研究目的
To convert water hyacinth (WH) into valuable carbon dots (CDs) via a versatile route and combine CDs with g-C3N4 to produce sunlight-responsive composites for photodegradation of 2,4-dichlorophenol.
研究成果
CDs derived from water hyacinth leaves were successfully combined with g-C3N4 to enhance its photocatalytic properties. The composites showed improved degradation efficiency for 2,4-DCP under sunlight, attributed to prolonged charge carrier lifetime and enhanced light absorption.
研究不足
The study focuses on the degradation of 2,4-DCP under sunlight irradiation. The applicability of the composites for other pollutants or under different light sources was not explored.
1:Experimental Design and Method Selection
CDs were derived from water hyacinth leaves via hydrothermal treatment and combined with g-C3N4 to form composites. The photocatalytic performance was evaluated under natural sunlight irradiation.
2:Sample Selection and Data Sources
Water hyacinth leaves were used as the green source for CDs synthesis. The photocatalytic degradation of 2,4-DCP was monitored using HPLC.
3:List of Experimental Equipment and Materials
Field emission scanning electron microscope (FESEM, Auriga, Zeiss), high resolution transmission electron microscope (HRTEM, Tecnai 20, Philips), X-ray diffractometer (XRD, D8 Advance, Bruker), X-ray photoelectron spectroscopy (XPS, Axis Ultra DLD, Kratos), Fourier transform infrared (FTIR) spectra (Perkin Elmer Spectrum 400), Ultraviolet–visible diffuse reflectance spectra (UV–vis DRS, UV-260, SHIMADZU), Brunauer–Emmett–Teller (BET) surface area analyzer (TriStar II 3020, Micrometrics?), Photoluminescence (PL) spectrophotometer (Perkin Elmer LS 55), Time Resolved Photoluminescence (TRPL, Edinburgh FLS 920).
4:Experimental Procedures and Operational Workflow
CDs were synthesized from WH leaves via hydrothermal treatment. The composites were prepared by mixing g-C3N4 with CDs solution and undergoing hydrothermal treatment. Photocatalytic experiments were conducted under natural sunlight.
5:Data Analysis Methods
The degradation rate was calculated using a first-order kinetic model. The active species in the photocatalytic process were identified using scavenger tests.
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X-ray diffractometer
D8 Advance
Bruker
Identification of crystalline phase
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X-ray photoelectron spectroscopy
Axis Ultra DLD
Kratos
Analysis of surface chemical composition
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Fourier transform infrared spectrophotometer
Spectrum 400
Perkin Elmer
Obtaining FTIR spectra of products
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Ultraviolet–visible diffuse reflectance spectrophotometer
UV-260
SHIMADZU
Performing UV–vis DRS
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Photoluminescence spectrophotometer
LS 55
Perkin Elmer
Acquisition of PL spectra of CDs solution
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Time Resolved Photoluminescence
FLS 920
Edinburgh
Acquisition of TRPL spectrum and exciton decay lifetime
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Field emission scanning electron microscope
Auriga
Zeiss
Observation of morphological structure and composition of CDs/g-C3N4
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High resolution transmission electron microscope
Tecnai 20
Philips
Observation of morphological structure at high resolution
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Brunauer–Emmett–Teller surface area analyzer
TriStar II 3020
Micrometrics?
Measurement of BET surface area based on nitrogen adsorption–desorption isotherms
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