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Factors and mechanisms controlling bromate removal by zerovalent iron.

机译:控制零价铁去除溴酸盐的因素和机理。

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摘要

The zerovalent iron (Fe(0)) technology widely used in remediating contaminated groundwater can be applied to drinking water treatment for reduction of bromate, a refractory by-product produced during ozone disinfection. Bromate reduction by Fe(0) under various conditions was investigated in batch tests to study the effects of iron properties (size and surface properties), repeated uses of iron, mixing rates, bromate/iron weight ratios, pH, DO, temperature, common anions and natural organic matter (NOM) on the reduction kinetics. Bromate can be completely reduced to bromide ions with good fit to pseudo-first-order kinetics and the reduction rate is considerably affected by the parameters studied. The results indicate that bromate reduction in aqueous solution is a surface-mediated chemical reduction reaction. This reaction is predominantly controlled by the iron surface conditions, although diffusion to iron surface is essential.; The role of humic acid in bromate reduction by Fe(0) was further examined in the study. The reduced functional groups present in humic acid were observed to regenerate Fe(II) and reduce bromate abiotically. The electron spin resonance further demonstrated that the redox functional groups in humic acid are most likely quinone-phenol moieties.; The growth of films of iron precipitates may affect chemical reduction of bromate by Fe(0) through the change of the interfacial properties. X-ray photoelectron spectroscopy, time-of-flight secondary mass ion spectrometry, micro-raman spectroscopy and scanning electron microscope-energy dispersive analysis of X-ray were utilized in this study to characterize the property of the film. These microscopic observations and the enhanced bromate reduction with addition of Fe(II) form a model to describe the bromate reduction with the presence of iron precipitates.; Bromate reduction by Fe(0) with incorporation of copper or palladium was investigated in batch tests. The enhanced bromate reduction rate in the presence of copper observed here is the result of the newly formed active Cu(I). The presence of PdO was evidenced by XPS but it possibly counter-balanced the reduction in adsorption and thereby yielded no enhancement in bromate reduction. Finally, the Cu2O present on the iron surface because of copper impurities in commercially available iron was found to be involved in the bromate reduction and to accelerate the reduction rate.
机译:广泛用于补救受污染的地下水的零价铁(Fe(0))技术可用于饮用水处理中,以减少溴酸盐的含量,溴酸盐是臭氧消毒过程中产生的难处理副产物。在分批测试中研究了在各种条件下通过Fe(0)还原溴酸盐的过程,以研究铁性能(尺寸和表面性能),铁的重复使用,混合速率,溴酸盐/铁重量比,pH,DO,温度,常见条件的影响。阴离子和天然有机物(NOM)的还原动力学。溴酸盐可以完全还原为溴离子,非常适合拟一级动力学,而且还原速率受研究参数的影响很大。结果表明,水溶液中的溴酸盐还原是表面介导的化学还原反应。该反应主要受铁表面条件控制,尽管扩散到铁表面是必不可少的。在研究中进一步检查了腐殖酸在Fe(0)还原溴酸盐中的作用。观察到腐殖酸中存在的还原的官能团可再生Fe(II)并非生物还原溴酸盐。电子自旋共振进一步表明,腐殖酸中的氧化还原官能团最可能是醌-酚部分。铁沉淀物膜的生长可能会通过界面性质的变化影响Fe(0)对溴酸盐的化学还原。本研究利用X射线光电子能谱,飞行时间二次质量离子能谱,显微拉曼光谱和扫描电子显微镜对X射线的能量色散分析来表征薄膜的性能。这些微观观察和添加Fe(II)增强的溴酸盐还原形成了描述铁沉淀存在下溴酸盐还原的模型。在批量测试中研究了通过掺入铜或钯的Fe(0)还原溴酸盐。此处观察到的在存在铜的情况下提高的溴酸盐还原速率是新形成的活性Cu(I)的结果。 XPS证明了PdO的存在,但它可能抵消了吸附量的减少,因此溴酸盐的减少量没有增加。最后,发现由于可商购铁中的铜杂质而存在于铁表面的Cu2O参与了溴酸盐的还原并加速了还原速率。

著录项

  • 作者

    Xie, Li.;

  • 作者单位

    Hong Kong University of Science and Technology (People's Republic of China).;

  • 授予单位 Hong Kong University of Science and Technology (People's Republic of China).;
  • 学科 Environmental Sciences.; Engineering Environmental.
  • 学位 Ph.D.
  • 年度 2005
  • 页码 187 p.
  • 总页数 187
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类 环境科学基础理论;环境污染及其防治;
  • 关键词

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