Collaborative Innovation Center for Advanced Nuclear Energy Technology, INET, Tsinghua University, Beijing 100084, P. R. China.
College of Chemistry and Materials Science, Sichuan Normal University, Chengdu, Sichuan 610068, P. R. China.
Environ Sci Technol. 2020 Aug 18;54(16):10361-10369. doi: 10.1021/acs.est.0c03256. Epub 2020 Jul 28.
Graphite carbon nitride (g-CN) has a stable structure but poor catalytic capability for activating peroxymonosulfate (PMS). In this study, the codoping of g-CN with bimetallic oxides (iron and cobalt) and oxygen was investigated to enhance its catalytic capability. The results showed that iron, cobalt, and oxygen codoped g-CN (Fe-Co-O-g-CN) was successfully prepared, which was capable of completely degrading sulfamethoxazole (SMX) (0.04 mM) within 30 min, with a reaction rate of 0.085 min, indicating the superior catalytic activity of Fe-Co-O-g-CN. The mineralization efficiency of SMX was 22.1%. Sulfate radicals and singlet oxygen were detected during the process of PMS activation. However, the role that singlet oxygen played in degrading SMX was not obvious. Surface-bound reactive species and sulfate radicals were responsible for SMX degradation, in which sulfate radicals contributed to 46.6% of SMX degradation. The superior catalytic activity was due to the synergistic effect of metal oxides and O-g-CN, in which O-g-CN could act as a carrier and an activator as well as an electron mediator to promote the conversion of Fe(III) to Fe(II) and Co(III) to Co(II). Four main steps of SMX degradation were proposed, including direct oxidation of SMX, bond fission of N-C, bond fission of N-S, and bond fission of S-C. The effect of the pH, temperature, PMS concentration, chloridion, bicarbonate, and humic acids on SMX degradation was investigated. Cycling experiments demonstrated the good stability of Fe-Co-O-g-CN. This study first reported the preparation of bimetallic oxide and oxygen codoped g-CN, which was an effective PMS activator for degradation of toxic organic pollutants.
石墨相氮化碳(g-CN)具有稳定的结构,但对于激活过一硫酸盐(PMS)的催化能力较差。在这项研究中,研究了双金属氧化物(铁和钴)和氧共掺杂 g-CN 以提高其催化能力。结果表明,成功制备了铁、钴和氧共掺杂 g-CN(Fe-Co-O-g-CN),它能够在 30 分钟内完全降解磺胺甲恶唑(SMX)(0.04mM),反应速率为 0.085 min,表明 Fe-Co-O-g-CN 具有优异的催化活性。SMX 的矿化效率为 22.1%。在 PMS 激活过程中检测到了硫酸盐自由基和单线态氧。然而,单线态氧在降解 SMX 中的作用并不明显。表面结合的反应性物质和硫酸盐自由基是 SMX 降解的原因,其中硫酸盐自由基对 SMX 降解的贡献为 46.6%。优异的催化活性是由于金属氧化物和 O-g-CN 的协同作用,其中 O-g-CN 可以作为载体和激活剂以及电子介体来促进 Fe(III)向 Fe(II)和 Co(III)向 Co(II)的转化。提出了 SMX 降解的四个主要步骤,包括 SMX 的直接氧化、N-C 键的断裂、N-S 键的断裂和 S-C 键的断裂。研究了 pH、温度、PMS 浓度、氯离子、碳酸氢根和腐殖酸对 SMX 降解的影响。循环实验证明了 Fe-Co-O-g-CN 的良好稳定性。本研究首次报道了双金属氧化物和氧共掺杂 g-CN 的制备,它是一种有效的 PMS 激活剂,可用于降解有毒有机污染物。