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首页> 外文期刊>Canadian Journal of Chemistry >Formation of Hg(II) tetrathiolate complexes with cysteine at neutral pH
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Formation of Hg(II) tetrathiolate complexes with cysteine at neutral pH

机译:在中性pH下与半胱氨酸形成Hg(II)Hg(II)配合物

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摘要

Mercury(II) ions precipitate from aqueous cysteine (H(2)Cys) solutions containing H(2)Cys/Hg(II) mole ratio >= 2.0 as Hg(S-HCys)(2). In the absence of additional cysteine, the precipitate dissolves at pH similar to 12 with the [Hg(S,N-Cys)(2)](2-) complex dominating. With excess cysteine (H(2)Cys/Hg(II) mole ratio >= 4.0), higher complexes form and the precipitate dissolves at lower pH values. Previously, we found that tetrathiolate [Hg(S-Cys)(4)](6-) complexes form at pH = 11.0; in this work, we extend the investigation to pH values of physiological interest. We examined two series of Hg(II)-cysteine solutions in which C-Hg(II) varied between 8 and 9 mmol/L and 80 and 100 mmol/L, respectively, with H(2)Cys/Hg(II) mole ratios from 4 to similar to 20. The solutions were prepared in the pH range 7.1-8.8 at the pH at which the initial Hg(S-HCys)(2) precipitate dissolved. The variations in the Hg(II) speciation were followed by Hg-199 NMR, X-ray absorption, and Raman spectroscopic techniques. Our results show that in the dilute solutions (C-Hg(II) = 8-9 mmol/L), mixtures of di-, tri-(major), and tetrathiolate complexes exist at moderate cysteine excess (C-H2Cys similar to 0.16 mol/L) at pH 7.1. In the more concentrated solutions (C-Hg(II) = 80-100 mmol/L) with high cysteine excess (C-H2Cys > 0.9 mol/L), tetrathiolate [Hg(S-cysteinate)(4)](m-6) (m = 0-4) complexes dominate in the pH range 7.3-7.8, with lower charge than for the [Hg(S-Cys)(4)](6-) complex due to protonation of some (m) of the amino groups of the coordinated cysteine ligands. The results of this investigation could provide a key to the mechanism of biosorption and accumulation of Hg(II) ions in biological/ environmental systems.
机译:汞(II)离子从半胱氨酸(H(2)Cys)水溶液中析出,其中H(2)Cys / Hg(II)摩尔比> = 2.0作为Hg(S-HCys)(2)。在没有额外的半胱氨酸的情况下,沉淀物在[Hg(S,N-Cys)(2)](2-)络合物占主导的pH值下类似于12溶解。随着过量的半胱氨酸(H(2)Cys / Hg(II)摩尔比> = 4.0),形成更高的络合物,沉淀物在更低的pH值下溶解。以前,我们发现四硫醇盐[Hg(S-Cys)(4)](6-)配合物在pH = 11.0时形成;在这项工作中,我们将研究扩展到具有生理价值的pH值。我们研究了两个系列的Hg(II)-半胱氨酸溶液,其中C-Hg(II)分别在H(2)Cys / Hg(II)摩尔之间变化,介于8至9 mmol / L和80至100 mmol / L之间。比率从4到接近20。在初始Hg(S-HCys)(2)沉淀溶解的pH值下,在7.1-8.8的pH范围内制备溶液。 Hg(II)形态的变化之后是Hg-199 NMR,X射线吸收和拉曼光谱技术。我们的结果表明,在稀溶液(C-Hg(II)= 8-9 mmol / L)中,二,三(主要)和四硫醇盐络合物的混合物以中等半胱氨酸过量存在(C-H2Cys类似于0.16摩尔/升)在pH 7.1。在半胱氨酸过量过多(C-H2Cys> 0.9 mol / L)的更浓缩溶液(C-Hg(II)= 80-100 mmol / L)中,四硫醇盐[Hg(S-半胱氨酸)(4)](m- 6)(m = 0-4)络合物在pH范围7.3-7.8中占主导地位,其电荷比[Hg(S-Cys)(4)](6-)络合物低,这是由于某些(m)的质子化配位的半胱氨酸配体的氨基。这项研究的结果可以为生物/环境系统中Hg(II)离子的生物吸附和积累机制提供关键。

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