two phases of HgS, cinnabar (α-HgS) and metacinnabar (β-HgS), form depending on the total concentration of Hg(II) and sulfide in the exposure medium. However, α-HgS exclusively forms in assays that contain an excess of cysteine. Scanning transmission electron microscopy images reveal that nanoparticulate HgS is primarily located at the cell surface/extracellular matrix of Gram-negative E. coli and G. sulfurreducens and in the cytoplasm/cell membrane of Gram-positive B. subtilis. Intracellular Hg(II) was detected even when the predominant cell-associated species was HgS. This study shows that HgS species can form from exogenous thiol-containing ligands and endogenous sulfide in Hg(II) biouptake assays under nondissimilatory sulfate reducing conditions, providing new considerations for the interpretation of Hg(II) biouptake results.
我们研究了指数生长期细菌(大肠杆菌、枯草芽孢杆菌和脱硫弧菌)暴露于 50 nM、500 nM 和 5 μM 总 Hg(II) 时的 Hg(II)化学性质,以及有无添加半胱氨酸的情况。通过 X 射线吸收光谱,我们为所有测试的细菌提供了形成细胞相关 HgS 的直接证据。添加半胱氨酸(100-1000 μM)会促进 HgS 的形成(>总细胞相关 Hg(II)的 70%),这是由于添加的半胱氨酸生物降解为硫化物的结果。当不添加半胱氨酸作为硫化物源时,也会检测到细胞相关的 HgS 物种。取决于暴露介质中总 Hg(II)和硫化物的浓度,会形成两种 HgS 相,辰砂(α-HgS)和汞黝铜矿(β-HgS)。然而,α-HgS 仅在含有过量半胱氨酸的测定中形成。扫描透射电子显微镜图像显示,纳米颗粒状 HgS 主要位于革兰氏阴性大肠杆菌和脱硫弧菌的细胞表面/细胞外基质中,以及革兰氏阳性枯草芽孢杆菌的细胞质/细胞膜中。即使主要的细胞相关物种是 HgS,也能检测到细胞内的 Hg(II)。本研究表明,在非异化硫酸盐还原条件下的 Hg(II)生物摄取测定中,HgS 物种可以由外源性含巯基配体和内源性硫化物形成,为 Hg(II)生物摄取结果的解释提供了新的考虑因素。