State Key Laboratory of Environment Simulation, School of Environment, Beijing Normal University, No. 19 Xinjiekouwai Street, Beijing 100875, China.
State Key Laboratory of Environment Simulation, School of Environment, Beijing Normal University, No. 19 Xinjiekouwai Street, Beijing 100875, China.
Water Res. 2016 Jan 1;88:671-680. doi: 10.1016/j.watres.2015.10.045. Epub 2015 Oct 27.
This study, for the first time, demonstrated a continuously accelerated Fe(0) corrosion driven by common oxidants (i.e., NaClO, KMnO4 or H2O2) and thereby the rapid and efficient removal of heavy metals (HMs) by zero-valent iron (ZVI) under the experimental conditions of jar tests and column running. ZVI simply coupled with NaClO, KMnO4 or H2O2 (0.5 mM) resulted in almost complete As(V) removal within only 10 min with 1000 μg/L of initial As(V) at initial pH of 7.5(±0.1) and liquid solid ratio of 200:1. Simultaneous removal of 200 μg/L of initial Cd(II) and Hg(II) to 2.4-4.4 μg/L for Cd(II) and to 4.0-5.0 μg/L for Hg(II) were achieved within 30 min. No deterioration of HM removal was observed during the ten recycles of jar tests. The ZVI columns activated by 0.1 mM of oxidants had stably treated 40,200 (NaClO), 20,295 (KMnO4) and 40,200 (H2O2) bed volumes (BV) of HM-contaminated drinking water, but with no any indication of As breakthrough (<10 μg/L) even at short empty bed contact time (EBCT) of 8.0 min. The high efficiency of HMs removal from both the jar tests and column running implied a continuous and stable activation (overcoming of iron passivation) of Fe(0) surface by the oxidants. Via the proper increase in oxidant dosing, the ZVI/oxidant combination was applicable to treat highly As(V)-contaminated wastewater. During Fe(0) surface corrosion accelerated by oxidants, a large amount of fresh and reactive iron oxides and oxyhydroxides were continuously generated, which were responsible for the rapid and efficient removal of HMs through multiple mechanisms including adsorption and co-precipitation. A steady state of Fe(0) surface activation and HM removal enabled this simply coupled system to remove HMs with high speed, efficiency and perdurability.
这项研究首次证明,在实验室规模的搅拌试验和柱运行条件下,常见氧化剂(即次氯酸钠、高锰酸钾或过氧化氢)持续加速铁(0)腐蚀,从而实现了零价铁(ZVI)对重金属(HM)的快速高效去除。ZVI 与 NaClO、KMnO4 或 H2O2(0.5 mM)简单耦合,在初始 pH 值为 7.5(±0.1)和液固比为 200:1 的条件下,仅 10 分钟内即可完全去除初始浓度为 1000 μg/L 的 As(V)。在 30 分钟内,同时去除 200 μg/L 的初始 Cd(II)和 Hg(II),Cd(II)的去除率为 2.4-4.4μg/L,Hg(II)的去除率为 4.0-5.0μg/L。在搅拌试验的十个循环中,没有观察到 HM 去除率的下降。用 0.1 mM 氧化剂激活的 ZVI 柱稳定地处理了 40200(NaClO)、20295(KMnO4)和 40200(H2O2)床体积(BV)的含 HM 饮用水,但即使在较短的空床接触时间(EBCT)为 8.0 分钟时,也没有出现 As 穿透(<10μg/L)的迹象。搅拌试验和柱运行中对 HMs 的高效去除表明,氧化剂连续且稳定地激活(克服铁钝化)Fe(0)表面。通过适当增加氧化剂剂量,ZVI/氧化剂组合可用于处理高浓度 As(V)污染废水。在氧化剂加速 Fe(0)表面腐蚀的过程中,大量新鲜且具有反应活性的铁氧化物和氢氧化物不断生成,这通过多种机制(包括吸附和共沉淀)实现了对 HMs 的快速高效去除。Fe(0)表面激活和 HM 去除的稳定状态使该简单耦合系统能够以高速、高效和持久的方式去除 HMs。