Journal of Nanomaterials

Journal of Nanomaterials / 2021 / Article

Research Article | Open Access

Volume 2021 |Article ID 9980810 | https://doi.org/10.1155/2021/9980810

Fengyun Guo, Ziyi Guo, Lei Gao, Dongming Qi, Guichu Yue, Nü Wang, Yong Zhao, Ni Li, Jie Xiong, "Electrospun Core-Shell Hollow Structure Cocatalysts for Enhanced Photocatalytic Activity", Journal of Nanomaterials, vol. 2021, Article ID 9980810, 7 pages, 2021. https://doi.org/10.1155/2021/9980810

Electrospun Core-Shell Hollow Structure Cocatalysts for Enhanced Photocatalytic Activity

Academic Editor: Jim Low
Received01 Apr 2021
Revised20 Apr 2021
Accepted09 May 2021
Published25 May 2021

Abstract

The core-shell NaYF4/Yb/Tm/TiO2 hollow composite fibers were prepared by coaxial electrospinning and high-temperature calcination. The composite fibers exhibit excellent photocatalytic activity under the dual synergistic of regulating the core-shell hollow microstructure and the composition by doping nanoparticles. Compared with commercial P25 and hollow fiber without nanoparticles, the degradation efficiency of rhodamine B using the core-shell composite fiber was significantly improved up to 99%. Moreover, the nanoparticles in the composite fibers can exist stably and maintain good structure and photocatalytic activity after repeated use. Therefore, the composite fiber has a wide application prospect in photocatalytic degradation of organic pollutants.

1. Introduction

Water pollution is one of the most serious problems all mankind faced. Providing and sustainably managing water and sanitation for all is one of the sustainable development goals. The UN World Water Development Report proposes to improve waste water management by reducing source pollution, removing waste water pollutants, recycling recycled water, and recovering useful byproducts. With the development of scitech and society, global attention to water pollution control is increasing year by year. Since Fujishima and Honda discovered that TiO2 could be used as an electrode for photodegradation of aquatic hydrogen in 1972 [1], the development of new TiO2-based photocatalytic materials and their application to degradation of organic dyes and other pollutants has become a worldwide research hotspot [25].

Due to the excellent photocatalytic activity, chemical stability, environmentally friendly feature, and low biological toxicity of TiO2, TiO2-based catalyst is currently recognized as the most promising photocatalyst for organic dye degradation and has great potential in wastewater purification treatment [6, 7]. However, due to the wide intrinsic band gap of TiO2, it can only absorb ultraviolet light and has a low utilization rate of sunlight. At the same time, the carrier life of TiO2 is short, and the photogenerated electrons and holes are easy to compound, leading to the degradation of catalytic performance [8]. Recombining TiO2 and other nanomaterials, making composite catalyst absorbance range extension to visible light area, and further improving the efficiency of separation and migration of the carrier, is the main research direction for developing high-performance TiO2 composite photocatalyst. The current main composite methods generally include cationic replace, precious metal nanoparticle load, and heterostructure built. Li et al. [9] prepared V3+/V5+ substituted mesoporous TiO2 using the sol-gel method for catalytic degradation of methylene blue. Compared with mesoporous TiO2, vanadium ion substituted mesoporous TiO2 has higher photocatalytic activity. Zhang et al. [10] reported HAc-Ag/TiO2 composite photocatalyst loaded with silver nanoparticles using the photochemical reduction method combined with acetic acid impregnation for the degradation of methyl orange in water. The synergy of HAc and Ag makes HAc-Ag/TiO2 a more narrower band gap width and correction to the top of valence band location, which endow a good visible light catalytic activity. Building heterojunction is widely applied in catalysis. For example, Wang et al. [11] deposited Ag2O on TiO2 nanorods constructing the Ag2O/TiO2 heterojunction. Ag2O has a narrower band gap than TiO2, and the electron-hole pair generated under visible light irradiation is captured by the electron trap of TiO2, which prolongs the recombination time of electrons and holes, and realizes the efficient catalytic degradation of methyl orange in water.

The core-shell structure has the advantages of large specific surface area, regular size, stable, and controllable performance, which makes it a wide application prospect in the field of catalysis [1214]. Greiner et al. [15] prepared the core-shell structure fiber of gold nanoparticles supported on polymer tube by the electrospinning technique. The fiber has obvious catalytic activity for the hydrolysis oxidation and alcoholysis of dimethylphenylsilane. Moreover, the macroscopic nonwoven fabric can be used as the catalyst system and shows excellent reusable performance. In recent years, upconversion nanomaterials have become a research hotspot due to the characteristics of near-infrared photoexcitation, narrow emission band, large antistoke shift, stable photochemical properties, and adjustable luminescence properties [1619]. Through the multiphoton process, the upconversion material doped with rare earth elements can convert low energy near-infrared light to high energy visible light and ultraviolet light and stimulate TiO2 to complete the photocatalytic effect. It is one of the effective means to improve the utilization of light by compound the upconversion material with the ultraviolet photocatalytic material to broaden the intrinsic excitation wavelength of the photocatalytic material. The upconversion materials can be doped with rare earth elements to further regulate and improve their luminescence properties.

Based on the above considerations, a NaYF4/Yb/Tm/TiO2 core-shell fiber was designed and prepared by the coaxial electrospinning method and liquid paraffin wax as a position holder. NaYF4/Yb/Tm can convert near-infrared light and visible light to ultraviolet light and be utilized by TiO2 for the degradation of rhodamine B in waste water.

2. Experimental Part

2.1. Reagents and Instruments

Reagents include polyvinylpyrrolidone (PVP, , Aldrich), anhydrous ethanol (AR, Beijing Chemical Factory), glacial acetic acid (AR, Beijing Chemical Factory), tetrabutyl titanate (AR, National medicine group chemical reagent Co., Ltd.), rhodamine B (red dye, Aldrich), liquid paraffin wax (AR, Beijing Chemical Factory), and cyclohexane (AR, Beijing Chemical Factory), and NaYF4/Yb/Tm nanoparticles are given as a present from the University of Wollongong. The experimental instruments include electrospinning device (high voltage power supply, receiving device, and syringe), scanning electron microscopy (SEM, Quanta 250 FEG), transmission electron microscope (TEM, FEI Tecnai G2-F20), muffle furnace (German, LH15/13), and UV-Vis spectrophotometer (Hitachi U3900).

2.2. Experimental Process
2.2.1. The Preparation of Precursor Solution

(1) The shell spinning solution: dissolving 0.5 g PVP in a mixed solution of 7.5 g anhydrous ethanol and 2.0 g acetic acid and continuous stirring it with a magnetic agitator to form a homogeneous and clarified solution until PVP is fully dissolved. Dissolving 2.0 g tetrabutyl titanate in the above mixture, stirring it slowly with a magnetic stirrer during the adding process, and continue stirring for 1 h after forming a homogeneous solution. The solution was evenly mixed resulting in PVP/tetrabutyl titanate precursor solution. (2) The core spinning solution: referring to the method in the literature [20], NaYF4/Yb/Tm nanoparticles were synthesized by solvothermal technology, and the optimal ratio of core spinning solution was determined. And then 300 L of nanoparticle dispersion was measured, and 200 L of cyclohexane and 3.5 mL of paraffin were added to prepare core spinning solution for use.

2.2.2. Preparation of NaYF4/Yb/Tm/TiO2 Core-Shell Hollow Structure Composite Fibers

The electrospinning process was performed using a home-made setup including coaxial needles and basic equipment. The inner and outer layer precursor body solutions were feed into the syringe, respectively, and the diameter, voltage, and receiving distance of the needle were controlled in the coaxial electrospinning process. Nanoparticle/PVP/tetrabutyl titanate primary fiber membrane was obtained by adjusting the solution parameters and electrospinning conditions. Next, the primary fiber membrane was placed in a temperature-controlled muffle furnace at a heating rate of 1°C/min, calcined at 500°C in air atmosphere, and naturally cooled to room temperature. The organic components were removed, and the nanoparticles were coated in the interior surface of fibers obtaining the core-shell hollow composite fiber membrane.

2.2.3. Morphology Characterization

The morphology characterization was performed by the following procedure using different techniques. For the SEM sample, the fiber membrane and its cross-sectional were directly pasted on the SEM test platform, gold was sprayed under vacuum condition, and then the surface morphology and section structure of the fiber were characterized by SEM. The acceleration voltage was 10 kV. For TEM samples, nanoparticles and calcined samples were dispersed in ethanol solution, dropped on the surface of copper mesh with carbon film, and dried naturally, and then the morphology of the nanoparticles and the internal structure of the fibers were characterized by TEM. The acceleration voltage was 200 kV. Finally, the size of the nanoparticles was statistical and obtained from one hundred selected samples.

2.2.4. Photocatalytic Degradation Experiment

The photocatalytic properties of composite fibers were characterized by catalytic degradation of rhodamine B. The composite fiber membrane obtained from the calcination was cut into small pieces and placed in the prepared rhodamine B solution, which was soaked under the condition of avoiding light to achieve saturated adsorption. The sample to be tested was placed flat in a surface dish containing 10 mL and 0.01 mmol/L rhodamine B solution, irradiated with xenon lamp, and the supernatant fluid was taken into a quartz colorimetric dish at a certain interval of time. The absorbance at 554 nm corresponds to the absorption maximum of rhodamine B. The absorbance value was measured by UV-Vis spectrophotometer to describe the concentration change and examine its photocatalytic activity. The test results were obtained from five selected samples. For comparison, the photocatalytic experiments of the two types of core-shell hollow structure fiber with and without NaYF4/Yb/Tm nanoparticles were carried out under the same conditions. Quantification of the rhodamine B concentration at different intervals was taken by using a calibration plot of rhodamine B. The absorbance was measured every 20 minutes until the color did not change significantly, and then the photocatalytic degradation curve of the material under light conditions was plotted.

3. Results and Discussion

3.1. Preparation, Morphology, and Structure Analysis of NaYF4/Yb/Tm/TiO2 Core-Shell Composite Fibers

As shown in Figure 1, we first prepared core-shell hollow TiO2 nanofibers with and without incorporated NaYF4/Yb/Tm nanoparticles using coaxial electrospinning and calcination and then investigated catalytic degradation of rhodamine B. Specifically, two types of core-shell hollow structure fiber with NaYF4/Yb/Tm nanoparticles and without NaYF4/Yb/Tm nanoparticles were selected for comparison. The fibers were obtained by coaxial electrospinning with optimized preparation parameters and calcination at 500°C, and their surface and fracture morphology and structure were characterized and analyzed using SEM and TEM. Figure 2 shows the corresponding scanning electron microscope images and statistical images of particle diameter. Figures 2(b) and 2(d) are local enlargements of Figures 2(a) and 2(c), respectively. After calcination, interior cyclohexane and paraffin are removed, leaving only the hollow structure or the nanoparticles. As can be seen from Figures 2(a)–2(d), the core-shell hollow TiO2 fiber has smooth interior surface, showing an obvious hollow core-shell structure. As can be seen from Figures 2(c) and 2(d), after adding nanoparticles, the surface of the fiber is smooth, but the interior of the fiber is obviously covered with nanoparticles. The size of the prepared nanoparticles is small and uniform. According to statistics, the average particle size of the nanoparticles is , as shown in Figure 2(e). For the overall morphology, fibers cross each other in a state of disordered accumulation, as shown in Figure 2(f). The EDS element analysis diagram in Figure 3 also proves that the composite fiber successfully loads nanoparticles.

3.2. Performance Analysis of Photocatalytic Degradation of Rhodamine B by NaYF4/Yb/Tm/TiO2 Core-Shell Composite Fibers

In order to prove the photocatalytic degradation performance of composite fibers, the catalytic degradation experiment of rhodamine B was carried out, and the results were shown in Figure 4. The composite fiber catalyst was first added to the as-prepared rhodamine B solution and stirred for 30 min to achieve adsorption equilibrium with rhodamine B. After stirred, the nanoparticles were naked. Then, the sample was placed in a colorimetric dish, and the UV-Vis absorption spectrum was measured in the wavelength range of 300-800 nm. Figures 4(a) and 4(b) show the absorption spectra at different catalytic times. At 550 nm, the maximum absorption peak intensity gradually decreases with the extension of reaction time. As can be seen from the illustration, as time goes on, the catalytic degradation reaction proceeds, and the color of the dye changes from dark to light until it totally disappears. However, in the absence of nanoparticles, the catalytic degradation rate was slower, indicating that both nanoparticles and structures are vital factors for the catalysis. After 2 h reaction, the degradation efficiency of fiber without nanoparticles was 83.79%, while the degradation efficiency of fiber with nanoparticles was 99.12%. The catalytic degradation efficiency of both of them was much higher than the photocatalytic degradation rate of commercial TiO2 (P25) [16, 17]. These results indicate that the composite fiber has excellent photocatalytic activity, in which the synergistic effect of the hollow core-shell structure and nanoparticles plays an important role in improving the photocatalytic performance.

3.3. Cyclic Utilization Analysis of NaYF4/Yb/Tm/TiO2 Core-Shell Composite Fibers

In order to prove the recyclability, the fiber morphology before and after photocatalysis was characterized, as shown in Figure 5. It can be found that the morphology and internal structure of the fiber membrane have no obvious change before and after photocatalysis, the core-shell structure of the fiber was almost intact, the internal covered nanoparticles still existed, and the loading effect was unsacrificed. In addition, as a catalyst carrier, the own chemical stability and thermal stability of the core-shell micro/nanofiber make it difficult to be degraded by ultraviolet light or strong oxidizing hydroxyl radicals in the long-term photocatalytic process, indicating that the fiber have good photocatalytic performance and loading stability.

3.4. Photocatalytic Mechanism Analysis of NaYF4/Yb/Tm/TiO2 Core-Shell Composite Fibers

As shown in Figure 6, for NaYF4/Yb/Tm/TiO2 core-shell fiber catalyst, the possible photocatalytic reaction mechanism is shown as follows: NaYF4/Yb/Tm absorbs visible light and converts it into ultraviolet light and emits it to TiO2, photogenerated electrons migrate to the surface of TiO2 and react with adsorbed oxygen to generate O2- or O22-, and then O2- or O22- reacts with H2O to generate H2O2 and ·OH. The conduction band of TiO2 is above the REDOX potential of rhodamine B; so, the oxygen-containing active species (O2-, O22-, H2O2, ·OH, etc.) produced by photoexcitation of TiO2 have the performance of oxidizing organic molecules.

4. Conclusion

NaYF4/Yb/Tm/TiO2 core-shell composite fibers were prepared by coaxial electrospinning and high temperature calcination. The morphology, structure, and photocatalytic properties of the materials were characterized by comprehensive techniques including scanning electron microscopy, transmission electron microscopy, and UV-Vis spectrophotometer. By dual synergistic, the degradation efficiency of rhodamine B using the core-shell composite fiber was significantly improved up to 99%, which is superior to commercial P25 and hollow fiber without nanoparticles. The results show that the design of the hollow core-shell structure and the doping of upconversion nanoparticles can greatly improve the photocatalytic performance of the composite fiber, and the material has a potential application prospect in the catalytic degradation of organic pollutants.

Data Availability

The data used to support the findings of this study are included within the article.

Conflicts of Interest

The authors declare that they have no conflicts of interest.

Acknowledgments

This work is supported by the National Natural Science Foundation of China, Grant 51803183.

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Copyright © 2021 Fengyun Guo et al. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

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