Fabrication of g-C3N4/NiO/ZnO based Ternary Nanocomposite for Efficient Photocatalytic Degradation of Methylene Blue

doi:10.21203/rs.3.rs-5250401/v1

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Fabrication of g-C₃N₄/NiO/ZnO based Ternary Nanocomposite for Efficient Photocatalytic Degradation of Methylene Blue

https://doi.org/10.21203/rs.3.rs-5250401/v1

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Photocatalysis has emerged as a widely recognized and environmentally friendly technique for the degradation of biological contaminants into less hazardous substances. The technique offers a sustainable path for contamination reduction by utilizing sunlight-activated catalysts to initiate reactions for the degradation of pollutants. In this work, a facile co-precipitation approach was utilized to synthesize a ternary nanocomposite-based photocatalyst to improve photocatalytic performance. The metal oxide semiconductors ZnO and NiO were successfully integrated into the g-C₃N₄ matrix to develop a photocatalyst that showed substantially increased photocatalytic activity. The synthesized ternary nanocomposite was investigated for different physicochemical techniques such as photoluminescence (PL), ultraviolet-visible (UV-Vis) absorption spectroscopy, scanning electron microscopy (SEM), Raman spectroscopy, and X-ray diffraction (XRD). The structural, morphological, and optical characteristics of the ternary nanocomposite were thoroughly explored by these physiochemical techniques. The synthesized CNZ ternary nanocomposites-based photocatalyst revealed a significantly enhanced photocatalytic degradation rate of 92%, outperforming all other samples. The ternary nanocomposite demonstrated excellent reusability even after five successive reaction cycles, unveiling the superior potential in the photocatalytic application for an extended period without significantly losing its effectiveness. The synergistic integration of NiO and ZnO into g-C₃N₄ boosted the photocatalytic activity by enhancing electron-hole separation and reducing recombination reactions. The hybrid photocatalyst offers a great deal of promise for effectively eliminating harmful pollutants from aqueous solutions.

g-C3N4/NiO/ZnO

ternary nanocomposite

methylene blue

photocatalysis.

In order to solve the persuasive concerns of expanding global energy demand and escalating environmental challenges, it is now imperative to explore and utilize renewable and clean energy sources [1–3]. Wastewater discharged from various industrial and medical activities that contains significant amounts of dyes and medicines poses a significant threat to ecological health and is a major obstacle to environmental hygiene [4–6]. For the treatment of water polluted with organic contaminants, advanced oxidation processes (AOPs) such as photocatalytic oxidation mechanisms are well-established techniques [7]. These techniques are essential for applications involving water purification since they are remarkably effective at breaking down complex organic molecules [8]. Photocatalysis is now considered to be a very flexible and promising approach with a wide range of applications including wastewater purification, microbial disinfection, and the decomposition of hazardous organic compounds [9, 10]. As the method utilizes photocatalysts to initiate catalytic activities, this approach to treating many environmental challenges is sustainable and beneficial for the environment. The immense potential of semiconductor-based photocatalysis in energy and environmental applications, including water splitting for the generation of hydrogen and oxygen, oxidation of organic pollutants, and reduction of carbon dioxide, has triggered a lot of attraction [11, 12]. This approach produces electron-hole pairs that may efficiently initiate and drive these chemical processes by absorbing photons with energies higher than the semiconductor bandgap [13]. The majority of semiconductor photocatalysts, including the extensively investigated ZnO, WO₃, SnO₂, TiO₂, CeO₂, ZnS, and ZrO₂, normally have a single metal center [14–16].

Among others, Wurtzite ZnO (n-type semiconductor) is renowned for its exceptional characteristics, which include low production costs, unique electrical structure, outstanding chemical stability, and biocompatibility [17, 18]. It is widely used in several photocatalytic energy conversion applications. ZnO has a large exciton binding energy and a UV-active band gap of 3.37 eV at ambient temperature. Its broad and useful application in photocatalysis is nevertheless constrained by its large band gap and excessive recombination rate [19, 20]. This limitation is addressed by sensitizing ZnO with narrow band gap semiconductors, such as g-C₃N₄, which causes its absorption band to shift into the visible spectrum. ZnO/polymer and ZnO/metal oxide hybrid nanocomposites have demonstrated visible-light photodegradation activity. This occurs due to the formation of intermediate states in photocatalysts, subsequently promoting the absorption of visible light and encouraging the generation of electron holes during the photoreaction process [21–23].

Nickel oxide (NiO) is another semiconductor (p-type) renowned for its remarkable hole mobility and high theoretical specific capacitance making it a highly desirable contender for applications in a variety of sectors such as dye-sensitized solar cells and supercapacitors [24, 25]. Furthermore, NiO may be used to build p-n heterojunctions with a variety of n-type materials primarily due to its wide bandgap [26]. By reducing the recombination of photogenerated electron-hole pairs, these heterojunctions efficiently increase the efficiency of photocatalysis. The hybrid TiO₂/NiO nanorods produced by the sol-gel technique showed high photocatalytic activity for the degradation of methylene blue [27]. Additionally, ZnO/NiO porous hollow spheres, which were produced by the calcination of Ni-Zn bimetallic organic frameworks, had noticeably more photocatalytic activity for the reduction of CO₂ as compared to pure ZnO or NiO [28]. In addition, there are several benefits of depositing NiO onto g-C₃N₄. Firstly, NiO functions as a co-catalyst, facilitating effective charge transfer and electron-hole separation between the semiconductor and the chemical system. Furthermore, a large interfacial area is generated by the development of a NiO/g-C₃N₄ heterostructure, which enhances charge separation and facilitates the production of electron-hole pairs at the interface. Furthermore, effective photogenerated electron transfer from g-C₃N₄ to NiO is made possible by the heterojunction between NiO and g-C₃N₄, which reduces electron-hole recombination even further and improves overall photocatalytic performance [29]. ZnO combined with NiO may efficiently inhibit electron-hole recombination due to the synergistic interaction between the two semiconductors enabling pollutant degradation under both UV and visible light conditions [30].

Recently, researchers have also integrated graphitic carbon nitride (g-C₃N₄) with numerous semiconductors such as ZnO and NiO intending to substantially reduce recombination reactions resulting in enhanced sunlight absorption efficiency [31]. g-C₃N₄ has drawn a lot of scientific interest considering its appropriate band gap (2.7 eV) successfully allowing visible light absorption [32]. Furthermore, its inexpensive and non-toxic nature offers potential benefits in the photodegradation of organic pollutants and water splitting under visible light irradiation. Despite this, fast charge carrier recombination significantly reduces the photocatalytic efficiency of g-C₃N₄. To overcome the obstacle, several attempts have been rendered to improve the photocatalytic activity of g-C₃N₄ by combining it with other semiconductors and doping with metals or non-metals [33]. The development and fabrication of heterojunctions have emerged to be one of the most viable and efficient approaches for improving the photocatalytic efficiency of these mechanisms. Significantly higher photocatalytic activity has been observed in g-C₃N₄₋based nanocomposites (such as g-C₃N₄/ZnO, g-C₃N₄/TiO₂, g-C₃N₄/CeO₂ and g-C₃N₄/CuO based nanocomposites) as compared to pure g-C₃N₄ [34, 35].

This work provides an in-depth investigation of the facile synthesis, characterization, and utilization of g-C₃N₄/NiO/ZnO ternary nanocomposite-based photocatalyst for the degradation of methylene blue (MB) dye. The ternary nanocomposite was successfully synthesized via a facile co-precipitation approach. A comprehensive characterization was performed employing numerous techniques such as XRD, RAMAN, SEM, UV-Vis, EIS, and PL spectroscopic techniques. The photocatalytic activity of g-C₃N₄/NiO/ZnO ternary nanocomposite-based photocatalyst was measured. The different factors including concentrations of the photocatalyst, and initial dye concentration were assessed to optimize the dye and photocatalyst concentrations for the potential use. Finally, the impact of scavengers and the reusability of the photocatalyst were investigated for stability. The utilization of g-C₃N₄/NiO/ZnO ternary nanocomposite-based photocatalysts in the degradation of MB is not yet covered in any currently available research. This investigation will further explore our comprehension of the photocatalytic activity, reusability, and catalytic characteristics of g-C₃N₄/NiO/ZnO ternary nanocomposite.

2.1 Materials

Nickel nitrate hexahydrate (Ni(NO₃)₂.6H₂O), zinc nitrate hexahydrate (Zn(NO₃)₂.6H₂O), urea (CH₄N₂O), sodium hydroxide (NaOH), sodium carbonate (Na₂CO₃), ethanol (C₂H₅OH) and methylene blue (MB) dyes were purchased from Sigma Aldrich. The different solvents and reagents used in the study were of analytical grade and utilized devoid of any further purification.

2.2 Synthesis of g-C₃N₄/NiO/ZnO (CNZ) Nanocomposite

The facile co-precipitation approach was utilized to synthesize nanocomposite of zinc oxide, nickel oxide, and graphitic carbon nitride (g-C₃N₄/NiO/ZnO). 2.90 g of Nickel nitrate hexahydrate (Ni(NO₃)₂.6H₂O) and 2.97 g of zinc nitrate hexahydrate (Zn(NO₃)₂.6H₂O) were mixed together in 50 ml distilled water. Afterward, g-C₃N₄ (100 mg) in 50 mL NaOH solution was added to the above dispersion under stirring. The solution was vigorously stirred for 3 h to obtain a homogenous dispersion. The final product underwent an 8 h drying process after being thoroughly washed with ethanol and distilled water. The dry product was calcined for 3 h at 500°C (@ ramp rate of 5°C/min). Finally, the calcined powder was finely ground for subsequent analysis. The ternary nanocomposite was designated as CNZ for convenience. Figure 1 demonstrates the schematic design of g-C₃N₄/NiO/ZnO ternary nanocomposite-based photocatalyst. The NiO/ZnO, g-C₃N₄/ZnO, g-C₃N₄/NiO, ZnO, and NiO nanocomposites were synthesized using exactly the same procedure and were designated as NZ, CZ, CN, ZnO, and NiO, respectively. The g-C₃N₄ was prepared according to previous reports [36].

2.3 Measurement and Characterization

A Bruker D8 Advance diffractometer and BWS415-532S spectrophotometer were utilized for X-ray diffraction (XRD) and Raman analysis of the synthesized nanocomposites to gain insights into the structural mechanism. The morphology of g-C₃N₄/NiO/ZnO ternary nanocomposite and pristine ZnO, NiO, and g-C₃N₄ samples was studied using a Tescan VEGA 3 scanning electron microscope (SEM). A JENWAY spectrophotometer was used to record the UV-Vis absorption spectra in order to analyze the optical behavior. Bio-Logic VSP-1086 electrochemical workstation was utilized for the electrochemical impedance spectroscopic (EIS) analysis of the ternary nanocomposite. The charge transfer mechanism was examined using a photoluminescence spectrofluorometer.

The photocatalytic behavior of the CZN ternary nanocomposite was measured by monitoring the degradation of the dye (MB) in aqueous solution. Initially, the CZN ternary nanocomposite-based photocatalyst (0.05 g) was dispersed in an aqueous solution of MB (50 mL containing 10 mg/L). Prior to initiating the photoreaction, the mixture was thoroughly stirred for 90 minutes to establish an adsorption-desorption equilibrium, between the catalyst and the dye. To irradiate the solution, an 80 W xenon lamp was utilized to simulate sunlight. In order to avoid thermal catalytic effects and to keep the experiment at ambient temperature, cooling fans were employed. A spectrometer was used to determine the concentration of MB in a 10 mL sample collected at predetermined intervals. The concentration of the photocatalyst and the dye was also optimized and their influence on photocatalytic activity was examined. The reusability of CZN ternary nanocomposite-based photocatalyst was studied in comparison to commercially available ZnO nanoparticles solution up to 5 cycles. Electron capture tests were conducted using the same conditions in order to identify and scavenge the free radicals responsible for the degradation of MB. Ethanol, silver nitrate, and isopropyl alcohol (0.05 mM) were added as scavengers for holes (h⁺), electrons (e⁻), and hydroxyl radicals (•OH), respectively.

Figure 2a demonstrates the XRD pattern of different samples including g-C₃N₄, ZnO, NiO, CZ, and CNZ photocatalyst. The g-C₃N₄ sample exhibits a single diffraction peak at 27.60° well matching to (002) crystal face resulting from graphite structure (JCPDS No. 87-1526) affirming the existence of nanolayers of g-C₃N₄. Similarly, the XRD pattern of ZnO exhibited 2θ peaks at 31.81°, 34.62°, 36.27°, 47.70°, 56.68°, 63.11°, 66.44°, and 68.18° well correspond to (100), (002), (101), (102), (110), (103), (112), and (201) crystal planes of hexagonal wurtzite ZnO (JCPDS No. 36-1451), respectively, confirming the formation of ZnO nanoparticles [37]. The XRD pattern of NiO exhibited three diffraction peaks at 2θ, 37.26°, 43.31°, and 62.73° matches with (111), (200) and (200) crystal planes of NiO (JCPDS No. 04-0835) [38]. The XRD pattern of CZ was noted to be similar to that of ZnO with no peak observed for g-C₃N₄ might be due to the higher concentration of ZnO. However, no extra peak was observed due to the integration of g-C₃N₄ in ZnO corroborating the crystallinity of the nanocomposite. A slight change in peak position with a minor blue shift was observed for the target CNZ ternary nanocomposite. A new peak at 11.19° was observed in the CNZ sample corresponding to interlayer stacking of g-C₃N₄ nanosheets. Overall, the XRD pattern of CNZ ternary nanocomposite exhibited the successful incorporation of metal oxide semiconductors (ZnO and NiO) into g-C₃N₄.

Figure 2b displays the Raman spectra including g-C₃N₄, ZnO, NiO, and CNZ photocatalyst. Typically, graphitic carbon nitride has two noticeable bands that are slightly displaced. The existence of sp³-hybridized carbon is suggested by the D band (1343 cm^− 1), which can be explained by the material defects in structure and disordered regions. On the other hand, sp²-hybridized carbon is linked to the G band (1596 cm^− 1), which is in good agreement with previous reports [39]. The Raman spectrum ZnO nanoparticles (NPs) demonstrated different peaks at 432 cm^− 1, 577 cm^− 1, 1041 cm^− 1, and 1146 cm^− 1 corresponding to E_2H, E₁(LO), E₁(TO) + E₁(LO), 2P vibration modes of ZnO NPs [40]. The wurtzite structure of ZnO NPs is confirmed by a strong E_2H peak as corroborated by XRD measurements. NiO Raman spectrum exhibits characteristics peak of vibrational modes 1P TO mode (544 cm^− 1), 1P LO (656 cm^− 1), 2P LO + TO (1040 cm^− 1), 2P LO (1261 cm^− 1), and 2M (1731 cm^− 1) [41]. The Raman spectrum of CNZ ternary nanocomposite demonstrated slight displacement in peak positions attributed to the formation of an integrated structure produced by the incorporation of two metal oxide semiconductors (ZnO and NiO) into g-C₃N₄. However, the incorporation did not cause any noticeable change in the structure of ternary nanocomposite.

The surface morphology of the pre-synthesized samples was examined by SEM. Figure 3 displays the SEM images of pure g-C₃N₄, ZnO, and NiO along CNZ ternary nanocomposite. The pure g-C₃N₄ (Fig. 3a) resembles a stacked plate structure. This finding suggests that there is interconnectivity between the g-C₃N₄ sheets. ZnO exhibits morphology like spherical nanoparticles (Fig. 3b) with a diameter ̴ 50 nm and NiO also reveals nanoparticle morphology (Fig. 3c) but due to agglomeration the exact size of NPs is crucial to estimate. The surface morphology of g-C₃N₄/NiO/ZnO ternary nanocomposite-based photocatalyst shows a random morphology with NiO and ZnO NPs anchored onto g-C₃N₄ nanosheets. The ternary nanocomposite generated a heterojunction structure that can effectively separate photogenerated charge carriers, increasing charge transfer efficiency and performance all around. The aggregation in Fig. 3d also affirms the high surface area of the ternary nanocomposite, a prerequisite for effective degradations of pollutants.

UV-Vis absorption spectra were recorded at room temperature in order to evaluate the optical characteristics of pristine g-C₃N₄, NiO, ZnO, CZ, and CNZ photocatalysts. A narrow absorbance in the ultraviolet (UV) region was noticed for the majority of the synthesized samples (Fig. 4a). However, CNZ revealed better light absorption and a noticeable redshift in the absorption edge towards the visible range. The better light absorption and redshift in the absorption edge of CNZ ternary nanocomposite-based photocatalyst is consistent with previous studies on nanocomposites designed particularly for visible light absorption [42]. The enhanced light absorption in the visible range and noticeable redshift indicate that absorption characteristics of CNZ ternary nanocomposite-based photocatalyst are successfully improved by integrating ZnO and NiO into g-C₃N₄ nanosheets. As a result, CNZ ternary nanocomposite is beneficial for photocatalytic processes as it can absorb more photons of visible light, encouraging the formation of electron-hole pairs and reactive species.

The PL spectra of ZnO, NiO, NZ, and CNZ are illustrated in Fig. 4b. The emission spectra of ZnO NPs and NiO NPs exhibited highly intense but narrower peaks, suggesting an increased rate of charge carrier recombination. Nevertheless, a drop in PL intensity for NZ indicates that combining ZnO with NiO considerably lowers the recombination rate of electron-hole pairs. The CNZ ternary nanocomposite-based photocatalyst demonstrated a suppressed or lower peak intensity as compared to the NZ binary nanocomposite as well as NiO NPs and ZnO NPs. The results corroborate that the formation of heterostructures using g-C₃N₄, NiO, and ZnO may efficiently inhibit the recombination of electron-hole pairs generated during photocatalysis. Additionally, by inhibiting the photoinduced charge carriers, the synergistic impact improves charge separation and reduces the rate at which photogenerated charge carriers recombine. Further evidence of the increased electron-hole separation in the CNZ ternary nanocomposite was provided by electrochemical impedance spectroscopy (EIS) analysis. The EIS spectra of g-C₃N₄, NiO, ZnO, and CNZ are shown in Fig. 4c. The spectra demonstrate that CNZ has a lower arc radius in the Nyquist plot than the other samples, suggesting more effective transfer and separation of photogenerated charge carriers. The enhanced separation of photoinduced electron-hole pairs in CNZ is highlighted by this outcome.

Due to its numerous potential applications in the field of solar energy conversion, photocatalysis has become a highly promising technology that might alleviate global energy constraints and environmental pollutants. Only 4% of ultraviolet (UV) radiation can be recognized in solar light, an endless natural energy source; visible light makes up a far bigger share (46%). Thus, boosting the photocatalytic efficiency of semiconductors in visible and ultraviolet light has emerged as a crucial field of investigation for optimizing solar energy utilization. To investigate the synergistic impact of the CNZ ternary nanocomposite-based photocatalyst, the photocatalytic activities of different photocatalysts were examined for the degradation of MB solution, a model organic pollutant, under visible light irradiation. The photodegradation curves of MB to time using several samples of the photocatalysts under UV light irradiation are displayed in Fig. 5a. With a photodegradation efficiency (PE) of 92% after 60 minutes of exposure, CNZ demonstrated the best performance among all the evaluated samples. In the same testing conditions, it outperformed other photocatalysts such as NZ (79% PE), CZ (82% PE), CN (60% PE), ZnO (77% PE), NiO (63% PE), and g-C₃N₄ (38% PE).

The ternary nanocomposite CNZ exhibited the highest PE, followed by the CZ and NZ photocatalysts. These results suggest that the photocatalytic activity for pollutant degradation under irradiation is significantly enhanced by the formation of CNZ ternary nanocomposite. In order to provide a quantifiable comparison of photocatalytic performance, a pseudo-first-order kinetic reaction model (ln(c/c_o) = kt) was employed to analyze the collected data [43]. The MB concentration at a given irradiation time is denoted by c in this equation, while the rate constant is denoted by k and the irradiation period is indicated by t. With a correlation coefficient (R²) larger than 0.9, Fig. 5b shows a strong linear connection, suggesting that the photocatalytic reaction follows first-order kinetics. Table 1 displays the k and R² values for each photocatalyst that was utilized in the photodegradation of MB. The rate constant k for MB degradation using CNZ ternary nanocomposite-based photocatalyst is estimated to be around 0.0427 min^− 1 quicker than the rate constants for CZ (0.0293 min^− 1), CN (0.0155 min^− 1), NZ (0.0261 min^− 1), ZnO (0.0251 min^− 1), NiO (0.0161 min^− 1), and g-C₃N₄ (0.0080 min^− 1). These findings imply that the CNZ photocatalyst discloses a much better MB degrading efficiency as compared to all other samples. Therefore, it can be presumed that CNZ can be utilized as an optimized photocatalyst for enhanced photocatalytic activity.

Table 1

k and R² values using different photocatalysts.
Photocatalysts	k (min^− 1)	R²
CNZ	0.0427	0.9955
CZ	0.0293	0.9844
CN	0.0155	0.9841
NZ	0.0261	0.9807
ZnO	0.0251	0.9959
NiO	0.0161	0.9811
g-C₃N₄	0.0080	0.9973

We also measured the effect of CZN photocatalyst concentration and initial dye (MB) concentration by varying their masses to gain further insights into the optimization of the photocatalyst quantity and dye concentration. CZN photocatalyst concentration varied from 0.25 g/L to 1 g/L. The PE dramatically increased up to 0.75 g/L but then declined, as seen in Fig. 6a. It has been established that increasing the photocatalyst concentration can result in the generation of further charge carriers and active species, both of which are essential for the degradation of MB. Agglomeration in the dye solution, on the other hand, can also result from using excessive photocatalyst which can reduce the quantity of light entering the solution and consequently decrease photodegradation efficiency. The optimal photocatalyst concentration was thus determined to be 0.75 g/L of CZN, which would enable effective light absorption and prevent the demand for additional catalysts. The effects of initial dye concentration were also evaluated across a range of 5 to 20 mg/L on the photodegradation of MB using 0.75 g/L of CZN. As shown in Fig. 6b, the highest photocatalytic performance was noted for 15 mg/L MB concentrations.

There was a noticeable drop in the PE above this concentration. A higher concentration of MB can reduce the photoactivation of the catalyst for photodegradation since it can obstruct light from entering the reaction system. In addition, the PE decreases with increasing dye concentrations due to excess MB molecules which may block active sites and reduce their availability for photodegradation. In order to investigate the function of the energetic species in the photodegradation process of the CNZ ternary nanocomposite-based photocatalyst, trapping experiments were conducted and displayed in Fig. 6c. It was probed out how different reactive species, such as hydroxyl radicals (•OH), holes (h⁺), and superoxide radicals (•O₂⁻), contributed to photocatalytic degradation. To specifically quench these species, three types of trapping agents were used: AgNO₃ was used to trap O₂⁻ radicals, C₃H₈O for hydroxyl radicals, and C₂H₅OH was used to capture h⁺. The results reveal that adding 0.05 mM AgNO₃ (electron scavenger) resulted in a slight decrease in the photocatalytic degradation of methylene blue (MB) over the CNZ ternary nanocomposite. This indicates that the main active species involved in the degradation process are not photogenerated electrons. By contrast, the addition of C₃H₈O and C₂H₅OH (hydroxyl radicals and hole capture) greatly inhibited the photocatalytic activity. These results confirm that the primary oxidative species responsible for the photocatalytic degradation of MB are photogenerated holes and •OH radicals. Reusability is another crucial component in evaluating the practical performance of photocatalysts [44]. The synthesized CZN photocatalyst exhibited remarkable stability as shown by Fig. 6d by retaining 86% degradation efficiency for MB despite five cycles of reuse. The results confirm that CZN demonstrates long-term durability in photocatalytic applications. On the contrary, the degrading efficiency of MB using commercial ZnO decreased significantly with each cycle, reaching just over 62% after five cycles. The subsequent decrease in photocatalytic activity originates due to small particle size and high dispersion of ZnO, making it difficult to completely remove from the reaction system resulting in an enormous loss of ZnO powder. In contrast, the better surface morphology and improved absorption of CZN ternary nanocomposite-based photocatalyst make solid-liquid separation simpler. These results highlight the stability and reliability of the CZN ternary nanocomposite-based photocatalyst for MB degradation in the presence of sunlight.

The facile co-precipitation approach was employed to effectively synthesize a CNZ ternary nanocomposite-based photocatalyst, yielding substantial aggregates of g-C₃N₄, NiO, and ZnO. XRD and Raman studies confirmed the crystalline structure of ternary nanocomposite with high purity. Particularly, the nanocomposites show an extended absorption edge into the visible light spectrum, suggesting the potential of ternary nanocomposites, particularly for photocatalytic applications. CZN showed a significantly higher photoactivity than all other samples, achieving a degradation rate of 92% for MB. Further photocatalytic analysis revealed that a variety of parameters, such as initial MB concentration and photocatalyst quantity, influence the performance of CNZ. The ternary nanocomposites were also assessed by stability measurements over five successive reaction cycles confirming superior reusability in photocatalytic applications. The synergistic impact of the unique structure is mainly responsible for the improved photocatalytic performance. Furthermore, the degradation process is further enhanced by the increased number of active adsorption sites provided by the CNZ photocatalyst. We contemplate that combining distinct features of g-C₃N₄, NiO, and ZnO may realize possible applications in the fields of energy conversion and environmental purification, and open new avenues to develop more effective photocatalysts.

Acknowledgement

The authors would like to extend their sincere appreciation to the Researchers Supporting Project Number (RSPD2024R1118), King Saud University, Riyadh, Saudi Arabia for funding this study.

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Fabrication of g-C₃N₄/NiO/ZnO based Ternary Nanocomposite for Efficient Photocatalytic Degradation of Methylene Blue

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Version 1

Abstract

Figures

1. Introduction

2. Experimental Section

2.1 Materials

2.2 Synthesis of g-C₃N₄/NiO/ZnO (CNZ) Nanocomposite

2.3 Measurement and Characterization

3. Results and Discussion

4. Conclusions

Declarations

References

Additional Declarations

Status:

Version 1

Fabrication of g-C3N4/NiO/ZnO based Ternary Nanocomposite for Efficient Photocatalytic Degradation of Methylene Blue

Status:

Version 1

Abstract

Figures

1. Introduction

2. Experimental Section

2.1 Materials

2.2 Synthesis of g-C3N4/NiO/ZnO (CNZ) Nanocomposite

2.3 Measurement and Characterization

3. Results and Discussion

4. Conclusions

Declarations

References

Additional Declarations

Status:

Version 1

Fabrication of g-C₃N₄/NiO/ZnO based Ternary Nanocomposite for Efficient Photocatalytic Degradation of Methylene Blue

2.2 Synthesis of g-C₃N₄/NiO/ZnO (CNZ) Nanocomposite