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Transition metal/UV-based advanced oxidation technologies for water decontamination

机译:基于过渡金属/紫外线的高级氧化技术,可用于水净化

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This study explores the effect of ultraviolet (UV) light radiation and/or transition metals (M) for the activation of common oxidants (Ox) with the objective of treating recalcitrant organic contaminants in water. Hydrogen peroxide, potassium peroxymonosulfate and potassium persulfate were combined with iron, cobalt and silver, respectively, and/or with UV light (254 inn) and were tested for the treatment of 2,4-dichlorophenol (2,4-DCP). Results from our previous studies indicated that these particular transition metals are the best catalysts for the activation of the respective oxidants [G.P. Anipsitakis, D.D. Dionysiou, Environ. Sci. Technol. 37 (2003) 4790; G.P. Anipsitakis, D.D. Dionysiou, Environ. Sci. Technol. 38 (2004) 3705]. From the combined use of UV, the oxidants and the transition metals, four general categories of advanced oxidation technologies were evaluated and compared for the degradation and mineralization of 2,4-DCP. Those were (i) the dark conjunction of each oxidant with its favorable metal activator (M/Ox), (ii) the use of UV alone, (iii) the combination of UV with each oxidant (UV/Ox) and (iv) the use of UV combined with each metal/oxidant systems (UV/M/Ox). In particular, the systems UV/KHSO5, UV/Co(II)/KHSO5 and UV/A-(I)/K2S2O8 and the sulfate radicals generated thereby have never been tested before for water decontamination, as opposed to the extensively investigated hydroxyl radicals generated by UV/H2O2 and the photo-Fenton. The comparison of the results with respect to the transformation of 2.4-DCP and the extent of organic carbon removal led to the construction of the following order of efficiencies: UV/K2S2O8 > UV/KHSO5 > UV/H2O2 for the UV/Ox processes and UV/Fe(III)/H2O2 > UV/Fe(II)/H2O2 > UV/Co(II)/KHSO5 > UV/A-(I)/K2S2O8 for the UV/M/Ox processes tested here. All experiments were homogeneous and conducted at ambient room temperature. The relative absorbance of the species participating in the reactions supports the former order of efficiency, since persulfate followed by peroxymonosulfate were proven more photosensitive than hydrogen peroxide. Among the metals tested, only iron species such as Fe(OH)(2+) were found to absorb strongly at 254 nm and to this is attributed the higher efficiencies obtained with the photo-Fenton reagents. (C) 2004 Elsevier B.V. All rights reserved.
机译:这项研究探索了紫外线(UV)辐射和/或过渡金属(M)对常见氧化剂(Ox)活化的作用,目的是处理水中的难降解有机污染物。将过氧化氢,过氧一硫酸钾和过硫酸钾分别与铁,钴和银和/或与紫外线(254客栈)混合,并测试了其对2,4-二氯苯酚(2,4-DCP)的处理。我们以前的研究结果表明,这些特定的过渡金属是活化相应氧化剂的最佳催化剂。阿尼皮西塔基斯(Danielitakis) Dionysiou,环境。科学技术。 37(2003)4790; G.P.阿尼皮西塔基斯(Danielitakis) Dionysiou,环境。科学技术。 38(2004)3705]。通过结合使用紫外线,氧化剂和过渡金属,评估了四类高级氧化技术,并比较了其对2,4-DCP的降解和矿化作用。这些是(i)每种氧化剂与有利的金属活化剂(M / Ox)的暗键,(ii)单独使用UV,(iii)UV与每种氧化剂(UV / Ox)的组合,以及(iv)将紫外线与每种金属/氧化剂系统(UV / M / Ox)结合使用。尤其是,UV / KHSO5,UV / Co(II)/ KHSO5和UV / A-(I)/ K2S2O8系统以及由此产生的硫酸根以及从未进行过水去污的测试,与经过广泛研究的羟基相反由UV / H2O2和光Fenton产生。关于2.4-DCP转化和有机碳去除程度的结果比较导致了以下效率顺序的构建:UV / K2S2O8> UV / KHSO5> UV / HxO2工艺的UV / H2O2和对于此处测试的UV / M / Ox工艺,UV / Fe(III)/ H2O2> UV / Fe(II)/ H2O2> UV / Co(II)/ KHSO5> UV / A-(I)/ K2S2O8所有实验均是均质的,并在室温下进行。参与反应的物质的相对吸光度支持效率的前一个顺序,因为事实证明过硫酸盐接着过氧一硫酸盐比过氧化氢更具光敏性。在测试的金属中,仅发现铁物种(例如Fe(OH)(2+))在254 nm处强烈吸收,这归因于使用光芬顿试剂获得的更高效率。 (C)2004 Elsevier B.V.保留所有权利。

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