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Frontiers of Environmental Science & Engineering

ISSN 2095-2201

ISSN 2095-221X(Online)

CN 10-1013/X

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Front. Environ. Sci. Eng.    2024, Vol. 18 Issue (4) : 44    https://doi.org/10.1007/s11783-024-1804-7
RESEARCH ARTICLE
Enhanced Fenton-like process over Cu/L(+)-ascorbic acid co-doping mesoporous silica for toxicity reduction of emerging contaminants
Yuhang Liu, Wenxuan Deng, Xiaojun Wu, Chun Hu, Lai Lyu()
Key Laboratory for Water Quality and Conservation of the Pearl River Delta (Ministry of Education), Institute of Environmental Research at Greater Bay, Guangzhou University, Guangzhou 510006, China
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Abstract

● Cu-C-MSNs are developed via a co-doping step of Cu with L(+)-ascorbic acid.

● Cu-C-MSNs show superb performance in removing contaminants and purifying wastewater.

● The performance is owing to the polarization electric field and cation-π structures.

● The biological toxicity of bisphenol A is considerably weakened after the reaction.

Effective removal of emerging contaminants (ECs) to minimize their impacts on human health and the natural environment is a global priority. For the removal of ECs in water, we fabricated a seaweed spherical microsphere catalyst with Cu cation-π structures by in situ doping of Cu species and ascorbic acid in mesoporous silica (Cu-C-MSNs) via a hydrothermal method. The results indicate that bisphenol A (BPA) is substantially degraded within 5 min under natural conditions, with its biological toxicity considerably weakened. Moreover, industrial wastewater could also be effectively purified by Cu-C-MSNs/H2O2 system. The presence of metal sites and the complexation of ECs via cation-π interaction and π-π stacking on the catalyst surface were directly responsible for the polarization distribution of electrons, thus activating H2O2 and dissolved oxygen (DO). The removal of contaminants could be attributed primarily to 1) the activation of H2O2 into OH to attack the contaminants and 2) self-cleavage because of the transfer of electrons from the contaminants to the catalysts. This study provides an innovative solution for the effective treatment of ECs and has positive implications for easing global environmental crises.

Keywords Cation-π structures      Polarization electric field      Fenton-like process      Contaminants cleavage     
Corresponding Author(s): Lai Lyu   
Issue Date: 15 December 2023
 Cite this article:   
Yuhang Liu,Wenxuan Deng,Xiaojun Wu, et al. Enhanced Fenton-like process over Cu/L(+)-ascorbic acid co-doping mesoporous silica for toxicity reduction of emerging contaminants[J]. Front. Environ. Sci. Eng., 2024, 18(4): 44.
 URL:  
https://academic.hep.com.cn/fese/EN/10.1007/s11783-024-1804-7
https://academic.hep.com.cn/fese/EN/Y2024/V18/I4/44
Fig.1  (a) Preparation process of Cu-C-MSNs. (b) and (c) SEM images of Cu-C-MSNs. (d) and (e) TEM images of Cu-C-MSNs. (f) Element mapping of O, Si, Cu and C from SEM images.
Fig.2  (a) XRD patterns of C-SiO2 NSs and Cu-C-MSNs. (b) FT-IR spectra of Cu-C-MSNs. XPS orbit spectrum of Cu-C-MSNs and SiO2 NSs in (c) Cu 2p3/2, (d) Si 2p, (e) O 1s.
Fig.3  (a) Degradation of BPA in the Cu-C-MSNs, C-SiO2, Cu-MSNs system with H2O2. (b) The catalytic effect of different contaminants. (c) Reusability of Cu-C-MSNs for BPA degradation. (d) Excitation-Emission-Matrix Spectra of printing and dyeing wastewater. (e) Wastewater after 120 min of degradation of Cu-C-MSNs/H2O2 system. (f) Wastewater after 180 min of degradation of Cu-C-MSNs/H2O2 system. Reaction conditions: [catalyst] = 1.0 g/L, [H2O2] = 0.01 mol/L, [BPA] =0.01 g/L, t = 35 °C.
Fig.4  (a) The catalytic effect of different catalyst dosages for degradation of BPA. (b) The catalytic effect of different H2O2 concentrations for degradation of BPA. (c) The catalytic effect of different BPA concentrations. (d) Degradation of BPA in the range pH = 5–9. (e) Influence of different anions (10 mmol/L) in degrading BPA. (f) The catalytic effect of different HA concentrations for degradation of BPA. Reaction conditions: [Catalyst] = 1.0 g/L, [H2O2] = 0.01 mol/L, [BPA] = 0.01 g/L, t = 35 °C.
Fig.5  (a) BMPO trapped ?OH in various aqueous. (b) BMPO trapped O2?? various aqueous. (c) BPA degradation curves in Cu-C-MSNs/H2O2 system in the presence of TBA (?OH quenching agent) and BQ (O2?? quenching agent). (d) Schematic illustration of H2O2/O2 activation and contaminants conversion.
Fig.6  (a) Proposed degradation pathways in the Cu-C-MSNs system. (b) Fathead minnow LC50 (96 h), (c) Daphnia magna LC50 (48 h), and (d) Developmental toxicity of BPA and its degradation intermediates.
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