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溶解有机质对 TiO2 悬浮液中吸附态 Fe(II)还原 2-硝基苯酚活性的影响。

Effects of dissolved organic matter on adsorbed Fe(II) reactivity for the reduction of 2-nitrophenol in TiO2 suspensions.

机构信息

Guangzhou Institute of Geochemistry, Chinese Academy of Sciences, Guangzhou 510640, PR China.

出版信息

Chemosphere. 2013 Sep;93(1):29-34. doi: 10.1016/j.chemosphere.2013.04.053. Epub 2013 Jun 21.

Abstract

Dissolved organic matter (DOM) is widespread in aquatic and terrestrial environments. Iron is the most abundant transition metal in the Earth's crust. The biogeochemistry of iron and the strength of Fe(II) as a reducing agent while adsorbed on minerals are affected by DOM. This study investigated the effects of Fe(II)/DOM interactions on the reduction of 2-nitrophenol (2-NP) in TiO2 suspensions. Kinetic measurements demonstrated that rates (k) of 2-NP reduction by adsorbed Fe(II) species are affected by adding DOM (denoted O-DOM), and the obtained k values under the impact of the Fe(II)/DOM interaction with different molecular weight DOM fractions [including MW<3500Da (L-DOM), 3500<MW<14000Da (M-DOM), and MW>14000Da (H-DOM)] showed significant differences. The enhanced rates of 2-NP reduction contributed to increases in the amount of adsorbed Fe(II) species and negative shifts in peak oxidation potential values (EP) in CV tests. For different molecular weight DOM fractions, increases in k (O-DOM<L-DOM<M-DOM<H-DOM) are consistent with increases in molar electron transfer capacities (ETC) based on k values at a fixed DOM concentration (O-DOM<L-DOM<M-DOM<H-DOM). This study attributed the impact of DOM on the enhanced reductive reactivity of Fe(II) to the higher level of adsorbed Fe(II) and the lower EP values. In addition, the ETC values were slightly higher in the TiO2 suspension containing the H-DOM fraction as compared the other two DOM fractions, which would further enhance the reduction rate of 2-NP. These findings promote a general understanding of Fe(II)/DOM interactions and their impact on the fate of contaminants in actual subsurface environments.

摘要

溶解有机质(DOM)广泛存在于水相和陆相环境中。铁是地壳中最丰富的过渡金属。DOM 影响铁的生物地球化学和矿物表面吸附态 Fe(II)的还原能力。本研究考察了 Fe(II)/DOM 相互作用对 TiO2 悬浮液中 2-硝基苯酚(2-NP)还原的影响。动力学测量表明,添加 DOM(表示为 O-DOM)会影响吸附态 Fe(II)物种还原 2-NP 的速率(k),并且在 Fe(II)/DOM 与不同分子量 DOM 分数[包括 MW<3500Da(L-DOM)、3500<MW<14000Da(M-DOM)和 MW>14000Da(H-DOM)]相互作用的影响下得到的 k 值存在显著差异。2-NP 还原速率的提高归因于吸附态 Fe(II)物种数量的增加以及 CV 测试中峰氧化电位值(EP)的负移。对于不同分子量的 DOM 分数,k 的增加(O-DOM<L-DOM<M-DOM<H-DOM)与基于固定 DOM 浓度(O-DOM<L-DOM<M-DOM<H-DOM)下 k 值的摩尔电子转移容量(ETC)的增加一致。本研究将 DOM 对 Fe(II)还原反应活性增强的影响归因于更高水平的吸附态 Fe(II)和更低的 EP 值。此外,与另外两个 DOM 分数相比,含有 H-DOM 分数的 TiO2 悬浮液中的 ETC 值略高,这将进一步提高 2-NP 的还原速率。这些发现促进了对 Fe(II)/DOM 相互作用及其对实际地下环境中污染物命运影响的普遍理解。

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