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用于水中草酸臭氧氧化的铁基催化剂。

Iron type catalysts for the ozonation of oxalic acid in water.

作者信息

Beltrán Fernando J, Rivas Francisco J, Montero-de-Espinosa R

机构信息

Departamento de Ingeniería Química y Energética. Universidad de Extremadura. 06071 Badajoz, Spain.

出版信息

Water Res. 2005 Sep;39(15):3553-64. doi: 10.1016/j.watres.2005.06.018.

Abstract

Two iron catalysts (Fe(III) and Fe2O3/Al2O3) have been used in the ozonation of oxalic acid in water at pH 2.5. Percentage removals of oxalic acid were 1.8%, 7% and 30% corresponding to the non-catalytic, homogeneous (Fe(III)) and heterogeneous (Fe2O3/Al2O3) catalytic ozonations, respectively. Catalytic oxalic acid ozonation leads in all cases to total mineralization. The mechanism of ozonation likely develops through formation of iron-oxalate complexes that further react with ozone without the participation of hydroxyl radicals. Because of the stringent acidic conditions, some metal leaching has been observed and quantified in the heterogeneous process. In the homogeneous catalysis, the kinetics was found to be first order with respect to ozone and oxalic acid while for the heterogeneous catalysis, the kinetic order depends on the concentration of ozone in the gas fed. Thus, at ozone concentrations lower than 30 mg L(-1), the heterogeneous ozonation is between first and zero order with respect to both ozone and oxalic acid while at higher ozone gas concentrations, the kinetics was found to be first and zero order with respect to oxalic acid and ozone, respectively. This kinetics is supported through an Eley-Rideal mechanism that involves a surface reaction between non-adsorbed ozone and adsorbed oxalic acid. Apparent activation energies of the homogeneous and heterogeneous catalytic ozonations were found to be 18.2 and 13.6 kcal mol(-1), respectively.

摘要

在pH为2.5的水中,使用了两种铁催化剂(Fe(III)和Fe2O3/Al2O3)对草酸进行臭氧化处理。对应于非催化、均相(Fe(III))和非均相(Fe2O3/Al2O3)催化臭氧化,草酸的去除率分别为1.8%、7%和30%。催化草酸臭氧化在所有情况下都能实现完全矿化。臭氧化的机理可能是通过形成草酸铁络合物来进行的,该络合物进一步与臭氧反应,而无需羟基自由基的参与。由于酸性条件苛刻,在非均相过程中观察到并定量了一些金属浸出。在均相催化中,发现动力学对臭氧和草酸为一级,而对于非均相催化,动力学级数取决于进料气体中臭氧的浓度。因此,在臭氧浓度低于30 mg L(-1)时,非均相臭氧化对臭氧和草酸均介于一级和零级之间,而在较高的臭氧气体浓度下,发现动力学对草酸和臭氧分别为一级和零级。这种动力学通过Eley-Rideal机理得到支持,该机理涉及未吸附的臭氧与吸附的草酸之间的表面反应。均相和非均相催化臭氧化的表观活化能分别为18.2和13.6 kcal mol(-1)。

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