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零价铁在含腐殖酸的中等硬度水中还原六价铬的动力学:铁的溶解与腐殖酸的吸附

Chromium(VI) reduction kinetics by zero-valent iron in moderately hard water with humic acid: iron dissolution and humic acid adsorption.

作者信息

Liu Tongzhou, Tsang Daniel C W, Lo Irene M C

机构信息

Department of Civil Engineering, The Hong Kong University of Science and Technology, Hong Kong, China.

出版信息

Environ Sci Technol. 2008 Mar 15;42(6):2092-8. doi: 10.1021/es072059c.

Abstract

In zerovalent iron treatment systems, the presence of multiple solution components may impose combined effects that differ from corresponding individual effects. The copresence of humic acid and hardness (Ca2+/Mg2+) was found to influence Cr(VI) reduction by Feo and iron dissolution in a way different from their respective presence in batch kinetics experiments with synthetic groundwater at initial pH 6 and 9.5. Cr(VI) reduction rate constants (k(obs)) were slightly inhibited by humic acid adsorption on iron filings (decreases of 7-9% and 10-12% in the presence of humic acid alone and together with hardness, respectively). The total amount of dissolved Fe steadily increased to 25 mg L(-1) in the presence of humic acid alone because the formation of soluble Fe-humate complexes appeared to suppress iron precipitation. Substantial amounts of soluble and colloidal Fe-humate complexes in groundwater may arouse aesthetic and safety concerns in groundwater use. In contrast, the coexistence of humic acid and Ca2+/Mg2+ significantly promoted aggregation of humic acid and metal hydrolyzed species, as indicated by XPS and TEM analyses, which remained nondissolved (>0.45 microm) in solution. These metal-humate aggregates may impose long-term impacts on PRBs in subsurface settings.

摘要

在零价铁处理系统中,多种溶液成分的存在可能会产生与相应单一成分影响不同的综合效应。研究发现,腐殖酸和硬度(Ca2+/Mg2+)共存时对Feo还原Cr(VI)和铁溶解的影响,与它们在初始pH为6和9.5的合成地下水的间歇动力学实验中各自单独存在时的影响不同。腐殖酸吸附在铁屑上会使Cr(VI)还原速率常数(k(obs))略有降低(单独存在腐殖酸时降低7 - 9%,腐殖酸与硬度共存时降低10 - 12%)。单独存在腐殖酸时,溶解态铁的总量稳步增加至25 mg L(-1),因为可溶性铁 - 腐殖酸络合物的形成似乎抑制了铁的沉淀。地下水中大量的可溶性和胶体态铁 - 腐殖酸络合物可能会引起地下水使用中的美观和安全问题。相比之下,XPS和TEM分析表明,腐殖酸与Ca2+/Mg2+共存显著促进了腐殖酸和金属水解产物的聚集,这些聚集物在溶液中保持不溶解状态(>0.45微米)。这些金属 - 腐殖酸聚集体可能会对地下环境中的渗透反应墙产生长期影响。

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