4.7 Article

Enhanced norfloxacin degradation by iron and nitrogen co-doped biochar: Revealing the radical and nonradical co-dominant mechanism of persulfate activation

Journal

CHEMICAL ENGINEERING JOURNAL
Volume 420, Issue -, Pages -

Publisher

ELSEVIER SCIENCE SA
DOI: 10.1016/j.cej.2021.129902

Keywords

Persulfate; Catalytic mechanism; Fe@N co-doped biochar; Degradation pathway; Norfloxacin

Funding

  1. National Key R&D Program of China [2019YFC0408500]
  2. National Natural Science Foundation of China [51809068]
  3. Major Science and Technology Projects of Anhui Province [201903a07020009]
  4. Fundamental Research Funds for the Central Universities [JZ2020HGTB0022]
  5. Changfeng County-Hefei University of Technology Industrial Innovation Guidance Fund Key Project
  6. Suzhou Science and Technology Plan Project [2019056]

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The study introduced a novel method using iron and nitrogen co-doped biochar material for the removal of antibiotics in water, showing significant degradation efficiency. Under optimal conditions, rapid degradation of antibiotics was achieved with potential for sustainable reuse through multiple cycles.
The long-term abuse of antibiotics such as norfloxacin (NOR) poses a significant threat to aquatic environments. The development of efficient and economical treatments is still a pain point in the industry. Herein, we reported a directly robust carbonization-pyrolysis method to synthesize iron and nitrogen co-doped biochar material (Fe@N co-doped biochar) that was first applied to NOR removal through persulfate (PS) activation. The catalytic performance and operating factors were systematically investigated. It was found that 10 mg/L NOR achieved 95% degradation within 20 min under optimal reaction conditions. The removal rate of NOR could still achieve 80% and almost 50% of NOR was completely mineralized after five cycles. Through combined electron-paramagnetic-resonance analysis, quenching experiments, and X-ray-photoelectron-spectroscopy tests, center dot OH, center dot SO4-, and O-1(2) were confirmed as reactive oxygen species in catalytic reaction. Iron activated PS to produce center dot OH and center dot SO4- through electron transfer and nitrogen-containing functional groups (graphitic N, C-OH/C = N) accepted electrons from PS to generate O-1(2). The radical pathway involving hydroxyl radicals and the nonradical pathways involving singlet oxygen together accounted for the rapid degradation of NOR. The degradation pathways were comprehensively established, including defluorination, decarboxylation, piperazine ring breakage and nalidixic ring transformation. This study shed light on a new mechanism of radical and nonradical co-dominated PS activation and proposed a simple and inexpensive antibiotic wastewater treatment system.

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