Guangdong Provincial Engineering Technology Research Center for Drinking Water Safety, School of Chemistry & Environment, South China Normal University, Guangzhou, 510006, China.
State Key Joint Laboratory of Environment Simulation and Pollution Control (SKJLESPC), Beijing Key Laboratory of Emerging Organic Contaminants Control (BKLEOCC), School of Environment, Tsinghua University, Beijing, 100084, China.
Chemosphere. 2019 Nov;235:470-480. doi: 10.1016/j.chemosphere.2019.06.168. Epub 2019 Jun 25.
Mesoporous Fe-Cu@SiO core-shell catalyst was synthesized and assessed for its catalytic activity in the ozonation of salicylic acid (SA). The synthesized catalyst was characterized by XRD, TEM, SEM, XPS, H-TPR, etc. Fe-Cu@SiO exhibited a regular spherical shape and had the surface area at 1216 m g. The wrapping of metal components and their strong interaction prevented metal leaching. Fe-Cu@SiO showed the highest activity for SA mineralization when compared with Fe@SiO and Cu@SiO. In Fe-Cu@SiO/O, 88% TOC was removed, which was 2.5 times as much as that in sole ozonation. SA degradation efficiency in Fe-Cu@SiO/O increased with initial pH. O, ·OH and HO were the main reactive oxygen species accounting for SA mineralization. Due to their scavenging effect of ·OH, NH, NO and humic acids would inhibit the degradation efficiency of Fe-Cu@SiO/O. Acidic sites, oxygen vacancies and the Fe-Cu(I/II) electron transfer were responsible for ozone decomposition and ·OH generation. SA mineralization proceeded through the ·OH mechanism. Moreover, SA mineralization in O and Fe-Cu@SiO/O both exhibited a two-stage pseudo first-order kinetics (stage I: 0-45 min; stage II: 45-120 min). The degradation intermediates were detected to investigate the reaction pathway. ORP and EEM were used to monitor the degradation process. Great difference was found for carboxylic acids accumulation in O and Fe-Cu@SiO/O. The accelerated removal of oxalic acid and humic acid-like intermediates were responsible for the two-stage pseudo first-order kinetics.
介孔 Fe-Cu@SiO 核壳催化剂被合成并用于评估其在水杨酸(SA)臭氧化中的催化活性。所合成的催化剂通过 XRD、TEM、SEM、XPS、H-TPR 等进行了表征。Fe-Cu@SiO 呈现出规则的球形,表面积为 1216 m²/g。金属组分的包裹及其强相互作用防止了金属浸出。与 Fe@SiO 和 Cu@SiO 相比,Fe-Cu@SiO 对 SA 矿化表现出最高的活性。在 Fe-Cu@SiO/O 中,88%的TOC 被去除,是单独臭氧化的 2.5 倍。在 Fe-Cu@SiO/O 中,SA 的降解效率随初始 pH 值的增加而增加。O、·OH 和 HO 是主要的活性氧物种,占 SA 矿化的 88%。由于其对·OH 的清除作用,NH₄+、NO₃-和腐殖酸会抑制 Fe-Cu@SiO/O 的降解效率。酸性位、氧空位和 Fe-Cu(I/II)电子转移负责臭氧分解和·OH 的生成。SA 的矿化通过·OH 机制进行。此外,O 和 Fe-Cu@SiO/O 中的 SA 矿化都表现出两阶段拟一级动力学(阶段 I:0-45 分钟;阶段 II:45-120 分钟)。检测降解中间体以研究反应途径。ORP 和 EEM 用于监测降解过程。在 O 和 Fe-Cu@SiO/O 中,羧酸积累有很大差异。草酸和类腐殖酸中间产物的加速去除是两阶段拟一级动力学的原因。