研究目的
Investigating the synthesis, characterization, and visible-light driven photocatalytic activity of a new Ag/AgBr/LaAlO3 plasmonic composite for environmental remediation.
研究成果
The Ag/AgBr/LAO composite exhibited enhanced photocatalytic activity compared with pristine LAO due to its higher surface area, enhanced visible light absorption, and more efficient charge separation. The composite showed excellent stability and can be used as a promising catalyst for environmental remediation.
研究不足
The study focuses on the photocatalytic degradation of MB under visible-light irradiation, and the stability of the composite was tested up to five cycles. Further optimization and application to other pollutants could be explored.
1:Experimental Design and Method Selection
The Ag/AgBr/LAO composite was prepared by deposition of metallic Ag nanoparticles onto the pre-prepared AgBr/LAO heterostructure by visible-light photo-reduction. The photocatalytic degradation of methylene blue (MB) was used as a probe reaction to evaluate their photocatalytic activity under visible-light irradiation.
2:Sample Selection and Data Sources
Pristine LaAlO3 (LAO) was synthesized by a simple and facile gel-burning process, using citric acid and ethylene glycol. The Ag/AgBr/LAO composites were prepared by deposition–precipitation method followed by photo-reduction process.
3:List of Experimental Equipment and Materials
Rigaku MiniFlex 600 x-ray diffractometer, Micromeritics (ASAP 2000) analyzer, FEI Verios scanning electron microscope, JEOL 1010 and JEOL 2010 microscopes, Thermo Scientific K-Alpha spectrometer, JASCO V650 UV–Vis spectrophotometer, JASCO IR-5300 spectrometer, JASCO FP-8500 spectrofluorometer.
4:Experimental Procedures and Operational Workflow
The synthesis involved gel-burning for LAO, deposition–precipitation for AgBr/LAO, and photo-reduction for Ag/AgBr/LAO. Photocatalytic degradation of MB was performed under visible-light irradiation at ambient conditions.
5:Data Analysis Methods
The photocatalytic degradation efficiency was expressed as C/C0, where C is concentration of the MB solution at a certain irradiation time, C0 is the initial concentration of MB solution. The kinetic behavior was studied using pseudo-first-order model.
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FEI Verios scanning electron microscope
Verios
FEI
Surface morphologies determination
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JEOL 1010 instrument
1010
JEOL
Transmission electronic microscopic (TEM) images recording
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JEOL 2010 microscope
2010
JEOL
High-resolution–transmission electronic microscopic (HR-TEM) electron diffraction images and selected-area (SAED) micrographs obtaining
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Thermo Scientific K-Alpha spectrometer
K-Alpha
Thermo Scientific
x-ray photoelectron spectroscopy (XPS) measurements
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JASCO V650 UV–Vis spectrophotometer
V650
JASCO
UV–Vis diffuse reflectance spectra (UV–Vis DRS) performance
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JASCO IR-5300 spectrometer
IR-5300
JASCO
Fourier transform-infrared spectra (FT-IR) recording
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JASCO FP-8500 spectrofluorometer
FP-8500
JASCO
Photoluminescence (PL) spectra measurement
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Rigaku MiniFlex 600 x-ray diffractometer
MiniFlex 600
Rigaku
Phase formation analysis of the samples
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Micromeritics (ASAP 2000) analyzer
ASAP 2000
Micromeritics
Nitrogen adsorption–desorption isotherms measurement
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