研究目的
To develop a noble metal-free photocatalyst with full solar spectrum light response for efficient photocatalytic removal of aqueous nitrite with high N2 selectivity.
研究成果
The PANI@W18O49 composite exhibits superior photocatalytic activity and high N2 selectivity for nitrite removal under full solar spectrum light, attributed to effective charge separation and suitable redox levels. The catalyst is stable over multiple cycles and offers a noble metal-free alternative for environmental applications.
研究不足
The photocatalytic performance is pH-dependent, with optimal activity at low pH (3.0), which may not be practical for all wastewater treatments. The study uses simulated solar light and may not fully replicate natural conditions. The stability over long-term use and scalability for industrial applications are not extensively tested.
1:Experimental Design and Method Selection:
The study involved synthesizing PANI@W18O49 composite via a facile solvent evaporation method to enhance photocatalytic activity. Theoretical models focused on the built-in junction between n-type W18O49 and p-type PANI for improved charge separation.
2:Sample Selection and Data Sources:
Samples included pure W18O49, PANI, and PANI@W18O49 composites with different weight ratios (1 wt%, 3 wt%, 7 wt%). Data were collected from photocatalytic experiments under various light sources.
3:List of Experimental Equipment and Materials:
Equipment included XRD (JEOLJDX 8030), Raman (Labram HR800), FTIR (Magna-IR 750), SEM (Zeiss Merlin), TEM (TecnaiG2F20), UV–vis DRS (Hitachi U4100), PL (FLS 980), ion chromatograph (ICS-1000, Dionex), UV–vis spectrophotometer (TU-1810), and light sources (300 W Xe lamp, 200 W mercury lamp, 200 W infrared lamp). Materials included WCl6, aniline, APS, THF, sodium nitrite, and organic acids.
4:Experimental Procedures and Operational Workflow:
Synthesis of W18O49 via solvothermal method, PANI via polymerization, and PANI@W18O49 via solvent evaporation. Photocatalytic tests involved stirring catalyst suspensions in nitrite solution under dark for adsorption equilibrium, followed by irradiation with light sources. Samples were periodically withdrawn, filtered, and analyzed for nitrite, nitrate, and ammonium concentrations.
5:Data Analysis Methods:
Data were analyzed using pseudo-first-order kinetics for reaction rates, and N2 selectivity was calculated based on concentration changes. Statistical analysis included comparison of different catalysts and conditions.
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X-ray diffractometer
JEOLJDX 8030
JEOL
Characterization of crystal structure via XRD analysis
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Scanning electron microscope
Zeiss Merlin
Zeiss
Morphological analysis via SEM imaging
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Transmission electron microscope
TecnaiG2F20
FEI
Detailed structural analysis via TEM imaging
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UV–vis spectrophotometer
Hitachi U4100
Hitachi
Optical absorption analysis via UV–vis DRS
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Fluorescence spectrophotometer
FLS 980
Edinburgh Instruments
Photoluminescence analysis via PL spectroscopy
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Raman spectrometer
Labram HR800
Horiba
Analysis of molecular structure via Raman spectroscopy
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FTIR spectrometer
Magna-IR 750
Nicolet
Identification of functional groups via FTIR spectroscopy
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Ion chromatograph
ICS-1000
Dionex
Analysis of nitrate and nitrite concentrations
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UV–vis spectrophotometer
TU-1810
Persee
Analysis of ammonium concentrations using Nessler's method
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Xenon lamp
300 W
Simulated solar light source for photocatalytic experiments
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Mercury lamp
200 W
UV light source for photocatalytic experiments
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Infrared lamp
200 W
NIR light source for photocatalytic experiments
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