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Peer-reviewedCC BY 4.0Catalysts

Boron-Accelerated Fe3+/Fe2+ Recycling Enhances Periodate Activation for Sulfamethazine Degradation

4 affiliations
  1. 1Nanjing Institute of Environmental Sciences, Ministry of Ecology and Environment, Nanjing 210042, China
  2. 2Hangzhou Environmental Protection & Scientific Research Design Co., Ltd., Hangzhou 310000, China
  3. 3Zhejiang Huanyao Environmental Construction Co., Ltd., Hangzhou 310000, China
  4. 4College of Ecology and Environment, Nanjing Forestry University, Nanjing 210037, China

Abstract

Elemental boron, an eco-friendly and cost-effective metalloid reductant, was employed as a reductive co-catalyst to accelerate Fe3+/Fe2+ redox cycling in Fe2+-initiated periodate (PI) activation for sulfamethazine (SMT) degradation. The standalone Fe2+/PI system achieved only 24.1% SMT elimination within 30 min, whereas the constructed B/Fe2+/PI system delivered up to 97.7% removal under an extremely low iron dosage (10 μM Fe2+) and acidic condition (pH 3.0). Radical quenching assays combined with molecular probe identification revealed the co-existence of Fe(IV), •OH, 1O2, O2•−, and IO3•−, with •OH, among which •OH was identified as the dominant oxidant, and its generation was notably amplified by boron. X-ray photoelectron spectroscopy (XPS) characterization demonstrated that surface B-B bonds and low-valent boron moieties act as electron donors to reduce Fe3+ to Fe2+, sustaining continuous Fe3+/Fe2+ redox turnover. Eight transformation intermediates were identified by mass spectrometry, based on which plausible degradation pathways for SMT were proposed. The B/Fe2+/PI system exhibited robust tolerance against prevalent inorganic anions, maintained favorable catalytic capability in natural lake water, and preserved stable performance across five successive recycling runs. Accordingly, boron-augmented Fe2+-triggered periodate activation represents a promising low-iron technical paradigm for antibiotic remediation in water environments.

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BibTeX
@article{bu2026boronaccelerated,
  title = {{Boron-Accelerated Fe3+/Fe2+ Recycling Enhances Periodate Activation for Sulfamethazine Degradation}},
  author = {Zhuoyu Bu and Nanhao Xu and Wei Wang and Shang Gao and Yuwei Pan},
  journal = {Catalysts},
  year = {2026},
  month = nov,
  doi = {10.3390/catal16110988},
  url = {https://www.mdpi.com/2073-4344/16/11/988},
  note = {CC BY 4.0},
}
RIS
TY  - JOUR
TI  - Boron-Accelerated Fe3+/Fe2+ Recycling Enhances Periodate Activation for Sulfamethazine Degradation
AU  - Zhuoyu Bu
AU  - Nanhao Xu
AU  - Wei Wang
AU  - Shang Gao
AU  - Yuwei Pan
PY  - 2026
DA  - 2026/11/06
JO  - Catalysts
DO  - 10.3390/catal16110988
UR  - https://www.mdpi.com/2073-4344/16/11/988
AB  - Elemental boron, an eco-friendly and cost-effective metalloid reductant, was employed as a reductive co-catalyst to accelerate Fe3+/Fe2+ redox cycling in Fe2+-initiated periodate (PI) activation for sulfamethazine (SMT) degradation. The standalone Fe2+/PI system achieved only 24.1% SMT elimination within 30 min, whereas the constructed B/Fe2+/PI system delivered up to 97.7% removal under an extremely low iron dosage (10 μM Fe2+) and acidic condition (pH 3.0). Radical quenching assays combined with molecular probe identification revealed the co-existence of Fe(IV), •OH, 1O2, O2•−, and IO3•−, with •OH, among which •OH was identified as the dominant oxidant, and its generation was notably amplified by boron. X-ray photoelectron spectroscopy (XPS) characterization demonstrated that surface B-B bonds and low-valent boron moieties act as electron donors to reduce Fe3+ to Fe2+, sustaining continuous Fe3+/Fe2+ redox turnover. Eight transformation intermediates were identified by mass spectrometry, based on which plausible degradation pathways for SMT were proposed. The B/Fe2+/PI system exhibited robust tolerance against prevalent inorganic anions, maintained favorable catalytic capability in natural lake water, and preserved stable performance across five successive recycling runs. Accordingly, boron-augmented Fe2+-triggered periodate activation represents a promising low-iron technical paradigm for antibiotic remediation in water environments.
SN  - 2073-4344
ER  -