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Article

Synthesis, Characterization and Enhanced Visible Light Photocatalytic Performance of ZnWO4[email protected] Nanocomposites

by
Norah Alhokbany
*,
Saad M. Alshehri
and
Jahangeer Ahmed
*
Department of Chemistry, College of Science, King Saud University, Riyadh 11451, Saudi Arabia
*
Authors to whom correspondence should be addressed.
Catalysts 2021, 11(12), 1536; https://doi.org/10.3390/catal11121536
Received: 15 November 2021 / Revised: 2 December 2021 / Accepted: 14 December 2021 / Published: 16 December 2021
(This article belongs to the Special Issue The Importance of Shape-Tailoring at Nano- and Micro-Levels in Catalytic and Photocatalytic Applications)
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Abstract

:
ZnWO4 nanoparticles on reduced graphene oxide (ZnWO4[email protected]) nanocomposites were synthesized using the hydrothermal method. Structural, morphological, optical, and photocatalytic studies of the ZnWO4[email protected] nanocomposites were successfully investigated. Photo-catalytic performances of the ZnWO4[email protected] nanocomposites were examined for the degradation of hazardous methylene blue dye (HMBD) in a neutral medium. ZnWO4[email protected] nanocomposites show superior photo-catalytic performances over pure ZnWO4 nanoparticles. ZnWO4[email protected] nanocomposites degrade ~98% dye while pure ZnWO4 nanoparticles degrade ~53% dye in 120 min. The prepared nanocomposites also show excellent recycled photo-catalytic efficiencies over multiple cycles.

1. Introduction

The recycling of catalysts for multifunctional purposes is currently receiving the attention of scientists, to reduce the cost of commercial materials for a diverse range of technological uses. In this paper, we focus on the catalytic efficiency of reused cost-effective materials for various applications. It is noteworthy that the compounds belonging to group VI-B (including tungsten) showed tremendous efficiencies in various applications including as photo-catalysis [1,2,3,4], electro-catalysis [5,6], and for energy storage [7,8]. The treatment of contaminated water is an important way to regulate health issues by removing organic pollutants from water through the photo-catalytic process. Photo-catalysis is one of the promising methods for environmental remediation. Semiconductor-based nanocomposite materials were investigated as low-cost and high-performance photo-catalysts to control water pollution problems [9,10,11,12,13]. Zinc tungstate (ZnWO4) has large band gap energy (3.5–3.7 eV) and is used as an efficient photo-catalyst in the degradation of organic dyes under ultraviolet (UV) radiation [1,14]. ZnWO4 nanostructured materials used as photo-catalysts were also previously reported to degrade dyes [15,16,17,18,19]. However, the recombination of charge carriers in these materials is a challenge for researchers. Therefore, loading heteroatoms, carbon-based materials, or transition metal ions into a ZnWO4 matrix could be helpful for achieving efficient charge separation in semiconductors to improve their photocatalytic performance. The amalgamation of WO3 and ZnWO4 nanocomposites has enabled the achievement of efficient electron-hole charge separation, resulting in their reporting as efficient photo-catalysts [13,20]. Recently, Ag/ZnWO4 nanocomposites have shown promising efficiencies in the degradation of methyl orange (MO) and methylene blue (MB) dyes under UV irradiation [21,22]. ZnWO4 nanostructured materials have also been used for a range of purposes including for the extraction of dyes and heavy metals [23,24,25], as bacterial disinfectants [23], and for their photoluminescence [26], alongside being used as components in lithium-ion batteries [27,28] and supercapacitors [29,30]. Nevertheless, some reports state that dyes are not appropriate molecules for visible-light degradation reactions because they can absorb light and desensitize the photo-catalysts [31,32]. Previously, we have designed various transition metal tungstate, molybdate, gallate, and ferrite nanostructured materials for a variety of applications including wastewater treatment [1,2], electro-catalysis [1,5,33,34,35,36,37], and supercapacitor [1,33,38] applications. Functionalization of the semiconducting nanoparticles with materials that have high electrical conductivities and surface areas is an interest of researchers for the effective improvement of the catalytic activities and stabilities of low-cost photo-catalysts. Graphene-based zinc oxide [39,40,41] nanocomposites were previously reported as promising photo-catalysts in organic dye degradation reactions. Therefore, we have designed nanocomposites containing rGO sheet-supported ZnWO4 nanoparticles (ZnWO4[email protected]) for superior photocatalytic activities in neutral media. Recently, nickel molybdenum oxide nano-rods were initially used as photo-catalysts, and thereafter reused as efficient catalysts in electrochemical sensing and energy storage applications [42]. This report is mainly focused on the synthesis, characterization, and enhanced visible-light photo-catalytic efficiencies of the synthesized ZnWO4[email protected] nanocomposites.

2. Materials and Methods

2.1. Preparation of ZnWO4 Nanoparticles

ZnWO4 nanoparticles were initially synthesized using a solvent-free method (i.e., using molten salts) as reported elsewhere [1]. To prepare ZnWO4 nanoparticles, one mole of Zn(NO3)2·6H2O (Sigma Aldrich, 99%), one mole of Na2WO4·2H2O (Sigma Aldrich, 99%), thirty moles of NaNO3 (Sigma Aldrich, 98 + %), and thirty moles of KNO3 (Sigma Aldrich, 99%) were taken and mixed homogeneously by grinding properly, and then heated at 500 ± 10 °C for 6 h in a muffle furnace. White-colored nano-powder was collected and washed with de-ionized water to remove the impurities. The resulting nanoparticles were dried at 50 °C. The phase purity of the prepared nanoparticles was analyzed by powder X-ray diffraction (XRD) studies using a Bruker D-8 Advanced diffractometer with Cu-Kα radiation.

2.2. Preparation of ZnWO4[email protected] Nanocomposites

The prepared ZnWO4 nanoparticles and commercially available reduced graphene oxides (rGO, Sigma Aldrich) were taken in an appropriate ratio, followed by dispersion in de-ionized water (18 mL) and ethylene glycol (2 mL) via sonication for twenty min. The suspension was then transferred into an autoclave and treated via the hydrothermal method at 120 °C for 48 h. Dark grey-colored ZnWO4[email protected] nanocomposites were collected through centrifugation and then dried at 60 °C.

2.3. Characterization

The structural characterization of the prepared ZnWO4[email protected] nanocomposites was undertaken by powder X-ray diffraction (XRD), Fourier-transform infrared spectroscopy (FTIR, Bruker TENSOR-27), and X-ray photoelectron spectroscopy (XPS, PHI-5300). The surface morphologies and elemental compositions were evaluated by field emission scanning electron microscope (FESEM, JEOL, JSM-7600F) and energy dispersive studies (EDS). The optical band gap energy of ZnWO4[email protected] nanocomposites was determined using UV–Vis absorption spectra (Shimadzu-2550 spectrophotometer).

2.4. Photocatalytic Studies

The photocatalytic performance of ZnWO4[email protected] nanocomposites was measured by the degradation of a hazardous methylene blue dye (HMBD) solution. The Xenon lamp (400 W) with λ of ~400 nm was used as the visible light source for irradiation of the HMBD solution. 50 mg of ZnWO4[email protected] photo-catalyst was taken with 20 mL aqueous HMBD solution followed by stirring for 30 min to confirm the adsorption/desorption equilibrium. The photocatalytic degradation of the HMBD solution was investigated in a neutral medium (pH ~7) at the λmax of ~662 nm. Samples of the suspension measuring 2.0 mL (with maximum transparency) were taken at regular time intervals for the photo-catalytic analysis. Note that the regeneration efficiency of the ZnWO4[email protected] photo-catalyst was also investigated using similar experimental conditions as explained above. The mass spectrometry (MS) method for measuring dye degradation using photo-catalysts was also performed using an Agilent HPLC 1200 connected to a triple quadrupole mass spectrometer (Agilent 6410 QqQ) using a direct injection connector instead of a column. Detection was performed on a QqQ MS detector operated with an electrospray ionization (ESI) source. Low purity N2 gas was used as drying gas with a flow rate of 12 L min−1, and high purity N2 gas as collision gas at a pressure of 60 psi. Source temperature and capillary voltage were set at 350 °C and 4000 V, respectively. Fragmentor voltage was set at 110 V with collision energy of 15 V.

3. Results and Discussion

The phases and crystalline structures of the prepared ZnWO4[email protected] nanocomposites were initially analyzed by XRD. Figure 1a shows the XRD patterns of the ZnWO4[email protected] nanocomposites, and all the reflections including the (011), (110), (111), (021), (200), (121), (112), (211), (022), (220), (130), (202), (113), (311), and (041) planes can be identified for the monoclinic phase of ZnWO4 (JCPDS # 15–774). The resulting XRD patterns also agree with previous reports [1]. The additional XRD peaks (as marked by an *) represent rGO. No other peaks based on Zn or W oxides were detected in the XRD patterns, which confirmed the formation of ZnWO4[email protected] nanocomposites. Figure 1b shows the FTIR spectrum of the ZnWO4[email protected] nanocomposites. FTIR bands at low wavenumbers confirm the presence of ZnWO4. FTIR bands at ~620 and ~850 cm−1 represent Zn-O-Zn and W-O bonds, respectively. FTIR bands at ~3500 and ~1650 cm−1 belong to the −OH groups from atmospheric moisture. FTIR bands at ~1220 and ~1570 cm−1 could be identified as the C=O and C-H vibrations of rGO, respectively, as supported by previous reports [5].
FESEM measurements were taken at different magnifications to understand the morphology of the ZnWO4[email protected] nanocomposites (Figure 2). The FESEM micrographs clearly show that the ZnWO4 nanoparticles are very well supported by the rGO sheets (Figure 2a,c). A careful visualization for particle size analysis was also studied at high magnification, and the average particle diameter of the ZnWO4 nanoparticles was found to be ~50 nm (Figure 2d). Energy dispersive spectroscopy (EDS) equipped with FESEM was employed for the compositional analysis of the ZnWO4[email protected] nanocomposites (Figure 3). The EDS study revealed the presence of the chemical elements (i.e., Zn, W, O, and C) in the ZnWO4[email protected] nanocomposites as expected (Figure 3). The atomic % compositions of Zn and W were found to be in a 1:1 ratio, in agreement with the initial 1:1 loaded stoichiometry. The XPS study was also further investigated to determine the elemental composition and chemical states of the ZnWO4[email protected] nanocomposites. Figure 4 shows a high-resolution XPS spectra of Zn (2p), W (4f), O (1s), and C (1s) in the ZnWO4[email protected] nanocomposites. Figure 4a shows the high-resolution XPS spectrum of Zn (2p). The XPS spectrum shows two peaks at ~1025 eV and 1048 eV, which are attributed to Zn (2p3/2) and Zn (2p1/2), respectively, and suggest the presence of a Zn2+ chemical state. Figure 4b shows the high-resolution XPS spectrum of W (4f). It shows two spin-orbit doublet peaks at ~35.25 eV and ~37.20 eV, which represent W (4f7/2) and W (4f5/2), respectively, in the W6+ chemical state. Figure 4c shows the high-resolution XPS spectrum of O (1s). The resulting O (1s) peak at ~532.7 eV was deconvoluted into two peaks at 532.8 and 533.9 eV, of Zn–O and W–O, respectively. A high-resolution XPS spectrum of C (1s) is shown in Figure 4d. A peak of C (1s) appeared at ~284.40 eV and deconvoluted into four peaks of C=C at ~284.22 eV, C-OH at ~284.44 eV, C-O-C at ~285.90 eV, and C=O at ~286.30 eV. It is noteworthy that the above characterization techniques strongly support the formation of ZnWO4[email protected] nanocomposites. Thereafter, the prepared nanocomposites were used as photo-catalysts in the degradation of organic pollutants into inorganic minerals under visible-light irradiation.
The optical properties of ZnWO4[email protected] nanocomposites were also examined using UV–Vis absorption studies. The absorbance data of the ZnWO4[email protected] nanocomposites were recorded in the region from 100 to 900 nm (Figure 5). The optical band gap of the ZnWO4[email protected] nanocomposites was calculated using the absorption data, followed by use of Tauc’s model [43]. The band gap energy of the ZnWO4[email protected] nanocomposites was found to be ~3.50 eV, as shown in the inset of Figure 5. The resulting band gap energy of the ZnWO4[email protected] nanocomposites was lower than that of pure ZnWO4 materials (i.e., ~3.8 eV), as reported elsewhere [44]. Figure 6a shows the mechanism of photo-catalytic degradation of the HMBD solution into inorganic minerals under visible-light irradiation in the presence of the ZnWO4[email protected] nanocomposites. Photo-catalytic degradation of HMBD could be accompanied by the transfer of electrons from the valence band (VB) to the conduction band (CB) to form the electron (e−)–hole (h+) pairs. The e−–h+ pairs generate the O2−• and OH• radicals, followed by the attack on HMBD to oxidize it into the form of inorganic minerals (e.g., NH4+, H2O, CO2, etc.). The reaction mechanism of hazardous methylene blue dye (HMBD) degradation could be summarized with the given mechanistic steps:
  • Photo-catalyst + hυ → Photo-catalyst (e− + h+) → Photo-catalyst + H+ + OH• + O2•−
  • Photo-catalyst (h+) + OH− → Photo-catalyst + OH•
The electrons of photo-catalyst reduce the molecular O2 to superoxide (O2•−) at CB:
  • Photo-catalyst + O2 + e− → Photo-catalyst + O2•
  • O2•− + H+ → HO2•
Formation of H2O2 followed by further reduction:
  • 2HO2•− → H2O2 + O2
  • H2O2 + e− → OH− + OH•
The degradation of hazardous methylene blue dye (HMBD) through direct oxidation reactions on the surface of photo-catalyst gives the oxidized products:
  • OH• + HMBD → HMBD• + H2O
  • HMBD + h+ → HMBD+• (degraded products, i.e., NH4+, H2O, CO2 etc.)
Photo-catalytic activities of the ZnWO4[email protected] nanocomposites were examined by degradation of an HMBD solution under visible-light irradiation at a pH of ~7, and the photo-catalytic degradation data were monitored at the maximum absorption peak (λmax) of ~662 nm by a UV–Vis spectrophotometer. The absorption peak intensities were reduced with time under visible-light irradiations (Figure 6b). The decremental responses in absorption peak intensities of the HMBD solution demonstrates the degradation of HMBD on the surface of the ZnWO4[email protected] nanocomposites. Photo-catalytic efficiencies of the ZnWO4[email protected] nanocomposites acting as photo-catalysts were estimated using the given formula (η = [1−(Ct/C0)] × 100%), where ‘C0’ and ‘Ct’ represent the initial concentration of the HMBD solution, and the concentration after time ‘t’, respectively. The ZnWO4[email protected] nanocomposites degraded ~98% of the HMBD solution, and almost decolorized the solution in 120 min, while ~52% of HMBD was degraded by pure ZnWO4-NPs in the same time (i.e., 120 min) as shown in Figure 6c. Figure 6d shows a linear plot of the photo-catalytic efficiencies with time vs. ln(C0/Ct). The linear plot shows the pseudo first-order kinetic behavior of the photo-catalytic reactions. The rate constant and R2 values were found to be ~0.016 m−1 and ~0.9833, respectively. The photo-catalytic degradations of HMBD were reported to be ~90%, 70%, and 30% with the ZnWO4, CuWO4, and CoWO4 photo-catalysts, respectively, in 120 min [45]. WO3 nanoparticles were also used as photo-catalysts in the degradation of HMBD, and the degradation of the dye was reported to be ~20% in 160 min [46]. Recently, ZnWO4 nanostructures were significantly used as photo-catalysts in the photo-catalytic degradation of an HMBD solution (i.e., ~85% degradation in 3 h) [1]. Hence, existing work reveals the enhanced photo-catalytic performance of ZnWO4[email protected] nanocomposites in the degradation of HMBD solutions under visible-light irradiations. An ESI-MS spectrometric study of the degraded samples was also undertaken to support our conclusions regarding the photocatalytic degradation reactions of methylene blue dye. Figure 7 shows the ESI-MS spectra of the HMBD solution before and after photo-catalytic degradation. The molecular ion peak of methylene blue dye was reported previously at the m/z peak position of 284 before degradation [2,47]. No spectral line was detected in the mass spectrometric spectrum at the m/z position of 284 after photocatalytic degradation of methylene blue dye. These results indicate that the dye had been oxidized into various intermediates or fragments (i.e., organic molecules), as the spectral lines appeared at various m/z values in the spectrum. This is noteworthy as the intermediates, or fragments of the dye could be generated by the attack of free radicals (i.e., OH• and O2•−) on dye molecules under visible-light irradiations. The intermediates, or fragments, can further degrade into inorganic minerals under longer irradiation times, as also reported elsewhere [48]. Recycling of the ZnWO4[email protected] photo-catalysts is one of the important concerns for industrial applications. The recycled photocatalytic efficiencies of the ZnWO4[email protected] nanocomposites were also examined for eight consecutive cycles under visible-light irradiation. ZnWO4[email protected] nanocomposites show excellent recycled efficiencies for the photo-catalytic degradation of HMBD solutions. We found that regenerated ZnWO4[email protected] photo-catalysts degraded the HMBD solution efficiently for up to eight cycles (Figure 8). Note that the ZnWO4[email protected] photo-catalysts were washed with deionized water several times after each cycle, and then used again for the next cycle repeatedly. Based on the current results, ZnWO4[email protected] nanocomposites work as superior photo-catalysts in water purification applications for environmental remediation.

4. Conclusions

Hydrothermally synthesized ZnWO4[email protected] nanocomposites were shown to have superior photo-catalytic activities over pure ZnWO4 nanoparticles. The photo-catalytic activities of ZnWO4[email protected] nanocomposites for the degradation of HMBD showed excellent performances with ~98% dye degradation, which is far better than that of pure ZnWO4 photo-catalysts (~53% dye degradation), in 120 min. Hence, ZnWO4[email protected] nanocomposites can be considered as significant photo-catalysts for environmental remediation and energy applications.

Author Contributions

Conceptualization, Data curation, Methodology, Formal analysis, N.A.; supervision, Validation, Project administration, S.M.A.; Investigation, Validation, Project administration, Writing – review & editing, J.A. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by Researchers Supporting Project number (RSP-2021/391), King Saud University.

Acknowledgments

The authors extend their sincere appreciation to Researchers Supporting Project at the King Saud University, Riyadh, Saudi Arabia.

Conflicts of Interest

The authors declare no conflict of interest.

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Figure 1. (a) XRD patterns and (b) FTIR spectrum of synthesized ZnWO4[email protected] nanocomposites.
Figure 1. (a) XRD patterns and (b) FTIR spectrum of synthesized ZnWO4[email protected] nanocomposites.
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Figure 2. FESEM micrographs of ZnWO4[email protected] nanocomposites at (a,b) low and (c,d) high magnifications.
Figure 2. FESEM micrographs of ZnWO4[email protected] nanocomposites at (a,b) low and (c,d) high magnifications.
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Figure 3. EDS study of ZnWO4[email protected] nanocomposites for elemental analysis.
Figure 3. EDS study of ZnWO4[email protected] nanocomposites for elemental analysis.
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Figure 4. High-resolution XPS spectra of (a) Zn (2p), (b) W (4f), (c) O (1s), and (d) C (1s) in ZnWO4[email protected] nanocomposites.
Figure 4. High-resolution XPS spectra of (a) Zn (2p), (b) W (4f), (c) O (1s), and (d) C (1s) in ZnWO4[email protected] nanocomposites.
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Figure 5. UV–Vis absorption spectrum of ZnWO4[email protected] nanocomposites. Inset shows the band gap energy of ZnWO4[email protected] nanocomposites.
Figure 5. UV–Vis absorption spectrum of ZnWO4[email protected] nanocomposites. Inset shows the band gap energy of ZnWO4[email protected] nanocomposites.
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Figure 6. (a) Reaction scheme, (b) absorption spectra, (c) percent degradation, and (d) linear plot of photo-degradation of HMBD using ZnWO4[email protected] nanocomposites.
Figure 6. (a) Reaction scheme, (b) absorption spectra, (c) percent degradation, and (d) linear plot of photo-degradation of HMBD using ZnWO4[email protected] nanocomposites.
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Figure 7. ESI-MS spectra of HMBD solution before and after photo-catalytic degradation.
Figure 7. ESI-MS spectra of HMBD solution before and after photo-catalytic degradation.
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Figure 8. Recycled photocatalytic efficiencies of ZnWO4[email protected] nanocomposites.
Figure 8. Recycled photocatalytic efficiencies of ZnWO4[email protected] nanocomposites.
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Alhokbany, N.; Alshehri, S.M.; Ahmed, J. Synthesis, Characterization and Enhanced Visible Light Photocatalytic Performance of ZnWO4[email protected] Nanocomposites. Catalysts 2021, 11, 1536. https://doi.org/10.3390/catal11121536

AMA Style

Alhokbany N, Alshehri SM, Ahmed J. Synthesis, Characterization and Enhanced Visible Light Photocatalytic Performance of ZnWO4[email protected] Nanocomposites. Catalysts. 2021; 11(12):1536. https://doi.org/10.3390/catal11121536

Chicago/Turabian Style

Alhokbany, Norah, Saad M. Alshehri, and Jahangeer Ahmed. 2021. "Synthesis, Characterization and Enhanced Visible Light Photocatalytic Performance of ZnWO4[email protected] Nanocomposites" Catalysts 11, no. 12: 1536. https://doi.org/10.3390/catal11121536

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