研究目的
To develop a highly efficient, low cost, environmental friendly and stable heterojunction composite photo-catalyst for water pollution treatment by enhancing the separation of photo-generated electron-hole pairs and improving photo-catalytic performance.
研究成果
The MoS2/g-C3N4 heterojunction composite exhibits excellent photocatalytic properties due to effective electron-hole separation driven by a built-in electric field, leading to enhanced degradation of pollutants like RhB and Cr6+. This provides a promising, efficient, and stable photocatalyst for environmental applications.
研究不足
The study may have limitations in scalability for industrial applications, potential variability in sample preparation, and the use of simulated sunlight instead of natural conditions. Optimization of mass ratios and long-term stability beyond three cycles could be further investigated.
1:Experimental Design and Method Selection:
The study involved preparing MoS2/g-C3N4 heterojunction composites via a two-step method including hydrothermal synthesis of MoS2 nano-spheres and calcination with melamine to form g-C3N4 coating. Theoretical calculations using DFT were combined with experiments to understand charge transfer mechanisms.
2:Sample Selection and Data Sources:
Samples included pure MoS2, pure g-C3N4, physically mixed MoS2/g-C3N4-P, and heterojunction MoS2/g-C3N4-H with different mass ratios. Chemicals were analytical grade from specified suppliers.
3:List of Experimental Equipment and Materials:
Equipment included XRD diffractometer, FTIR spectrometer, FE-SEM, TEM, XPS spectrometer, UV-Vis spectrophotometer, fluorescence spectrophotometer, electrochemical workstation, TOC analyzer. Materials included ammonium molybdate, thiourea, PVP, melamine, potassium dichromate, sodium oxalate, P-benzoquinone, isopropyl alcohol, Rhodamine B, silver nitrate.
4:Experimental Procedures and Operational Workflow:
MoS2 nano-spheres were synthesized hydrothermally, then coated with melamine, ultrasonically dispersed, stirred, centrifuged, dried, and calcined. Characterization involved XRD, FTIR, SEM, TEM, XPS, UV-Vis, PL, EIS, TOC tests. Photocatalytic measurements were done under simulated sunlight using LED, with degradation of RhB and reduction of Cr6+ monitored by UV-Vis spectrophotometry.
5:Data Analysis Methods:
Data analysis included fitting XRD and XPS peaks, calculating band gaps using Tauc plots, determining kinetic constants using first-order reaction models, and using scavengers to identify active species in photocatalytic processes.
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X-ray diffractometer
Dmax 3C
Rigaku
To obtain X-ray diffraction patterns to determine the structure of samples.
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Fourier transform infrared spectrometer
EQUINOX55
Bruker Optics
To obtain Fourier transform infrared spectra to analyze chemical bonds.
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Field emission scanning electron microscope
SU-8010
Hitachi
To measure morphology and microstructure of samples.
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Transmission electron microscope
TF-20
FEI
To examine microstructure and interface characteristics.
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Fluorescence spectrophotometer
FLS920
Edinburgh
To measure photoluminescence spectra.
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X-ray photoelectron spectrometer
AXIS-ULTRA DLD
To determine composition and chemical states of samples.
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UV-Vis spectrophotometer
Cary 5000
To characterize optical properties and monitor degradation.
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Electrochemical workstation
CHI 760E
To investigate electrochemical impedance spectroscopy.
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TOC analyzer
To perform total organic carbon tests.
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LED
5 W
To provide simulated sunlight for photocatalytic measurements.
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