研究目的
To design and fabricate novel porous AgBr/Bi24O31Br10 heterojunction composites via a hydrothermal calcination-ion exchange route for enhanced photocatalytic degradation of methylene blue under visible light irradiation.
研究成果
The AB/BOB composites, particularly the 20% ratio, exhibit superior photocatalytic activity and stability due to enhanced charge separation via a Z-scheme mechanism and high surface area. ?OH radicals are key active species. These composites show promise for wastewater treatment applications.
研究不足
The study is limited to laboratory-scale experiments with methylene blue as a model pollutant; scalability to industrial applications and performance with other pollutants were not extensively tested. The ion exchange method may have reproducibility issues, and long-term stability under harsh conditions was not fully evaluated.
1:Experimental Design and Method Selection:
The study employed a hydrothermal calcination-ion exchange route to synthesize AB/BOB composites, with characterization using XRD, XPS, SEM, EDX, UV-vis DRS, BET, and electrochemical measurements. Photocatalytic activity was assessed by degrading methylene blue under visible light.
2:Sample Selection and Data Sources:
Samples included pure AgBr, pure BOB, and AB/BOB composites with mass ratios of 10%, 20%, and 25%. Methylene blue dye was used as the pollutant.
3:5%. Methylene blue dye was used as the pollutant. List of Experimental Equipment and Materials:
3. List of Experimental Equipment and Materials: Materials included bismuth nitrate pentahydrate, sodium hydroxide, silver nitrate, potassium bromide, glucose, ethylene glycol, methylene blue, and deionized water. Equipment included X-ray diffractometer (D/max-2500, Rigaku), FE-SEM (SUAPR55, Zeiss), XPS (Thermo ESCALAB 250XI), UV-vis spectrophotometer (UV-2450, Shimadzu), electrochemical analyzer (CHI660C), BET surface area analyzer (TriStar II 3020, Micromeritics), and a 500 W Xenon lamp.
4:Experimental Procedures and Operational Workflow:
BOB was prepared hydrothermally and calcined. AB/BOB composites were synthesized via ion exchange. Photocatalytic tests involved adding photocatalyst to MB solution, irradiating with visible light, and sampling at intervals to measure degradation. Active species trapping used scavengers like EDTA-2Na, BQ, and IPA.
5:Data Analysis Methods:
Degradation efficiency was calculated using UV-vis spectrometry. Kinetic constants were derived from first-order kinetics. Electrochemical measurements assessed photocurrent responses.
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X-ray diffractometer
D/max-2500
Rigaku
Characterization of crystallographic structures of samples
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FE-SEM
SUAPR55
Zeiss
Acquisition of morphology, microstructure, and EDX spectra
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XPS
Thermo ESCALAB 250XI
Thermo
Measurement of elemental compositions and chemical states
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UV-vis spectrophotometer
UV-2450
Shimadzu
Obtainment of ultraviolet-visible diffuse reflectance spectra
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Electrochemical analyzer
CHI660C
CH Instruments
Conduction of electrochemical measurements
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BET surface area analyzer
TriStar II 3020
Micromeritics
Measurement of BET surface area
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Xenon lamp
500 W
Irradiation source for photocatalytic tests
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