Key Laboratory for Water Quality and Conservation of the Pearl River Delta, Ministry of Education, Institute of Environmental Research at Greater Bay, Guangzhou University, Guangzhou 510006, China.
Key Laboratory for Water Quality and Conservation of the Pearl River Delta, Ministry of Education, Institute of Environmental Research at Greater Bay, Guangzhou University, Guangzhou 510006, China.
J Hazard Mater. 2021 Apr 15;408:124818. doi: 10.1016/j.jhazmat.2020.124818. Epub 2020 Dec 11.
d-g-CN-Fe composites was prepared via a self-assembly and calcination process. According to measurements and density functional theory (DFT) computations, the complexation of iron and pyridinic N of g-CN (Fe‒N) occurred with Fe(III)-π interaction, causing more oxygen vacancies (OVs) with more electrons in iron oxides. In the catalyst air-saturated suspension, the adsorbed pollutants complexed surface Fe(III) through their hydroxyl group donated electrons to around OVs, reducing the surface Fe(III) to Fe(II) and were destructed by Fe(III)-π interaction of the complexation. The addition of HO mainly acted as acceptor being reduced OH at the OV centers, causing higher degradation rate of pollutants due to both OH and the surface reaction. However, for the adsorbed hydrophobic pollutants onto the sites of peripheral structure in g-CN, HO was mainly decomposed into O by the synergistic effect of iron species and OVs. Therefore, the catalyst exhibited high Fenton-like efficiency for the degradation of hydroxyl-containing pollutants and hydrophobic pollutants mixing with the former. Our results demonstrate that the Fe(III)-π interaction could carry out the oxidation of pollutants on the catalyst surface, decreasing the consumption of HO, and the role of OVs depends on pollutant adsorption patterns.
通过自组装和煅烧过程制备了 d-g-CN-Fe 复合材料。根据测量和密度泛函理论 (DFT) 计算,铁与 g-CN 的吡啶氮 (Fe-N) 发生了 Fe(III)-π 相互作用,导致铁氧化物中具有更多的氧空位 (OVs) 和更多的电子。在催化剂饱和空气悬浮液中,吸附的污染物通过其羟基与表面 Fe(III) 络合,将电子转移到周围的 OVs 中,将表面 Fe(III)还原为 Fe(II),并通过络合的 Fe(III)-π 相互作用被破坏。HO 的添加主要作为接受体,在 OV 中心还原 OH,由于 OH 和表面反应,导致污染物的降解率更高。然而,对于吸附在 g-CN 外围结构位上的疏水性污染物,HO 主要通过铁物种和 OVs 的协同作用分解为 O。因此,该催化剂对含羟基污染物和疏水性污染物的混合降解表现出高类芬顿效率。我们的结果表明,Fe(III)-π 相互作用可以在催化剂表面进行污染物的氧化,减少 HO 的消耗,而 OVs 的作用取决于污染物的吸附模式。