School of Civil and Environmental Engineering, University of New South Wales, Sydney, NSW 2052, Australia; State Key Laboratory of Pollution Control and Resources Reuse, School of Environmental Science and Engineering, Tongji University, Shanghai, 200092, PR China.
School of Civil and Environmental Engineering, University of New South Wales, Sydney, NSW 2052, Australia.
Water Res. 2016 Nov 15;105:331-340. doi: 10.1016/j.watres.2016.09.012. Epub 2016 Sep 13.
A comparative study of the ability of microparticulate zerovalent iron (mZVI) and nanoparticulate zerovalent iron (nZVI) to oxidize a target compound (in this study, C-labelled formate) under aerobic conditions has been conducted with specific consideration given to differences in reaction mechanisms. Results of Fe K-edge extended X-ray absorption fine structure (EXAFS) spectroscopy showed that mZVI underwent a slow transformation to ferrihydrite while nZVI, in contrast, rapidly transformed into lepidocrocite. The behavior of mZVI (compared to nZVI) could be attributed to either (i) a lower reactivity with oxygen and/or water, (ii) surface passivation by ferrihydrite resulting in reduced electron conductivity, and/or (iii) the relatively low concentration of Fe(II) which, in the case of nZVI, catalyzed the transformation of ferrihydrite to lepidocrocite. The influence of these structural transformations on contaminant removal was profound with the ferrihydrite that formed on mZVI inducing rapid adsorption of formate and moderating reactions of mZVI with oxygen and/or water. Although surface passivation of mZVI was significant, the effectiveness of the ensuing heterogeneous redox reactions in the mZVI/O system, as characterized by the molar ratio of oxidized formate to consumed Fe(0) (i.e., 13.7 ± 0.8 μM/M), was comparable to that for nZVI (16.5 ± 1.4 μM/M). The results of this study highlight the potential of mZVI for the oxidative degradation of target organics in preference to nZVI despite its lower intrinsic reactivity though some means (either natural or engineered) of inducing continual depassivation of the iron oxyhydroxide-coated mZVI would be required in order to maintain ongoing oxidant production.
已经对微颗粒零价铁 (mZVI) 和纳米颗粒零价铁 (nZVI) 在有氧条件下氧化目标化合物(在本研究中为 C 标记的甲酸盐)的能力进行了比较研究,并特别考虑了反应机制的差异。Fe K 边扩展 X 射线吸收精细结构 (EXAFS) 光谱结果表明,mZVI 缓慢转化为水铁矿,而 nZVI 则迅速转化为纤铁矿。mZVI 的行为(与 nZVI 相比)可能归因于以下原因之一:(i) 与氧气和/或水的反应性较低,(ii) 水铁矿导致的表面钝化导致电子电导率降低,和/或 (iii) 相对较低的 Fe(II)浓度,在 nZVI 的情况下,促进了水铁矿向纤铁矿的转化。这些结构转化对污染物去除的影响是深远的,形成于 mZVI 上的水铁矿诱导甲酸盐的快速吸附,并调节 mZVI 与氧气和/或水的反应。尽管 mZVI 的表面钝化是显著的,但 mZVI/O 系统中随后的非均相氧化还原反应的有效性(以氧化甲酸盐与消耗的 Fe(0)的摩尔比(即 13.7±0.8 μM/M)来表征)与 nZVI 相当(16.5±1.4 μM/M)。这项研究的结果强调了 mZVI 在氧化降解目标有机物方面的潜力,尽管其内在反应性较低,但由于需要某种方法(无论是自然的还是工程的)来诱导持续去钝化铁氢氧化物包覆的 mZVI,以维持持续的氧化剂产生。