School of Chemistry, The University of Sydney, Sydney, New South Wales 2006, Australia.
J Am Chem Soc. 2010 Jun 30;132(25):8720-31. doi: 10.1021/ja101675w.
The nature of the long-lived EPR-active Cr(V) species observed in cells and biological fluids exposed to carcinogenic Cr(VI) has been definitively assigned from detailed kinetic and spectroscopic analyses of a model reaction of Cr(VI) with p-bromobenzenethiol (RSH) in the presence or absence of cyclic 1,2-diols (LH(2)) in aprotic or mixed solvents. The first definitive structures for Cr(V) complexes with a monodentate thiolato ligand, Cr(V)O(SR)(4) (g(iso) = 1.9960, A(iso) = 14.7 x 10(-4) cm(-1)), Cr(V)OL(SR)(2) (g(iso) = 1.9854, A(iso) = (15.8-16.2) x 10(-4) cm(-1)) and Cr(V)(O)(2)(SR)(2) (g(iso) = 1.9828, A(iso) = 6.8 x 10(-4) cm(-1)) were assigned by EPR spectroscopy and electrospray mass spectrometry. The unusually low A(iso) ((53)Cr) value for the latter species is consistent with its rare four-coordinate, bis-oxido structure. The Cr(V)OL(SR)(2) species are responsible for the transient g(iso) approximately 1.986 EPR signals observed in living cells and animals treated with Cr(VI) (where RSH and LH(2) are biological thiols and 1,2-diols, respectively). For the first time, concentrations of Cr(V) intermediates formed during the reduction of Cr(VI) were determined by quantitative EPR spectroscopy, and a detailed reaction mechanism was proposed on the basis of stochastic simulations of the kinetic curves for Cr(V) species. A key feature of the proposed mechanism is the regeneration of Cr(V) species in the presence of Cr(VI) through the formation of organic free radicals, followed by the rapid reactions of the formed radicals with Cr(VI). The concentration of Cr(V) grows rapidly at the beginning of the reaction, reaches a steady-state level, and then drops sharply once Cr(VI) is spent. Similar mechanisms are likely to operate during the reduction of Cr(VI) in biological environment rich in reactive C-H bonds, including the oxidative DNA damage by Cr(V) intermediates.
在暴露于致癌 Cr(VI)的细胞和生物流体中观察到的长寿命 EPR 活性 Cr(V)物种的性质,已经通过 Cr(VI)与对溴苯硫醇 (RSH)在无质子或混合溶剂中存在或不存在环状 1,2-二醇 (LH(2))的模型反应的详细动力学和光谱分析来明确确定。第一个明确的具有单齿硫醇配体的 Cr(V)配合物的结构,Cr(V)O(SR)(4) (g(iso) = 1.9960, A(iso) = 14.7 x 10(-4) cm(-1))、Cr(V)OL(SR)(2) (g(iso) = 1.9854, A(iso) = (15.8-16.2) x 10(-4) cm(-1)) 和 Cr(V)(O)(2)(SR)(2) (g(iso) = 1.9828, A(iso) = 6.8 x 10(-4) cm(-1)) 通过 EPR 光谱和电喷雾质谱法确定。后一种物种的异常低的 A(iso) ((53)Cr) 值与其罕见的四配位、双氧化物结构一致。Cr(V)OL(SR)(2) 物种负责在用 Cr(VI)处理的活细胞和动物中观察到的瞬态 g(iso) 约为 1.986 的 EPR 信号 (其中 RSH 和 LH(2)分别是生物硫醇和 1,2-二醇)。首次通过定量 EPR 光谱法确定了 Cr(VI)还原过程中形成的 Cr(V)中间体的浓度,并基于 Cr(V)物种的动力学曲线的随机模拟提出了详细的反应机制。所提出的机制的一个关键特征是在 Cr(VI)存在下通过形成有机自由基再生 Cr(V)物种,然后形成的自由基与 Cr(VI)快速反应。反应开始时 Cr(V)的浓度迅速增加,达到稳定状态,一旦 Cr(VI)耗尽,浓度急剧下降。在富含反应性 C-H 键的生物环境中还原 Cr(VI)时,可能会发生类似的机制,包括 Cr(V)中间体对 DNA 的氧化损伤。