Fabrication and Characterization of Highly Efficient As-Synthesized WO3/Graphitic-C3N4 Nanocomposite for Photocatalytic Degradation of Organic Compounds

The incorporation of tungsten trioxide (WO3) by various concentrations of graphitic carbon nitride (g-C3N4) was successfully studied. X-ray diffraction (XRD), Scanning Electron Microscope (SEM), and Diffused Reflectance UV-Vis techniques were applied to investigate morphological and microstructure analysis, diffused reflectance optical properties, and photocatalysis measurements of WO3/g-C3N4 photocatalyst composite organic compounds. The photocatalytic activity of incorporating WO3 into g-C3N4 composite organic compounds was evaluated by the photodegradation of both Methylene Blue (MB) dye and phenol under visible-light irradiation. Due to the high purity of the studied heterojunction composite series, no observed diffraction peaks appeared when incorporating WO3 into g-C3N4 composite organic compounds. The particle size of the prepared composite organic compound photocatalysts revealed no evident influence through the increase in WO3 atoms from the SEM characteristic. The direct and indirect bandgap were recorded for different mole ratios of WO3/g-C3N4, and indicated no apparent impact on bandgap energy with increasing WO3 content in the composite photocatalyst. The composite photocatalysts’ properties better understand their photocatalytic activity degradations. The pseudo-first-order reaction constants (K) can be calculated by examining the kinetic photocatalytic activity.


Introduction
The photocatalytic performance of semiconductor materials, based on oxide semiconductors in their crystalline phases, has recently become desirable for producing hydrogen and oxygen via visible-light water splitting. Designing semiconductor composites produced between two semiconductor materials necessitates crystalline phase engineering [1][2][3]. The use of heterogeneous photocatalysis to convert water into hydrogen gas is regarded as one of the most promising options for addressing global energy and pollution problems [1,4,5]. In the present century, the rapid decline in energy sources, and increased power, waste, and renewable H 2 energy sources, are attributable to worldwide demand for fossil fuels. A. Fujishima et al. studied for a long time how to establish a clean and renewable photocatalytic hydrogen-production method [6]. The absorption wavelength range of semiconductor materials such as oxides, sulfides, nitrides, and solid solutions was examined under visible light, to improve the absorption wavelength range [7,8].
Heterojunction photocatalysts were used extensively to improve the separation efficiency of photoexcited electron-hole pairs. A single-phase photocatalyst has significant limitations in a photocatalytic response, because photogenerated electrons and holes are quickly mixed [9] to develop optical properties. Jiang et al. doped phosphorus nanosheets with g-C3N4 and added carbon defects, which significantly increased the rate of hydrogen evolution through the photocatalytic method [9]. Furthermore, studies report an improved hydrogen production rate through using a mineral acid or phosphoric acid etching of g-C 3 N 4 nanosheets to increase the number of active sites [10,11].
Graphite carbon nitride (g-C 3 N 4 ) has recently gained new interest as a promising material in different applications such as photocatalysts, fuel cell electrodes, light-emitting devices, and chemical sensors. g-C 3 N 4 stands out amongst many types of photocatalysts. A polymer photocatalyst bandgap is about 2.7 eV, allowing visible light to absorb up to 460 nm. Nevertheless, g-C 3 N 4 can absorb visible light effectively since graphitic C 3 N 4 has an adequate conduction band under illumination conditions that is able to be more harmful than protons formed by hydrogen [12,13]. Tungsten oxide (WO 3 ) is considered a promising material [13,14]. It has been reported that synthesis of WO 3 /g-C 3 N 4 composite organic compounds shapes a heterostructural composite photocatalyst [15,16],provided that the electron donor is an aqueous solution for triethanolamine. In the color-sensitization method, we looked at the composite catalyst's hydrogen production behavior under visible-light irradiation. g-C 3 N 4 composite, blended with WO 3 using a planetary mill, was prepared using hydrothermal treatment to improve its photocatalytic activity [15]. The photocatalytic activity incorporated WO 3 in g-C 3 N 4 composite organic compounds [17]. J. Liang et al. [18] investigated the use of crystalline phase engineering in WO 3 /g-C 3 N 4 composite organic compounds to improve photocatalytic activity under visible light. They demonstrated that WO 3 /g-C 3 N 4 composites with h-WO 3 show better dispersion of WO 3 , higher charge separation, and higher photocatalytic activity through visible-light photocatalytic degradation of Rhodamine B (RhB).
In this research, incorporating WO 3 into g-C 3 N 4, composite organic compound photocatalysts were prepared, and exhibited improved photocatalytic activity under visible light. Their morphological, diffused reflectance UV-Vis optical, and (Methylene blue (MB) and phenol) photocatalytic activity properties were analyzed and discussed in detail, to understand the effects of WO 3 on g-C 3 N 4 composite organic compounds.

Regents
In the experiment, an analytical grade of melamine, sodium tungstate dihydrate (Na 2 WO 4 ·2H 2 O) ACS reagent, ≥99%, and other chemicals purchased from Sigma-Aldrich were used. These chemicals did not need further purification as they were of analytical grade. De-ionized water was utilized to avoid contamination.

Synthesis of Pure g-C 3 N 4 and WO 3 /g-C 3 N 4 Composite Organic Compounds
Simple g-C 3 N 4 synthesis involves melamine pyrolysis prepared in an air atmosphere. Initially, 8 g of melamine was ground inside a crucible, then heated at a rate of 5 • C per min until it attained 550 • C, and then adjusted at this temperature for 2 h. Afterwards, the samples were left to cool down to ambient temperature. In the mortar, the resultant powder was then ground with a pestle. Following the first stage, Na 2 WO 4 ·2H 2 O was added to melamine to synthesize the doped WO 3 /g-C 3 N 4 composite organic compounds, after which the procedure for pure g-C 3 N 4 was repeated.

Characterization Techniques
The effect of WO 3 on the physical structure of the g-C 3 N 4 composite organic compounds for the 13 structures was characterized by X-ray diffraction. Shimadzu X-ray Diffractometer (XRD-6000 Series) was utilized with the standard copper X-ray tube at 30 kV and 30 mA with a wavelength equal to 1.5406 Å. The surface structure of all samples was evaluated by scanning electron microscopy (SEM-JSM6360 Series, with an acceleration voltage = 20 kV).
The effect of WO 3 on g-C 3 N 4 nanocomposite organic compounds was tested employing a UV-vis-NIR spectrophotometer model (Shimadzu UV-3600) with diffused reflectance in a wide range between 200 and 800 nm. The device was designed with the BaSO 4 built-in sphere attachment as reference material. To counteract the WO 3 /g-C 3 N 4 composites within the holder, as a guide for the BaSO 4 and the other holder, a specifically constructed holder attached to the integrating sphere device was employed. The thickness of the holder corresponds to the thickness of the WO 3 /g-C 3 N 4 nanocomposites. To track the photo-removal phase, a UV-visible spectrophotometer was used.
The diffused reflectance was measured in ambient conditions using a JASCO UV-Vis-NIR-V-570 double beam spectrophotometer.

Photocatalytic Measurements
A simple wooden photoreactor tested the photocatalytic activity of WO3/g-C3N4 nanocomposites under visible-light spectrum radiation of samples, using both methylene blue (MB) and aqueous phenol as a pollutant example in wastewater. I.S. Yahia and his group designed the photoreactor in NLEBA, Ain Shams University (ASU), Egypt, consisting of two parts: the outer part was in the form of a box made from wood (height: 100 cm, width: 65 cm); the inner part had seven visible lamps (18 W, 60 cm length, 425 to 600 nm), and could be separately controlled. Each set of nanopowders was placed in a beaker containing 50 mL of MB (20 mg/L) (i.e., for the phenol photodegradation). The sample was magnetically stirred in the dark system to reach equilibrium between dye and photocatalyst. The sample was removed from the solution after a specific time (every 15 min), and the amount of sample remaining was then exposed to visible light. A UV-Vis spectrophotometer was used to analyze the samples.

Structural XRD Measurements
The crystalline structure phase was analyzed with the XRD technique to reveal the effect of doping WO 3 in the final products. XRD patterns are shown in Figure 1 for pure g-C 3 N 4 and its doping with WO 3 on the g-C 3 N 4 composite organic compounds, with various WO 3 effects. As visualized in Figure 1, the g-C 3 N 4 powder sample highlights two peaks at 2θ = 13.1 • , and 2θ = 27.4 • , which can be indexed to a small peak, (100) plane, pertinent to the in-plane structural packing of graphitic material, and a sharp peak, (002) plane, assigned to the interlayer spacing of the conjugated aromatic system. The (002) peak indicates a higher-density packing of the g-C 3 N 4 molecules. This corresponds to the characteristic interplanar staking peaks of aromatic systems and the inter-layer structural packing, respectively [19,20]. These results are compared with Mo et al. [21]. The peak at 2θ = 27.4 • (JCPDS 87-1526) confirms the formation of hexagonal phase g-C 3 N 4 powders [18,20,21]. The introduction of doping WO 3 on g-C 3 N 4 composite organic compounds reduces the maximum intensity of peaks. In Figure 1, we notice that only two peaks appear in the entirety of the prepared samples related to pure g-C 3 N 4 except for the last sample, noted as 0.5 g WO 3 -doped g-C 3 N 4, showing the other two peaks related to WO 3 . The two peaks related to WO 3 appear at 2θ = 16.9 • and 32.51 • , related to (101) and (022), according to JCPDS 01-083-0950. The average crystallite size for the prepared samples was measured using the Debye-Scherrer formula, as follows [22]: The calculated crystallite size D depends on the broadening diffraction peak β, the diffraction angle θ , and the X-ray wavelength λ. Both dislocation density δ and lattice strain ε were calculated using the following equations [23,24]: The XRD structural parameters for the prepared samples summarized in Table 1 show that the average crystallite size for the pure g-C3N4 is 39.17 nm, and this increases from 35.91, 35.93, 40.84, 44.83, to 81.67 nm for the 0.5, 0.1, 0.05, 0.01, and 0.001 WO3-doped g-C3N4 composites, respectively.
The lower dislocation density values reflect the higher quality of the prepared samples. The average crystallite size for the prepared samples was measured using the Debye-Scherrer formula, as follows [22]: The calculated crystallite size D depends on the broadening diffraction peak β, the diffraction angle θ, and the X-ray wavelength λ. Both dislocation density δ and lattice strain ε were calculated using the following equations [23,24]: The XRD structural parameters for the prepared samples summarized in Table 1 show that the average crystallite size for the pure g-C 3 N 4 is 39.17 nm, and this increases from 35.91, 35.93, 40.84, 44.83, to 81.67 nm for the 0.5, 0.1, 0.05, 0.01, and 0.001 WO 3 -doped g-C 3 N 4 composites, respectively.
The lower dislocation density values reflect the higher quality of the prepared samples.

Morphologies and Microstructure Analysis
To assess the effect of WO 3 in g-C 3 N 4 composite organic photocatalyst compounds, the morphology and microstructure of the pure g-C 3 N 4 and its WO 3 -doped g-C 3 N 4 composite organic compounds was studied by using SEM image analysis. Figure 2a-f presents the SEM images of the investigated composite photocatalysts. The morphology of pure g-C 3 N 4 exhibited apparent granular aggregates and a typical sheet that consisted of small particles created from some irregular particles. Figure 2c-f shows that the WO 3 particles were attached to the surface of the sheet g-C 3 N 4 . The particle sizes obtained from SEM images of the investigated composite organic compounds were gathered in Table 2. The particle sizes varied between 1.65 and 1.51 µm. As the WO 3 doping particle contents increased, the g-C 3 N 4 composite photocatalyst had no noticeable influence on the obtained particle size. A similar result is reported by X. Chu et al. [25].  Figure 3a shows the optical UV-Vis diffused reflectance spectroscopy study to identify the bandgap energy of pure g-C3N4 and WO3-doped g-C3N4 composite organic photocatalyst compounds. The optical UV−Vis diffused reflectance spectra for other WO3/g- Figure 2.

MB Phenol
Pure g-C 3 Figure 3a shows the optical UV-Vis diffused reflectance spectroscopy study to identify the bandgap energy of pure g-C 3 N 4 and WO 3 -doped g-C 3 N 4 composite organic photocatalyst compounds. The optical UV-Vis diffused reflectance spectra for other WO 3 /g-C 3 N 4 photocatalyst composite samples should be the superimposed signals of g-C 3 N 4 . All diffused reflection spectra increased with increasing wavelengths up to 400 nm. The absorption edge spectra start to redshift towards the visible region, allocated to the intrinsic g-C 3 N 4 bandgap [25].
The redshift suggested that the photocatalyst composite compounds could use sunlight and produce more electron-hole pairs, which would help the photocatalytic response. The above findings may be caused by the interactions between the WO 3 and g-C 3 N 4 incorporated into the heterojunction materials. Figure 3b,c displays the direct and indirect energy bandgap of pure g-C 3 N 4 and its WO 3 atom-doped g-C 3 N 4 composite organic photocatalyst compounds, which can be estimated from the plots of (ahυ) 2 and (ahυ) 1/2 vs. the incident photon energy (hυ) using Tauc's formula [26]. The Kubelka-Munk function and its related absorption coefficient (α) are as follows [27][28][29]: where A is a pre-factor, E g is the energy bandgap, and r limits the transition band type. When r = 2 is related to the indirect allowed band, r = 1/2 is associated with the direct allowed band. The bandgap of the photocatalyst was determined by Tauc's plot, where (αhυ) 1/2 with hυ axis (i.e., the linear portion of the plots (αhυ) 2 with hυ axis). By drawing a tangent line of each curve, each photocatalyst composite material's bandgap was obtained from the intercept hυ axis. Therefore, the estimated bandgaps of pure g-C 3 N 4 and its WO 3 atom-doped g-C 3 N 4 composite organic photocatalyst compounds, with various WO 3 content, confirmed that the direct and indirect bandgaps for g-C 3     The redshift suggested that the photocatalyst composite compounds could use sunlight and produce more electron-hole pairs, which would help the photocatalytic response. The above findings may be caused by the interactions between the WO3 and g-C3N4 incorporated into the heterojunction materials. Figure 3b,c displays the direct and indirect energy bandgap of pure g-C3N4 and its WO3 atom-doped g-C3N4 composite organic photocatalyst compounds, which can be estimated from the plots of (ahυ) 2 and (ahυ) 1/2 vs. the incident photon energy (hυ) using Tauc's formula [26]. The Kubelka-Munk function and its related absorption coefficient (α) are as follows [27][28][29]: where A is a pre-factor, Eg is the energy bandgap, and r limits the transition band type. When r = 2 is related to the indirect allowed band, r = 1/2 is associated with the direct allowed band. The bandgap of the photocatalyst was determined by Tauc's plot, where (αhυ) 1/2 with hυ axis (i.e., the linear portion of the plots (αhυ) 2 with hυ axis). By drawing a tangent line of each curve, each photocatalyst composite material's bandgap was obtained from the intercept hυ axis. Therefore, the estimated bandgaps of pure g-C3N4 and its WO3 atom-doped g-C3N4 composite organic photocatalyst compounds, with various WO3 content, confirmed that the direct and indirect bandgaps for g-C3N4 were 2.83 [30] and 2.56 eV, respectively. This result was also reported by J.Y. Tai et al. [31]. For the indirect bandgap, we noted a slight change from 2.56 eV for the pure g-C3N4 changing to 2.6, 2.65, 2.66, 2.86, to 2.71 eV for the 0.5, 0.1, 0.05, 0.01, and 0.001 WO3-doped g-C3N4 composite, respectively. For the direct bandgap, a small change was also noted, from 2.83 eV for the pure g-C3N4 changing to 2.86. 2.88, 2.89, 2.90, 2.92 eV for the 0.5, 0.1, 0.05, 0.01, and 0.001

Kinetics of the Photodegradation Process of WO 3 -Doped g-C 3 N 4 Nanocomposites
The photocatalytic performances of pure g-C 3 N 4 and its WO 3 /g-C 3 N 4 composites, with various concentrations, were assessed using MB and phenol contaminants under visible-light irradiation. The extent of the concentration of MB and phenol contaminants on the photocatalyst was measured in the dark system until equilibrium. The equilibrium between the prepared photocatalyst and the investigated organic pollutants, MB, as a colored dye, and phenol, as a colorless organic compound, was recognized after 30 min of stirring. The photocatalytic performances of pure g-C 3 N 4 and its WO 3 /g-C 3 N 4 composites with different photocatalysts were investigated for the photodegradation of MB and phenol contaminants. The achieved results are shown in Figure 4a,b. Figure 4a shows a limited photocatalytic performance of the pure g-C 3 N 4 toward MB. However, the improved photocatalytic performance of WO 3 /g-C 3 N 4 composites was recorded, indicating a major effect on the photocatalytic activity of g-C 3 N 4 when modified with WO 3 . In general, the composite's photocatalytic activity increased after WO 3 was applied, and enhanced photocatalytic activity of 0.05% WO 3 was noted.
Nevertheless, the increase in WO 3 (0.1 and 0.5) has been found to reduce photocatalytic efficiency, which may be due to the decrease in visible-light absorption catalytic sites. Additionally, the same behavior was observed for the degradation of phenol. The composite material containing 0.5% WO 3 showed the maximum performance for phenol degradation, which can be attributed to the production of the WO 3 -semiconductor heterojunction effectively, which leads to transfer of charge from g-C 3 N 4 under the visible-light irradiation. Moreover, the kinetics of the degradation of MB and phenol was noticed to follow the pseudo-first-order model, and the reaction rates were calculated by Equation (2) [32]: between the prepared photocatalyst and the investigated organic pollutants, MB, as a colored dye, and phenol, as a colorless organic compound, was recognized after 30 min of stirring. The photocatalytic performances of pure g-C3N4 and its WO3/g-C3N4 composites with different photocatalysts were investigated for the photodegradation of MB and phenol contaminants. The achieved results are shown in Figure 4a,b. Figure 4a shows a limited photocatalytic performance of the pure g-C3N4 toward MB. However, the improved photocatalytic performance of WO3/g-C3N4 composites was recorded, indicating a major effect on the photocatalytic activity of g-C3N4 when modified with WO3. In general, the composite's photocatalytic activity increased after WO3 was applied, and enhanced photocatalytic activity of 0.05% WO3 was noted.  Nevertheless, the increase in WO3 (0.1 and 0.5) has been found to reduce photocatalytic efficiency, which may be due to the decrease in visible-light absorption catalytic sites. Additionally, the same behavior was observed for the degradation of phenol. The composite material containing 0.5% WO3 showed the maximum performance for phenol degradation, which can be attributed to the production of the WO3-semiconductor heterojunction effectively, which leads to transfer of charge from g-C3N4 under the visible-light irradiation. Moreover, the kinetics of the degradation of MB and phenol was noticed to follow the pseudo-first-order model, and the reaction rates were calculated by Equation (2)   Here, C o and C are the concentrations at the initial step and regular time intervals, respectively. Additionally, K is the pseudo-first-order reaction-rate constant (min −1 ) for investigated organic contaminants, and t is the time (min). Figure 5a,b shows the linear relationship between ln(C o /C) and t. According to these results, the photodegradation of MB and phenol pollutants follows pseudo-first-order reaction kinetics. Additionally, the degradation rate relies on the concentration of the organic substrate. Figure 6 shows the constant rate values for the degradation of MB and phenol contaminants. Percentage of degradation can be calculated to determine the efficiency of the prepared catalysts in the photocatalytic reaction, as illustrated in Figure 5. The efficiency of degradation increases with WO 3 content to 0.5%, then the efficiency decreases. It can be noted that the photocatalytic degradation rates of MB had better rate-constant characteristics than the photocatalytic degradation rates of phenol. The photodegradation using MB and phenol contaminants in aqueous solution improvement onto pure g-C 3 N 4 and its WO 3 /g-C 3 N 4 photocatalyst composites with various concentrations was evaluated under visible light. Dependant on variations in the WO 3 content, the plot of the irradiation time (t) against −ln(C/C o ) was nearly a straight line. This result has also been reported by G. Lui et al. [33]. The corresponding estimated degradation rate constants (K) were added to Table 2.

Photodegradation Conduction Mechanism of WO3-Doped g-C3N4 Nanocomposites
The proposed mechanism for photocatalytic behavior of WO3/g-CN composite unde the visible spectrum is interpreted in Figure 6. It is a successfully designed WO3/g-CN composite with various WO3. The Kubelka-Munk method was used to calculate the va lence band (VB) and conduction band (CB) edge potentials of the prepared pure g-CN and WO3/g-CN with different concentrations of WO3. The direct and indirect bandgaps for g CN are 2.83 and 2.56 eV, respectively. The increase in WO3 content in the WO3/g-CN com posite significantly influences bandgap energy [34]. The proposed system suggests tha both g-CN and WO3 will likely offer photogenerated charge carriers. The photogenerated electron in CB of WO3 then flows to VB of g-C3N4 due to electrostatic forces of attraction between the electron in CB of WO3 and the hole in VB g-CN, reducing the recombination of electrons and holes in the WO3/g-C3N4 composite and assisting in enhancing the charg separation spatially.
Furthermore, the electrons in the CB of g-C3N4 can also be retained by reducing th molecular oxygen O2 to form O −2• , due to the negative nature of the CB edge potentia compared to the standard redox capability of O2/O −2• [35]. Thus, the hole created in the VB of WO3 leads interacts with H2O to generate OH • radicals, giving the more positive poten tial of the VB than the standard redox capability of OH/OH − . In this manner, the produc tion of O −2• and OH • radicals plays a significant role in the photodegradation of MB and phenol degradation under visible light. With both OH • and O −2. , the phenol and Meth ylene Blue dyes produced CO2 and H2O [36,37]

Photodegradation Conduction Mechanism of WO 3 -Doped g-C 3 N 4 Nanocomposites
The proposed mechanism for photocatalytic behavior of WO 3 /g-CN composite under the visible spectrum is interpreted in Figure 6. It is a successfully designed WO 3 /g-CN composite with various WO 3 . The Kubelka-Munk method was used to calculate the valence band (VB) and conduction band (CB) edge potentials of the prepared pure g-CN and WO 3 /g-CN with different concentrations of WO 3 . The direct and indirect bandgaps for g-CN are 2.83 and 2.56 eV, respectively. The increase in WO 3 content in the WO 3 /g-CN composite significantly influences bandgap energy [34]. The proposed system suggests that both g-CN and WO 3 will likely offer photogenerated charge carriers. The photogenerated electron in CB of WO 3 then flows to VB of g-C 3 N 4 due to electrostatic forces of attraction between the electron in CB of WO 3 and the hole in VB g-CN, reducing the recombination of electrons and holes in the WO 3 /g-C 3 N 4 composite and assisting in enhancing the charge separation spatially.
Furthermore, the electrons in the CB of g-C 3 N 4 can also be retained by reducing the molecular oxygen O 2 to form O −2• , due to the negative nature of the CB edge potential compared to the standard redox capability of O 2 /O −2• [35]. Thus, the hole created in the VB of WO 3 leads interacts with H 2 O to generate OH • radicals, giving the more positive potential of the VB than the standard redox capability of OH/OH − . In this manner, the production of O −2• and OH • radicals plays a significant role in the photodegradation of MB and phenol degradation under visible light. With both OH • and O −2 , the phenol and Methylene Blue dyes produced CO 2 and H 2 O [36,37].
In comparison to the previous work, our 0.5% WO 3 /g-C 3 N 4 has the highest photocatalytic activity of both MB and phenol in the presence of visible light, as shown in Table 3. Using the hydrothermal impregnation and calcination method, Cong Zhao et al. [38] obtained simple and inexpensive C-doped g-C 3 N 4 /WO 3 as highly active photocatalysts. Tao Pan et al. [39] prepared WO 3 /g-C 3 N 4 that showed improved photocatalytic activity for TC degradation. Perhaps most importantly, the UV-C-induced-TC degradation activity outperformed all other degradations regardless of concentration or pH level. According to Zhao et al. [40], the Ag/WO 2.9 /g-C 3 N 4 composite outperforms pure g-C 3 N 4 and pure WO 3 in terms of light-selective adsorption and photocatalysis. Hong Yan et al. [41] proved that WO 3 /g-C3N4-modified nanocomposites had more significant photocatalytic activity than pure WO 3 and pure g-C 3 N 4 . Junling Zhao et al. [19] discovered that WO 3 /g-C 3 N 4 photocatalysts have increased degradation activities towards RhB dye when exposed to simulated sunlight. Minji Yoon et al. [42] demonstrated that WO 3 /g-C 3 N 4 does not exhibit any photocatalytic activity on the degradation of p-nitrophenol. On the other hand, the degradation rate of p-nitrophenol was remarkably increased by the addition of Fenton to WO 3 /g-C 3 N 4 , which means that photocatalytic activity was further enhanced in the presence of hydrogen peroxide (H 2 O 2 ) because of the generation of hydroxyl radicals. Table 3. Photocatalytic comparison between the prepared WO 3 /g-C 3 N 4 and various previous works. 3.6. Recycling of WO 3 -Doped g-C 3 N 4 Nanocomposites A 0.05 WO 3 /g-CN was subjected re-use in photodegradation of MB and phenol for 4 cycles. Figure 7 represents the recycling and reusability of WO 3 /g-C 3 N 4 . The samples exhibited high performance without further decreased reaction rate, which means that WO 3 /g-C 3 N 4 is a promising material in MB and phenolic compound photodegradation.  Figure 7. The recycling process for pure g-C3N4 and its WO3/g-C3N4 nanocomposites in photodegradation of (a) MB, (b) phenol.

Conclusions
Novel, efficient WO3/g-C3N4 nanocomposite with various concentrations of graphitic carbon nitride (g-C3N4) was prepared. The prepared composites exhibited improved photocatalytic activity on the degradation of MB and phenol under visible-light irradiation. The composite material containing 0.5% WO3 showed the maximum MB and phenol degradation performance. The kinetic study showed that the pseudo-first-order kinetic best fitted the photocatalytic process. A mechanism was proposed to degrade organic pollutants using WO3/g-C3N4 composites under visible-light irradiation.

Conclusions
Novel, efficient WO 3 /g-C 3 N 4 nanocomposite with various concentrations of graphitic carbon nitride (g-C 3 N 4 ) was prepared. The prepared composites exhibited improved photocatalytic activity on the degradation of MB and phenol under visible-light irradiation. The composite material containing 0.5% WO 3 showed the maximum MB and phenol degradation performance. The kinetic study showed that the pseudo-first-order kinetic best fitted the photocatalytic process. A mechanism was proposed to degrade organic pollutants using WO 3 /g-C 3 N 4 composites under visible-light irradiation.