Mishra Dhananjay, Farrell James
Department of Chemical and Environmental Engineering, University of Arizona, Tucson, Arizona 85721, USA.
Environ Sci Technol. 2005 Jan 15;39(2):645-50. doi: 10.1021/es049259y.
This study investigated the reaction mechanisms of nitrate (NO3-) with zerovalent iron (ZVI) media under conditions relevantto groundwatertreatment using permeable reactive barriers (PRB). Reaction rates of NO3- with freely corroding and with cathodically or anodically polarized iron wires were measured in batch reactors. Tafel analysis and electrochemical impedance spectroscopy (EIS) were used to investigate the reactions occurring on the iron surfaces. Reduction of NO3- by corroding iron resulted in near stoichiometric production of NO2-, which did not measurably react in the absence of added Fe(II). Increasing NO3- concentrations resulted in increasing corrosion currents. However, EIS and Tafel analyses indicated that there was little direct reduction of NO3- at the ZVI surface, despite the presence of water reduction. This behavior can be attributed to formation of a microporous oxide on the iron surfaces that blocked reduction of NO3- and NO2- but did not block water reduction. This finding is consistent with previous observations that NO3- impedes reduction of organic compounds by ZVI. Nitrite concentrations greater than 4 mM resulted in anodic passivation of the iron, but passivation was not observed with NO3- concentrations as high as 96 mM. This indicates that the passivating oxide preventing NO3- reduction was permeable toward cation migration. Since reaction with Fe(0) can be excluded asthe mechanism for NO3- and NO2- reduction, reaction with Fe(II)-containing oxides coating the iron surface is the most likely reaction mechanism. This suggests that short-term batch tests requiring little turnover of reactive sites on the iron surface may overestimate long-term rates of NO3- removal because the effects of passivation are not apparent in batch tests conducted with high initial Fe(II) to NO3- ratios.
本研究调查了在与使用渗透反应屏障(PRB)进行地下水处理相关的条件下,硝酸盐(NO₃⁻)与零价铁(ZVI)介质的反应机制。在间歇式反应器中测量了NO₃⁻与自由腐蚀以及阴极或阳极极化铁丝的反应速率。采用塔菲尔分析和电化学阻抗谱(EIS)来研究铁表面发生的反应。腐蚀铁对NO₃⁻的还原导致近乎化学计量的NO₂⁻生成,在没有添加Fe(II)的情况下,NO₂⁻没有明显反应。NO₃⁻浓度增加导致腐蚀电流增加。然而,EIS和塔菲尔分析表明,尽管存在析氢反应,但在ZVI表面几乎没有NO₃⁻的直接还原。这种行为可归因于铁表面形成了微孔氧化物,该氧化物阻碍了NO₃⁻和NO₂⁻的还原,但没有阻碍析氢反应。这一发现与之前观察到的NO₃⁻阻碍ZVI对有机化合物的还原一致。亚硝酸盐浓度大于4 mM会导致铁的阳极钝化,但在NO₃⁻浓度高达96 mM时未观察到钝化现象。这表明阻止NO₃⁻还原的钝化氧化物对阳离子迁移是可渗透的。由于与Fe(0)的反应可被排除为NO₃⁻和NO₂⁻还原的机制,与铁表面包覆的含Fe(II)氧化物的反应是最可能的反应机制。这表明,由于在高初始Fe(II)与NO₃⁻比例的间歇试验中钝化效应不明显,因此对铁表面反应位点周转需求很少的短期间歇试验可能高估了NO₃⁻的长期去除率。