School of Environmental Science and Engineering, Guangdong Provincial Key Lab of Environmental Pollution Control and Remediation Technology, Sun Yat-sen University, Guangzhou 510006, PR China.
School of Environmental Science and Engineering, Guangdong Provincial Key Lab of Environmental Pollution Control and Remediation Technology, Sun Yat-sen University, Guangzhou 510006, PR China.
Environ Int. 2020 Oct;143:105899. doi: 10.1016/j.envint.2020.105899. Epub 2020 Jul 3.
Reactive oxygen species (ROS) production for Fe is limited because of the formed iron corrosion products. In this study, C/FeC/Fe composite which produces enhanced ROS has been specifically designed and fabricated to remove typical antibiotics (i.e., oxytetracycline (OTC) and chloramphenicol (CAP)) as a heterogeneous Fenton-like catalyst. The C/FeC/Fe composite demonstrated excellent performance for both OTC and CAP removal as compared with Fe and biochar. Furthermore, X-ray photoelectron spectrometry, Fourier transform infrared spectrometry, high performance liquid chromatography-mass spectra and electron spin resonance analyses were conducted to elucidate the adsorption and degradation mechanisms. The adsorption of OTC and CAP was mainly dominated by H bonds and the electron-acceptor-acceptor on the surface of the C/FeC/Fe composite, respectively. In particular, OH simultaneously induced the degradation of OTC and CAP, while O presented the selective oxidation to OTC. More specifically, the degradation of OTC over C/FeC/Fe was stronger and faster than that of CAP, leading to 65.84% and 16.84% of removal efficiency for OTC and CAP, respectively. Furthermore, C/FeC/Fe exhibited superior reusability and stability after regeneration, but regenerated Fe almost lost its reactivity. Therefore, the efficiency in situ generation of O using C/FeC/Fe would shed new light on the selective oxidation of aqueous organic compounds.
活性氧 (ROS) 的产生受到限制,因为形成了铁腐蚀产物。在这项研究中,专门设计并制造了 C/FeC/Fe 复合材料,以作为非均相类芬顿催化剂来去除典型抗生素(即土霉素 (OTC) 和氯霉素 (CAP))。与 Fe 和生物炭相比,C/FeC/Fe 复合材料在去除 OTC 和 CAP 方面表现出优异的性能。此外,还进行了 X 射线光电子能谱、傅里叶变换红外光谱、高效液相色谱-质谱和电子顺磁共振分析,以阐明吸附和降解机制。OTC 和 CAP 的吸附主要由 C/FeC/Fe 复合材料表面的 H 键和电子受体-受体主导。特别是,OH 同时诱导 OTC 和 CAP 的降解,而 O 则表现出对 OTC 的选择性氧化。更具体地说,OTC 在 C/FeC/Fe 上的降解比 CAP 更强且更快,导致 OTC 和 CAP 的去除效率分别为 65.84%和 16.84%。此外,C/FeC/Fe 在再生后表现出优异的可重复使用性和稳定性,但再生后的 Fe 几乎失去了反应活性。因此,使用 C/FeC/Fe 原位生成 O 的效率将为水中有机化合物的选择性氧化提供新的思路。