School of Chemical Engineering, The University of New South Wales, Sydney, NSW, 2052, Australia.
Department of Chemical Engineering, Sharif University of Technology, Tehran, 11155, Iran.
Chemosphere. 2023 Oct;337:139282. doi: 10.1016/j.chemosphere.2023.139282. Epub 2023 Jun 20.
Removal of Metronidazole (MNZ) and Oxytetracycline (OTC) from wastewater by the prepared (C, N codoped)-TiO/g-CN (Graphitic carbon nitride) was examined. l-Arginine (C, N codoped)-TiO and l-Arginine (C, N codoped)-TiO/g-CN photocatalysts were successfully synthesized through the sol-gel method, and optimal ratio of l-arginine:TiO, as well as l-arginine/TiO:g-CN, was determined by a kinetic study of photodegradation process. The maximum photocatalytic removal rate (0.062 min for MNZ removal) was observed using 1% l-Arginine-TiO/g-CN (1:1) under visible light illumination, 2.2 and 12.4 times greater than those of 1% l-Arginine-TiO and pure TiO, respectively. l-Arginine (1%)-TiO/g-CN (1:1) (co-doped-TCN) was investigated using X-ray diffraction analysis (XRD), Field Emission Scanning Electron Microscopy (FESEM), Energy Dispersive X-ray (EDX), Photo-luminescence (PL), and Differential Reflectance Spectroscopy (DRS) as the best-performing photocatalyst. Response surface methodology (RSM) was used to study the effect of co-doped-TCN dosage (0.5-1.0 g/L), pH of simulated wastewater (4-10), initial concentration of MNZ and OTC (50-100 mg/L), and irradiation time (30-90 min for MNZ and 20-40 min for OTC) on removal efficiency of the antibiotics. Also, their optimum values were determined by RSM. The treated pharmaceutical wastewater showed high biodegradability features with 5-day biological oxygen demand/chemical oxygen demand (BOD/COD) of 0.51 and 0.46 after 40 and 100 min reaction for OTC and MNZ, respectively. The order of reactive species responsible for the photodegradation of pollutants was •O> •OH > h>O. The effect of inorganic anions showed that all anions decreased the removal efficiency of both antibiotics in order of NO> Cl >SO>HPO >HCO for MNZ and NO> SO > Cl >HPO >HCO for OTC. Also, introducing different oxidants improved the photocatalytic removal efficiency with the order of HO>KSO> KBrO.
用制备的(C、N 共掺杂)-TiO/g-CN(石墨相氮化碳)研究了废水 中甲硝唑(MNZ)和土霉素(OTC)的去除。通过溶胶-凝胶法成功合成了 l-精氨酸(C、N 共掺杂)-TiO 和 l-精氨酸(C、N 共掺杂)-TiO/g-CN 光催化剂,并通过光降解过程的动力学研究确定了 l-精氨酸:TiO 的最佳比例以及 l-精氨酸/TiO:g-CN。在可见光照射下,使用 1%l-精氨酸-TiO/g-CN(1:1)观察到最大光催化去除率(MNZ 去除率为 0.062 min),分别比 1%l-精氨酸-TiO 和纯 TiO 高 2.2 和 12.4 倍。使用 X 射线衍射分析(XRD)、场发射扫描电子显微镜(FESEM)、能量色散 X 射线(EDX)、光致发光(PL)和差示反射光谱(DRS)研究了 l-精氨酸(1%)-TiO/g-CN(1:1)(共掺杂-TCN),作为表现最佳的光催化剂。响应面法(RSM)用于研究共掺杂-TCN 剂量(0.5-1.0 g/L)、模拟废水 pH(4-10)、MNZ 和 OTC 的初始浓度(50-100 mg/L)以及照射时间(MNZ 为 30-90 min,OTC 为 20-40 min)对抗生素去除效率的影响。还通过 RSM 确定了它们的最佳值。处理后的制药废水具有高生物降解性,反应 40 和 100 min 后,OTC 和 MNZ 的 5 天生物需氧量/化学需氧量(BOD/COD)分别为 0.51 和 0.46。负责污染物光降解的反应性物质的顺序为 •O>•OH>h>O。无机阴离子的影响表明,所有阴离子均按 NO>Cl>SO>HPO>HCO 的顺序降低了两种抗生素的去除效率,对于 OTC 则按 NO>SO>Cl>HPO>HCO 的顺序降低了去除效率。此外,引入不同的氧化剂可提高光催化去除效率,顺序为 HO>KSO>KBrO。