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光合细菌对汞的吸收化学计量学与动力学

Stoichiometry and kinetics of mercury uptake by photosynthetic bacteria.

作者信息

Kis Mariann, Sipka Gábor, Maróti Péter

机构信息

Institute of Medical Physics, University of Szeged, Rerrich Béla tér 1, Szeged, 6720, Hungary.

出版信息

Photosynth Res. 2017 May;132(2):197-209. doi: 10.1007/s11120-017-0357-z. Epub 2017 Mar 4.

Abstract

Mercury adsorption on the cell surface and intracellular uptake by bacteria represent the key first step in the production and accumulation of highly toxic mercury in living organisms. In this work, the biophysical characteristics of mercury bioaccumulation are studied in intact cells of photosynthetic bacteria by use of analytical (dithizone) assay and physiological photosynthetic markers (pigment content, fluorescence induction, and membrane potential) to determine the amount of mercury ions bound to the cell surface and taken up by the cell. It is shown that the Hg(II) uptake mechanism (1) has two kinetically distinguishable components, (2) includes co-opted influx through heavy metal transporters since the slow component is inhibited by Ca channel blockers, (3) shows complex pH dependence demonstrating the competition of ligand binding of Hg(II) ions with H ions (low pH) and high tendency of complex formation of Hg(II) with hydroxyl ions (high pH), and (4) is not a passive but an energy-dependent process as evidenced by light activation and inhibition by protonophore. Photosynthetic bacteria can accumulate Hg(II) in amounts much (about 10) greater than their own masses by well-defined strong and weak binding sites with equilibrium binding constants in the range of 1 (μM) and 1 (mM), respectively. The strong binding sites are attributed to sulfhydryl groups as the uptake is blocked by use of sulfhydryl modifying agents and their number is much (two orders of magnitude) smaller than the number of weak binding sites. Biofilms developed by some bacteria (e.g., Rvx. gelatinosus) increase the mercury binding capacity further by a factor of about five. Photosynthetic bacteria in the light act as a sponge of Hg(II) and can be potentially used for biomonitoring and bioremediation of mercury-contaminated aqueous cultures.

摘要

汞在细胞表面的吸附以及细菌的细胞内摄取是生物体中剧毒汞产生和积累的关键第一步。在这项工作中,通过使用分析(双硫腙)测定法和生理光合标记物(色素含量、荧光诱导和膜电位)来研究光合细菌完整细胞中汞生物累积的生物物理特性,以确定结合到细胞表面并被细胞摄取的汞离子量。结果表明,Hg(II) 的摄取机制:(1)有两个动力学上可区分的组分;(2)包括通过重金属转运蛋白的协同流入,因为慢组分受到钙通道阻滞剂的抑制;(3)表现出复杂的pH依赖性,表明Hg(II) 离子与H离子(低pH)的配体结合竞争以及Hg(II) 与羟基离子形成络合物的高趋势(高pH);(4)不是被动过程而是能量依赖过程,光激活和质子载体抑制证明了这一点。光合细菌可以通过定义明确的强结合位点和弱结合位点,以比自身质量大得多(约10倍)的量积累Hg(II),其平衡结合常数分别在1(μM)和1(mM)范围内。强结合位点归因于巯基,因为摄取被巯基修饰剂阻断,并且其数量比弱结合位点的数量少得多(两个数量级)。一些细菌(例如,胶质红环菌)形成的生物膜可使汞结合能力进一步提高约五倍。光照下的光合细菌可作为Hg(II) 的海绵, potentially可用于汞污染水培物的生物监测和生物修复。

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