过氧二硫酸盐
降级(电信)
石墨烯
化学
氧化物
过程(计算)
四环素
环境化学
化学工程
材料科学
生物化学
计算机科学
纳米技术
工程类
抗生素
有机化学
催化作用
操作系统
电信
作者
Yuan Ouyang,Meifang Li,Chunfang Tang,Shiyu Song,Hui Wang,Chenxi Huang,Haoxiang Zhong,Jian Hua Zhu,Xiaodong Ji,Hao Xu,Zhangkai Chen,Zhiming Liu
标识
DOI:10.1016/j.envres.2024.119621
摘要
Atom-dispersed low-coordinated transition metal-N x catalysts exhibit excellent efficiency in activating peroxydisulfate (PDS) for environmental remediation. However, their catalytic performance is limited due to metal-N coordination number and single-atom loading amount. In this study, low-coordinated nitrogen-doped graphene oxide (GO) confined single-atom Mn catalyst (Mn-SA/NGO) was synthesized by molten salt-assisted pyrolysis and coupled to PDS for degradation of tetracycline (TC) in water. Aberration-corrected high-angle annular dark-field scanning transmission electron microscopy (AC-HAADF-STEM) and X-ray absorption fine structure spectroscopy (XAFS) analysis showed the successful doping of single-atom Mn (weight percentage 1.6%) onto GO and the formation of low-coordinated Mn–N 2 sites. The optimized parameters obtained by Box-Behnken Design achieved 100% TC removal in both prediction and experimental results. The Mn-SA/NGO + PDS system had strong anti-interference ability for TC removal in the presence of anions. Besides, Mn-SA/NGO possessed good reusability and stability. O 2 •− , •OH, and 1 O 2 were the main active species for TC degradation, and the TC mineralization reached 85.1%. Density functional theory (DFT) calculations confirmed that the introduction of single atoms Mn could effectively enhance adsorption and activation of PDS. The findings provide a reference for the synthesis of high-performance single-atom catalysts for effective removal of antibiotics. • Low-coordinated Mn–N 2 sites was successfully loaded on GO. • TC was almost completely removed with a mineralization rate of 85.1%. • Mn-SA/NGO has a wide pH adaptation range and strong anti-interference ability. • Adsorption and activation of Mn-SA/NGO was easier by DFT calculation. • O 2 . •− , •OH, and 1 O 2 were the main active species for TC degradation.
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