研究目的
To investigate the effect of dissolved natural organic matter (NOMs) on the photocatalytic micropollutant removal performance of TiO2 nanotube array (TNA), specifically for 4-chloro-2-methylphenoxyacetic acid (MCPA), and to study the influences of pH and co-existing inorganic anions.
研究成果
NOMs generally inhibit MCPA removal by TNA due to surface interactions, but acidic pH and certain anions (phosphate and bicarbonate) mitigate this effect by reducing h+ scavenging and competitive adsorption. Alkaline pH eliminates the inhibitory effect and enhances removal via photosensitization. The findings provide insights for optimizing TNA-based water treatment in complex environments.
研究不足
The study focuses on specific NOM types (SWR-NOM and UMR-NOM) and one micropollutant (MCPA); results may not generalize to other contaminants or water matrices. The experimental conditions (e.g., fixed light intensity, specific anion concentrations) might not cover all real-world scenarios. Optimization of TNA fabrication and scaling for practical applications are not addressed.
1:Experimental Design and Method Selection:
The study used a photocatalytic degradation setup with TNA as the catalyst and UV-LED light source to investigate the removal of MCPA in the presence of NOMs, varying pH and anion concentrations. Theoretical models include photocatalytic principles involving electron-hole pair generation and reactive oxidative species.
2:Sample Selection and Data Sources:
MCPA was used as the model micropollutant. NOMs (SWR-NOM and UMR-NOM) were obtained from IHSS. Water samples were prepared using ultrapure water from a Milli-Q system.
3:List of Experimental Equipment and Materials:
Titanium foil, chemicals (e.g., ammonium sulphate, MCPA), NOMs, UV-LED light source, crystallizing dish, power supply, SEM/EDX for characterization, LC-MS/MS for analysis, photocurrent measurement setup.
4:Experimental Procedures and Operational Workflow:
TNA was fabricated via electrochemical anodization, annealed, and characterized. Photocatalytic experiments involved placing TNA in reaction solution with MCPA and NOMs, irradiating with UV-LED for 120 min, sampling at intervals, and analyzing MCPA concentration. pH was adjusted using HCl or NaOH. Photocurrent measurements were conducted to study surface processes.
5:Data Analysis Methods:
MCPA concentration was measured using LC-MS/MS. Photocurrent decay was analyzed with a double-exponential model. Statistical analysis included duplicate experiments and curve fitting.
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Scanning electron microscope
JSM 6480
JEOL
Characterizes the surface morphology of the TiO2 nanotube array.
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X-ray diffractometer
D8 advanced
Bruker
Confirms the crystallographic phases of the TNA through XRD analysis.
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Radiant power meter
S150C
THORLABS
Measures the radiant power of the UV-LED light source.
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LC-MS/MS system
infinity 1260 LC-system with 6420 triple Quadrupole Mass Spectrometer
Agilent
Measures the concentration of MCPA in samples using liquid chromatography-mass spectrometry.
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Titanium foil
Titaniumshop
Used as the base material for fabricating TiO2 nanotube arrays via anodization.
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Milli-Q Advantage A10 system
Advantage A10
Merck Millipore
Produces ultrapure water for preparing stock solutions and reaction mixtures.
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EST150 DC power supply
EST150
Delta Elektronika
Provides DC power for electrochemical anodization during TNA fabrication.
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Furnace
Nabertherm
Used for annealing the anodized titanium foil to crystallize the TiO2 nanotube array.
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Raman spectrometer
LabRAM
Horiba
Records Raman spectra to analyze the crystallographic phases of the TNA.
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UV-LED light source
NCSU033B
NICHIA
Provides UV irradiation at 365 nm for photocatalytic experiments.
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