研究目的
Investigating the synergistic mechanism between Co and N codoped porous carbons for enhanced heterogeneous activation of peroxymonosulfate (PMS) for the degradation of organic pollutants.
研究成果
Codoping of Co and N into carbon generated the synergistic effect towards PMS activation to produce the sulfate radical, and the catalytic performance of Co–N-PC was greatly enhanced with the increase of Co–Nx sites. The activity of Co–N-PC even outperformed that of the best PMS catalyst (homogeneous Co2+) and the state-of-the-art PMS catalysts. The doped Co and N, which enhanced the electron-donating ability and PMS adsorption capacity of carbon, respectively, synergistically contributed to the enhanced PMS activation on carbon.
研究不足
The catalytic performance of Co–N-PC was not continuously enhanced by simply increasing the Co or N content. The performance decline mainly originates from the coverage of organic acid on its surface.
1:Experimental Design and Method Selection:
Co and N codoped porous carbons (Co–N-PCs) were constructed for enhanced PMS activation. The Co doping level was varied to study the role of Co in Co–N-PCs.
2:Sample Selection and Data Sources:
Phenol, bisphenol A, atrazine, and sulfamethoxazole were chosen to investigate the catalytic efficiency of Co–N-PCs.
3:List of Experimental Equipment and Materials:
Field emission scanning electron microscope (SEM, HitachiS-4800), transmission electron microscope (TEM, FEI-Tecnai G220), energy dispersive spectroscope (EDS, X-Max50), Raman spectra (Renishaw Micro-Raman system 2000 spectrometer), X-ray photoelectron spectroscopy (XPS, VG ESCALAB 250 spectrometer), inductively coupled plasma-atomic emission spectroscopy (ICP-AES, Optima 2000 DV), N2 adsorption–desorption isotherms (Quadrasorb instrument), Fourier transform infrared spectroscopy (FTIR, Vertex 70 spectrometer), electrochemical impedance spectroscopy (EIS, CHI660D, Shanghai Chenhua Ltd., China).
4:Experimental Procedures and Operational Workflow:
The catalytic performance of Co–N-PC was tested in a 50 mL beaker at ambient temperature.
5:Data Analysis Methods:
The pseudo-first-order kinetic constants of phenol degradation for Co–N-PCs were calculated.
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Field emission scanning electron microscope
HitachiS-4800
Hitachi
Observation of morphologies of Co–N-PCs
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Transmission electron microscope
FEI-Tecnai G220
FEI
Observation of morphologies of Co–N-PCs
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Energy dispersive spectroscope
X-Max50
Not provided
Examination of element distribution on Co–N-PCs
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Raman spectra
Renishaw Micro-Raman system 2000 spectrometer
Renishaw
Investigation of the graphitization degree of Co–N-PCs
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X-ray photoelectron spectroscopy
VG ESCALAB 250 spectrometer
VG
Measurement of the element distribution of Co–N-PCs
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Inductively coupled plasma-atomic emission spectroscopy
Optima 2000 DV
Not provided
Determination of the Co content
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N2 adsorption–desorption isotherms
Quadrasorb instrument
Not provided
Testing of the specific surface area and pore structure of Co–N-PCs
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Fourier transform infrared spectroscopy
Vertex 70 spectrometer
Not provided
Study of the interaction between PMS and carbon-based catalysts
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Electrochemical impedance spectroscopy
CHI660D
Shanghai Chenhua Ltd.
Analysis of the electron-donating capability of different carbon-based catalysts
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