研究目的
To improve the adsorption and photocatalytic performance of ZIF-8-derived ZnO under simulated sunlight irradiation by in situ incorporation of Al3+ to form a ternary ZnO/Zn6Al2O9/Al2O3 nanocomposite.
研究成果
The ZnO/Zn6Al2O9/Al2O3 nanocomposite, prepared by in situ Al3+ incorporation in ZIF-8-derived ZnO, exhibits enhanced photocatalytic activity due to higher specific surface area, reduced band gap, and inhibited electron-hole recombination. It achieved a 97.5% degradation rate for high-concentration MO under simulated sunlight, significantly outperforming pure ZnO. This approach offers a simple method to improve MOF-derived nanomaterials for environmental remediation.
研究不足
The study is limited to laboratory-scale experiments with specific conditions; scalability and real-world application under varying environmental factors were not addressed. The use of simulated sunlight may not fully replicate natural conditions. The nanocomposite's performance might be optimized further with different synthesis parameters or additional modifications.
1:Experimental Design and Method Selection:
The study involved synthesizing ZIF-8 and incorporating Al3+ in situ to form ZnO/Zn6Al2O9/Al2O3 nanocomposites, followed by calcination. Various characterization techniques (XRD, SEM, TEM, HRTEM, XPS, UV-Vis DRS, BET, PL) were used to analyze the materials. Photocatalytic activity was evaluated by degrading Methyl Orange (MO) under simulated sunlight irradiation.
2:Sample Selection and Data Sources:
Samples were prepared with different molar ratios of Al/Zn (0, 1, 2). MO solutions of varying concentrations (20-200 mg/L) were used for degradation tests.
3:2). MO solutions of varying concentrations (20-200 mg/L) were used for degradation tests. List of Experimental Equipment and Materials:
3. List of Experimental Equipment and Materials: Chemicals included Zn(NO3)2·6H2O, Al(NO3)3·9H2O, 2-methylimidazole, ammonium hydroxide, anhydrous ethanol, Methyl Orange. Equipment included X-ray diffractometer (Bruker D8 Advance), SEM (Nova Nano230), TEM and HRTEM (JEOL JEM 2010F), XPS (ESCALAB 250Xi), UV-Vis spectrophotometer (UV-2550, Shimadzu), PL spectrometer (Zolix), BET analyzer (ST-08), photocatalytic reactor (Beijing Aulight Lighting Co., Ltd.), xenon lamp (300 W), optical radiometer (ST-85), UV spectrophotometer (UV-2600, Shimadzu).
4:Experimental Procedures and Operational Workflow:
ZIF-8 was synthesized by mixing zinc nitrate and Hmim solutions, aging for 24 hours, centrifuging, washing, and drying. ZnO nanocomposites were obtained by calcination at 500°C for 3 hours. Photocatalytic tests involved dispersing catalyst in MO solution, stirring in dark for 30 minutes for equilibrium, then irradiating with simulated sunlight while stirring, and measuring MO concentration over time.
5:Data Analysis Methods:
Degradation rate was calculated as C/C0. Data were analyzed using standard techniques for XRD, SEM, TEM, XPS, UV-Vis, BET, and PL. Statistical error was within ±5% for photocatalytic measurements.
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Transmission electron microscope
JEM 2010F
JEOL
Imaging and analysis of morphology
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High-resolution transmission electron microscope
JEM-2010
JEOL
High-resolution imaging
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UV-vis spectrophotometer
UV-2550
Shimadzu
Obtaining UV-vis diffuse reflectance spectra
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UV spectrophotometer
UV-2600
Shimadzu
Measuring MO concentration
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X-ray diffractometer
D8 Advance
Bruker
Analysis of crystalline structure
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Scanning electron microscope
Nova Nano230
Observation of surface morphologies
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X-ray photoelectron spectroscopy
ESCALAB 250Xi
Examination of surface elemental chemical states
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Photoluminescence spectrometer
Zolix
Determining electron-hole separation-recombination characteristics
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BET analyzer
ST-08
Determining specific surface area
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Photocatalytic reactor
Beijing Aulight Lighting Co., Ltd.
Carrying out photocatalytic reactions
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Xenon lamp
300 W
Simulated sunlight source
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Optical radiometer
ST-85
Photoelectric Instrument Factory of Beijing Normal University
Measuring luminous intensity
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Water purification system
UHQ II
Elga-Pure
Purifying deionized water
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