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Hydrogen peroxide mediated oxidation of ferrous iron and associated production of hydroxyl radicals in natural aquatic systems

机译:过氧化氢介导的亚铁氧化和天然水生系统中的羟基自由基的产生

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摘要

The oxidation kinetics of ferrous iron, Fe(II), in natural aquatic systems is of interest due to both its importance to the biogeochemistry of iron, a critical micronutrient, and also due to the formation of reactive oxygen species (ROS) during these oxidation reactions. The most important oxidants of Fe(II) are O2 and H2O2, with the H2O2-mediated oxidation process of particular interest due to the potential formation of hydroxyl radical, HO•, a powerful oxidizing agent, during this process.The impact of natural organic matter (NOM) upon the H2O2-mediated oxidation of Fe(II) has been explored under both circumneutral freshwater and seawater conditions, with addition of NOM resulting in markedly slower Fe(II) oxidation rates compared to inorganic Fe(II). The formation of less-readily oxidized Fe(II)-NOM complexes is proposed to explain this, with the results quantitatively described by a kinetic model incorporating such complexes. The ability of NOM to complex Fe(II) is lower in seawater due to both ionic strength effects and the presence of cations such as Mg2+ and Ca2+ which compete with Fe(II) for NOM binding-sites, as such, the impact of NOM in seawater conditions was much lower, with the same kinetic model applicable after a decrease in the effective formation constant between Fe(II) and NOM.The question of whether HO• is formed during Fe(II) oxidation at circumneutral pH was explored using phthalhydrazide as a probe for HO•, with this method extensively characterized and validated for quantitative measurements in natural systems. Initial studies employed the well-characterized ligands EDTA, DTPA and citrate, where it was shown that at pH 8 HO• was only formed when Fe(II) was organically complexed; when inorganic Fe(II) is oxidized by H2O2 a species other than HO• is formed. Similar results were found when Fe(II) is complexed by NOM, with the HO• production data able to be modelled using the same kinetic model developed to describe the Fe(II) oxidation process if it is assumed that only Fe(II)-NOM complexes yield HO•. Overall, under circumneutral conditions Fe(II)-NOM complexes, although only slowly-oxidized by H2O2, yield HO•, whereas the more-rapidly oxidized inorganic Fe(II) species produce some other unidentified intermediate.
机译:天然水系统中亚铁(Fe(II))的氧化动力学很重要,因为它对重要的微量营养素铁的生物地球化学非常重要,而且还因为在这些氧化过程中形成了活性氧(ROS)反应。 Fe(II)最重要的氧化剂是O2和H2O2,H2O2介导的氧化过程特别受关注,因为在此过程中可能形成羟基自由基HO•(一种强大的氧化剂)。天然有机物的影响在环境中的淡水和海水条件下,都已经研究了H2O2介导的Fe(II)氧化过程中的氧化铁(NOM),添加NOM导致Fe(II)的氧化速率明显低于无机Fe(II)。提议形成较不易氧化的Fe(II)-NOM配合物来解释这一点,其结果通过结合了这种配合物的动力学模型进行了定量描述。由于离子强度效应和与Fe(II)竞争NOM结合位点的阳离子如Mg2 +和Ca2 +的存在,NOM在海水中络合Fe(II)的能力较低。 Fe(II)和NOM之间的有效形成常数减小后,适用于相同的动力学模型。在海水条件下,该条件适用。动力学问题。作为HO•的探针,这种方法广泛地表征和验证了天然系统中的定量测量。最初的研究使用了特征明确的配体EDTA,DTPA和柠檬酸盐,其中显示只有在pH 8 HO•时,Fe(II)有机络合才形成。当无机Fe(II)被H2O2氧化时,会形成HO•以外的物质。当Fe(II)与NOM络合时,发现了相似的结果,如果假定仅Fe(II)-,则可以使用为描述Fe(II)氧化过程而开发的相同动力学模型对HO•产量数据进行建模。 NOM复合物产生HO•。总的来说,在周围环境条件下,Fe(II)-NOM络合物虽然仅被H2O2缓慢氧化,但会生成HO•,而氧化得更快的无机Fe(II)物种则产生了其他一些未知的中间体。

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