Enhanced Photocatalytic Activity of Ficus elastica Mediated Zinc Oxide-Zirconium Dioxide Nanocatalyst at Elevated Calcination Temperature: Physicochemical Study

Abstract

The photocatalytic degradation of Rhodamine 6G dye was achieved using a Ficus elastica (F. elastic) leaf extract mediated zinc oxide-zirconium dioxide nanocatalyst (ZnO-ZrO₂ NC) under stimulated solar light, resulting in a substantial increase in photocatalytic activity at the highest calcination temperature. The crystal phase and crystallite size were determined using an X-ray diffractometer (XRD), and the degree of crystallinity was observed to rise with increasing calcination temperature. Energy dispersive X-ray (EDX) was used to investigate the elemental composition and purity of ZnO-ZrO₂ NC. Scanning electron microscopy (SEM) was used to investigate the surface morphology, and the morphological characteristics were altered when the calcination temperature was varied. For the ZnO-ZrO₂ NC calcined at 100, 300, 600, and 900 °C, the average grain size determined from SEM images is 79.56 nm, 98.78 (2) nm, 54.86 (2) nm, and 67.43 (2) nm, respectively. Using diffuse reflectance spectroscopy (DRS) data, the optical band gap energy was calculated using a Tauc’s plot. The ZnO in ZnO-ZrO₂ NC calcined at 100, 300, 600, and 900 °C had band gap energies of 3.31, 3.36, 3.38, and 3.29 eV. Similarly, ZrO₂ in ZnO-ZrO₂ NC calcined at 100, 300, 600, and 900 °C had band gap energies of 3.96, 3.99, 3.97, and 4.01 eV, respectively. Fourier transform infrared (FTIR) spectroscopy was used to identify the presence of various functional groups. The photocatalytic activity was also examined in relation to calcination temperature, pH, starting concentration, and catalyst dosage. Enhanced photocatalytic activity was observed at pH 11 and 15 ppm initial concentration with a catalyst dose of 25 mg. The photocatalytic activity of the sample calcined at 900 °C was the highest, with 98.94 percent of the dye mineralized in 330 min at a degradation rate of 0.01261/min.

1. Introduction

Environmental pollution has become a serious problem concerning to human health [1]. Paper, pulp, paint, varnishes, dyeing, petrochemical, cosmetics, ink, plastics, and textiles industries are releasing pollutants which affect the surrounding ecosystem [2]. During the process of dyeing, a large amount of dye is wasted and dumped into water. The industrial wastewater contains pathogens, agricultural and nutrients runoff, and organic and inorganic pollutants [3]. The wastewater which comes from the textile industries has a strong color and contains heavy metals, high concentrations of organic compounds, high pH, and high chemical oxygen demand [4]. Organic dyes are commonly used in today’s industry which have become a main source to create hazardous water pollutants [5]. These organic dyes are hazardous, toxic, carcinogenic, and badly affect the environment, human health, and aquatic ecosystems [2]. Several methods, such as ozonation, oxidation process, adsorption, ion exchange, membrane filtration, photocatalytic degradation, catalytic reduction, dialysis, and electrolysis, have been employed for the removal of dyes and other pollutants [5,6,7]. Photocatalysis is more appropriate method for the degradation of organic dyes due to eco-friendly and cost effect nature [8].

Transition metal oxides, metal–organic frameworks, and chalcogenides have been reported for photocatalytic degradation [9]. The semiconductor-assisted photocatalysis process has proven to be effective for the decomposition of organic pollutants found in wastewater, such as acids, dyes, and aromatic and phenolic compounds, due to its strong redox potential, environmental friendliness, moderate operation temperature, ease of operation, and useful final products [10]. Several attempted have been made to formulate highly stable and economical visible light driven photocatalysts with amendable band structure and low toxicity [11]. Binary nanocomposites of metal oxides increase the photodegradation efficiency as compared to individual metal oxide nanoparticles [12]. Silver and gold nanoparticles, NO₃/TiO₂ photoelectrodes, FePt-Ag nanocatalyst, and silver decorated magnetic nanocomposites were recently used as organic dyes reducing catalysts [1,4,13]. The ZnO/TiO₂ NC showed enhanced solar light-induced photocatalytic activity against brilliant green and methylene blue, whereas its activity was higher than the individual ZnO, TiO₂, and P-25 against 4-chlorophenol under low UV light. The chemically synthesized ZnO-ZrO₂ NC was used for the degradation of phenol, where activity was found to be higher than both the counterparts, and the activity also increased with the increasing ZnO in the sample. The ZnO and ZrO₂ are more focused due to the high stability, wide absorption range, and boosted oxidation property. ZnO is commonly used as a photocatalytic material due to its non-toxic nature and high thermal and chemical stability [14]. ZrO₂ is also used in photocatalytic reactions due to its low cost, re-useability, non-toxicity, excellent thermal stability, and inertness [15]. Binary composites of ZrO₂ and ZnO have recently been utilized for organic pollutant degradation, and enhanced photocatalytic activity has been connected to changes in their textural, structural, and optical characteristics. Additionally, the enhanced electron hole pair improves photocatalytic efficiency [16]. Recently, ZnO-ZrO₂ was synthesized via sol-gel, chemical precipitation, and hydrothermal methods; however, no literature was found for the green synthesis of ZnO-ZrO₂ [17]. So far, very limited data have been reported on the synthesized of ZnO-ZrO₂ NC and their biological and photocatalytic applications. However, no literature was found on the plant mediated synthesis of ZnO-ZrO₂ NC and the photocatalytic ability under several experimental condition. In addition, the effect of calcination temperature on the crystalline structure, composition, and photocatalytic action are yet to be reported.

In this study, the ZnO-ZrO₂ NC was synthesized by using F. elastic leaves extract and were calcined at 300, 600, and 900 °C. XRD, SEM, EDX, FTIR, and UV-Visible spectroscopy were used to investigate the structural characteristics. The photodegradation of Rhodamine 6G in its aqueous solution in the presence of artificial sunshine was achieved using synthesized pure and calcined ZnO-ZrO₂ NC. Mathematical formulae were utilized to calculate the degradation rate constant and % degradation of the photocatalyzed process.

2. Results and Discussion

2.1. XRD Analysis

The XRD diffractograms of ZnO-ZrO₂ NC calcined at 100, 300, 600, and 900 °C are given in Figure 1, which shows that the diffraction spectrum of ZnO-ZrO₂ calcined at 100 °C has no peak and are suggested to be amorphous. After increasing the temperature from 100 to 300 °C, the diffraction bands appeared in the spectrum at 2-theta position with corresponding hkl planes are 31.90 (100), 34.52 (002), 36.35 (101), 47.71 (102), 56.73 (110), 63.01 (103), and 68.08 (112). All these peaks, along with hkl planes, were found to be similar with those reported in the JCPDS card 01-075-0576, assigned to hexagonal-shaped ZnO with space group P63mc and space number 186. The crystallite size calculated with respect to the most intense diffraction band at 36.35° was 35.40 nm with a lattice strain of 0.313 percent. The length of three coordinates, i.e., a, b, and c, of orthorhombic ZnO was 3.2427, 3.2427, and 5.1948 Ǻ along with 90° of alpha and beta, and 120° of gamma, respectively. No diffraction band was observed for ZrO₂ in the XRD pattern of the ZnO-ZrO₂ calcined at 300 °C, depicting the amorphous nature of ZrO₂. The results were consistent with the previous data, where amorphous ZrO₂ was reported [15]. The diffraction peaks in the spectrum obtained for ZnO-ZrO₂ calcined at 600 °C at a 2 theta positions were 31.90, 34.52, 36.35, 47.71, 56.73, 63.01, and 68.08, with corresponding miller indices (100), (002), (101), (102), (110), (103), and (112), respectively. All these bands were matched with reference card 01-075-0576 and were assigned to the hexagonal geometrical shape of ZnO (having the same lattice parameters as stated above) with a space group of P63mc and space number 186. Another set of diffraction peaks at the 2-theta position, along with hkl values, were 30.44 (101), 35.46 (110), 50.33 (112), and 60.51 (211), corresponding to the JCPDS card No. 01-079-1771. These bands confirmed the tetragonal geometry of ZrO₂ with the space group and number of P42/nmc and 137, where a and b coordinates are of 3.5916 Ǻ while coordinate c is equal to 5.1790 Ǻ, where all the three angles are 90°. The crystallite size calculated for ZnO and ZrO₂ crystals were 70.90 and 23. 30 nm, with 0.157 and 0.563 percent lattice strain, respectively. The XRD pattern of ZnO-ZrO₂ calcined at 900 °C possessed similar diffraction bands at almost the same 2-theta positions with corresponding hkl planes explains the hexagonal and tetragonal geometrical shape of ZnO and ZrO₂. The crystallite size for the ZnO and ZrO2 in the ZnO-ZrO₂ sample calcined at 900 °C 105.83 and 41.80 nm with 0.105 and 0.317 percent imperfection in the crystals, respectively. A third set of Bragg’s reflections appeared in the diffractogram of ZnO-ZrO₂ calcined at 900 °C at 24.13, 28.31, 40.91, 49.35, 55.46, and 66.52 were found to be similar, with bands reported in reference card No. 00-032-1482 assigned to an unknown crystal system of ZnZrO₃ with a crystallite size of 59.42 nm and lattice strain of 0.239 percent. The three separate sets of diffraction bands in the spectra of ZnO-ZrO₂ calcined at 600 and 900 °C suggest the formation of hetero-structures. The intensity of diffraction peaks was seen to increase with increasing calcination temperature, revealing that the degree of crystallinity increased along with crystallite sizes. However, no shift was seen in the peak positions with increasing calcination temperature, suggesting that no phase transformation occurred.

2.2. SEM Analysis

The morphology and grain size of all annealed ZnO-ZrO₂ NC samples were measured using SEM and high magnification micrographics, as shown in Figure 2. The apparent borders between the grains vanish when the temperature rose from 100 to 300 °C, indicating that a condensation process occurred, culminating in the development of a solid structure with the evaporation of water molecules. A further rise in calcination temperature up to 600 °C indicates the degeneration/cracking of solid structure resulted in the formation of granular samples (small sized particles) due to heat treatment. The SEM micrograph (Figure 2d) shows that due to the high surface energy, granules were recombined into small–large-sized grains when the temperature was increased from 600 to 900 °C. Thus, the SEM analysis revealed that because of the change in calcination temperature, the phenomena of solidification/magnification, fragmentation, and coalescence occurred, steered to morphological changes. The average grain size determined from SEM images for the ZnO-ZrO₂ NC calcined at 100, 300, 600, and 900 °C was 79.56 (±3), 98.78 (±2), 54.86 (±2), and 67.43 (±2) nm, respectively. Grain sizes displayed anomalous behavior (decrease) after an unexpected rise in calcination temperature to 600 °C. Increasing the calcination temperature, on the other hand, caused grain size to increase. Amorphous content conversion, dehydration, particle rearrangement, and phase transition are the most plausible causes of grain size variation with calcination temperature. An increase in grain size from 100 to 300 °C may impede the calcination action of ZnO-ZrO₂ NC powder due to enhanced conversion (condensation) from the amorphous to the crystalline phase. The compact solid deteriorated and a rough surface sample was generated as a result of increasing the calcination temperature to 600 °C. An increase in the calcination temperature to 900 °C aided in the controlled nucleation and development of the ZnO-ZrO₂ grains.

2.3. FTIR Analysis

The wide band centred at 3429 cm⁻¹ indicates the stretching vibration of the OH group, whereas the two peaks at 1649.14 and 1558.14 cm⁻¹ indicate the bending vibrations of adsorbed water molecules and OH groups on the surface, respectively, in the FTIR spectra of ZnO-ZrO₂ NC calcined at 100, 300, 600, and 900 °C, as shown in Figure 3 [18,19]. The intensity at 1435.10 cm⁻¹ was assigned to the carbon–carbon stretching of organic compounds, whereas the bands at 1235.39 and 1073.03 cm⁻¹ indicate the bending vibrations of C–O–C and overlapping of C–O groups, respectively, which might have been present in the sample due to the use of plant material in the synthesis [13,20]. The strength of the above peaks decreased as the calcination temperature increased from 300 °C to 900 °C, which is due to the fact that water and other organic molecules evaporate at higher calcination temperatures. The bending vibrations of M–O–H bonds found on the surface groups were responsible for the band at around 1358.02 cm⁻¹ [16]. The vibration modes of Zr–O–Zr and O–Zr–O appeared at 873.59 and 656.90 cm⁻¹, respectively [16]. The wavenumber at 537.389 cm⁻¹ is associated with the Zn–O bond [18]. The band of 447.51 cm⁻¹ confirmed the formation of crystalline ZnO–ZrO₂ NC [20].

2.4. DRS Analysis

We calculated the band gap energy, which was the lowest energy required for electron excitation from the valance band to the conduction band [21]. The DRS spectrum of ZnO-ZrO₂ NC shows two absorption edges instead of one, suggesting the formation of ZnO-ZrO₂ heterojunction (Figure 4), as was also confirmed by XRD and FTIR analysis, where individual bands were seen for ZnO and ZrO₂. The DRS spectra for all calcined ZnO-ZrO₂ samples shows an absorption band in the range of 353 to 370 nm attributed to the excitation of electron from valance band to conduction band (O2p→Zn3d). The spectrum also shows another absorption edge appeared at a lower wavelength in the range of 293–303 nm due to the presence of Zr in the form of Zr⁴⁺ and the excitation of an electron from the valance band (O2p) to the conduction band (Zr4d). The absorption edges for ZnO and ZrO₂ in the ZnO-ZrO₂ samples calcined at 100, 300, 600, and 900 °C were found to be in close agreement with reported data [14]. The presence of two edges can be seen for ZnO-ZrO₂ materials and a band gap can also be determined through a Tauc plot. All the calcined ZnO-ZrO₂ NC revealed higher transmittance in the visible region and lower transmittance in the UV region [22,23]. The band gap energy for ZnO in ZnO-ZrO₂ heterojunction calcined at 100, 300, 600, and 900 °C were 3.31, 3.36, 3.38, and 3.29 eV, respectively. Similarly, the band gap energy for ZrO₂ in ZnO-ZrO₂ heterojunction calcined at 100, 300, 600, and 900 °C were 3.96, 3.99, 3.97, and 4.01 eV.

2.5. EDX Analysis

As shown in Figure 5, the elemental composition and purity of the synthesized ZnO-ZrO₂ NC were investigated using EDX. Zn is responsible for the sharp peaks at 1, 8.6, and 9.5 keV, whereas Zr is responsible for the peaks at 2, 2.5, 15.75, and 17.6 keV. The presence of a peak for O at 0.5 keV suggests that zinc and zirconium oxides were formed. The other peaks at 0.2 and 0.3 keV are due to Cl and C, which were caused by the chloride salt of the precursor and the carbon tape used during the EDX analysis. Zn, Zr, O, and Cl have weight percentages of 42.7, 34.1, 22.6, and 0.4 percent, respectively.

2.6. Photocatalytic Activity

The photocatalytic degradation of Rhodamine 6G in the presence of stimulated solar light was demonstrated utilizing ZnO-ZrO₂ NC. The reaction mixture was agitated in the dark for 30 min before being exposed to stimulated solar light, and the changes in absorbance maxima were measured using a double beam spectrophotometer. After exposure to stimulated solar light, a decrease in absorbance maxima with respect to time was examined, as shown in Figure 6a. The % degradation (as given in Figure 6b) and degradation rate constant (Figure 6c) of Rhodamine 6G were calculated by using Equations (1) and (2), (where C_o is initial absorbance and C_t is the absorbance after time (t)) respectively [24]. Where C_o denotes the starting concentration, C denotes the end concentration, C_t is the concentration of Rhodamine 6G following exposure to stimulated solar radiation, and k denotes the reaction rate constant. The percentage degradation of Rhodamine 6G was recorded to be 98.39, 97.78, 96.71, and 98.94 percent with the degradation rate constant of 0.0125, 0.0099, 0.00965, and 0.01261 per min. Based on the photocatalytic potential, ZnO-ZrO₂ NC calcined at 900 °C are the most efferent photocatalysts under the applied experimental condition. The stability of the ZnO-ZrO₂ NC calcined at different temperatures was tested under the current experimental conditions five times, and after 330 min, a fresh solution was added to the reactor. The same process was repeated five times for each calcined catalyst. The percent degradation recorded during stability test in the presence of ZnO-ZrO₂ calcined at 100 °C are 98.39, 96.54, 93.68, 8.92, and 84.46; for ZnO-ZrO₂ calcined at 300 °C are 97.78, 96.04, 92.30, 87.76, and 81.58; for ZnO-ZrO₂ calcined at 600 °C are 96.71, 93.88, 90.57, 86.67, and 79.02 and for ZnO-ZrO₂ calcined at 900 °C are 98.94, 97.08, 95.03, 91.46, and 86.93 % during 1st, 2nd, 3rd, 4th, and 5th cycles respectively. This shows the stability of the synthesized ZnO-ZrO₂ NC, and can be used for several-step degradation of organic pollutants. Based on the stability test, the catalysts calcined at 900 °C are more stable followed by the one calcined at 100 °C, whereas the ZnO-ZrO₂ calcined at 600 °C is the least stable among these catalysts.

On the basis of available literature, the photocatalytic efficiency of ZnO, ZrO₂, and ZnO-ZrO₂ nanostructures was compared as shown in

Table 1. Photocatalytic efficiency of ZnO, ZrO₂ and ZnO-ZrO₂ nanostructures against different organic pollutants.

Dye	ZnO		ZrO2		ZnO-ZrO2		References
	% Degradation	Time (min)	% Degradation	Time (min)	% Degradation	Time (min)
Methyl orange	99.55	80	99	110	No literature found		[28,29]
Phenol	74	120	78	320	89	120	[15,30]
Congo red	30	11	98	125	90	120	[31,32]
Methylene blue	87	90	11	70	97	30	[15]
2-Chlorophenol	61	60	51	240	No literature found		[33,34]
Rhodamine 6G	55.51	180	No literature found		98.94	330	[35] and present study

. The reported data clearly shows that the ZnO-ZrO₂ NC exhibits significantly enhanced photocatalytic activity against different organic pollutants, which might be due to the synergistic effect of both counterparts.

$$\% degradation=\frac{C_o-C_t}{C_o}\times 100$$

(1)

$$ln\left(\frac{C}{C_o}\right)=-kt$$

(2)

In the presence of a stimulated solar light source, ZnO-ZrO₂ NC destroys Rhodamine 6G. When photons of light reach the surface of the catalyst, an outermost electron is activated. The excited electron oxidizes the oxygen in the reaction mixture, forming an oxygen anion radical. To breakdown the dye, the oxygen ion radical interacts with Rhodamine 6G and transforms it into a simpler organic molecule [21,25]. A schematic diagram for the degradation of Rhodamine 6G is shown in Figure 6d. When the ZnO-ZrO₂ NC is activated by solar light, electrons migrate from the valence bands of both oxides to the conduction band, forming electron–hole pairs. Because the energy levels of zinc oxide fit nicely within the band gap of ZrO₂, electrons from the conduction band of zirconium dioxide may readily migrate to the conduction band of ZnO [26]. On the other hand, holes move from the valence band of ZnO to the valence band of ZrO₂, potentially reducing electron–hole pair recombination in ZnO-ZrO₂ NC. These e⁻ and h⁺ radicals react with oxygen and water to create (OH•) radicals, which may quickly oxidize Rhodamine 6G due to their high reactivity and production of water and carbon dioxide [27].

2.7. Factors Affecting the Photocatalytic Activity

The parameters like initial concentration, catalyst dose, pH, and calcination temperature greatly affect the photocatalytic activity of the ZnO-ZrO₂ NC and obtained data is depicted in Figure 7a–d. This effect is briefly explained below:

2.7.1. Effect of Calcination Temperature

The synthesized ZnO-ZrO₂ NC was calcined at 100, 300, 600, and 900 °C and the effect of calcination temperature was examined on the photocatalytic degradation of Rhodamine 6G. As studied in the XRD and SEM analysis, the sample phase and morphological parameters were constantly changed with increasing calcination temperature, which has a great influence on the photocatalytic efficacy of the ZnO-ZrO₂ NC. With increasing calcination temperature, a regular decrease in the photocatalytic activity was seen, which might be due to the transformation of the amorphous phase into the crystalline phase. The maximum photocatalytic activity was experienced for the sample calcined at 900 °C, where almost 98.94 percent of the dye was degraded in 330 min, where the maximum amount of the ZnO-ZrO₂ NC was converted into crystalline form. Moreover, the sample calcined at 900 °C contained three type species like ZnO, ZrO₂, and ZnZrO₃ (XRD analysis), which might have a potential effect on the photodegradation of Rhodamine 6G [36].

2.7.2. Effect of Catalyst Dose

Different quantities of ZnO-ZrO₂ NC (i.e., 5, 10, 15, 20, 25, and 30 mg) were used to investigate the effect of the catalyst on the photo-induced mineralization of Rhodamine 6G. A gradual increase in the photocatalytic activity was observed with the increase in the catalyst amount up to 25 mg, whereas a steady decrease was observed upon further increase of the catalyst. The increase in the degradation process is credited to the formation of active sites that promote degradation, whereas the quantity of catalyst more than 25 mg blocks the penetration of light, thus reducing the photodegradation of the dye [37].

2.7.3. Effect of Initial Concentration of Dye

In the present study, different concentrations of Rhodamine 6G (i.e., 5, 10, 15, 20, 25, and 30 ppm) were exposed to 25 mg of ZnO-ZrO₂ NC to scrutinize the effect of the initial concentration of the dye on its degradation. The results showed that the maximum degradation was seen at 15 ppm, where the concentration above 15 ppm results in a clear decrease in the degradation of Rhodamine 6G. This decrease in the degradation can be attributed to the phenomenon that at high initial concentration of the dye, maximum light is absorbed by the dye molecules rather than the photocatalysts, consequently reducing the degradation [38].

2.7.4. Effect of pH

To test the influence of pH on Rhodamine 6G degradation, 25 mg of ZnO-ZrO₂ NC was introduced to eight reaction vessels containing 50 mL of dye solution (15 ppm) each, while all other reaction conditions remained constant throughout the experiment. According to the findings, the greatest degradation occurred at pH 11. This demonstrates that the pH values have a significant impact on the photocatalytic degradation of Rhodamine 6G. The production of hydroxyl radicals (powerful oxidizing agents) that contribute to the degradation of Rhodamine 6G causes the greater degradation in the basic media [39].

3. Materials and Methods

3.1. Materials

The chemicals required for this study included zircon (IV) chloride, zinc chloride, sodium hydroxide, and Rhodamine 6G were purchased from Sigma-Aldrich, St. Louis, MO, USA. The F. elastic leaves were collected, and their aqueous extract was used as a reducing and capping agent for the synthesis of ZnO-ZrO₂ NC.

3.2. Preparation of F. Elastic Leaves Extract

The F. elastic leaves were collected and washed with tap water to get rid of dust particles, followed by distilled water to purify and kept for drying. Fifty grams of dried leaves were placed in a beaker with 1000 mL of distilled water and heated until a thick green color appeared. The F. elastic leaves extract was filtered and centrifuged for 20 min at 4000 rpm before storing the top clear layer at room temperature.

3.3. Synthesis of ZnO-ZrO₂ NC

Nanoparticles of ZrO₂ and ZnO were prepared by individual mixing of 50 mL of zircon (IV) chloride (1.28 g) and zinc chloride (1.05 g) solution with 20 mL of the prepared extract agitated at 70 °C. The pH of both reactions was fixed at 10 by the addition of NaOH solution and constantly heated and stirred for 30 min, and the obtained precipitate was aged for 5 hours. To eliminate the chloride ion and other contaminants, the precipitates were washed three times with distilled water and dried in an oven at 100 °C.

Next, both the ZrO₂ and ZnO NPs were dissolved in 30% (v:v) nitric acid individually and mixed together at 70 °C with vigorous stirring. The NaOH solution was added to get the pH up to 10, and the mixture was continually agitated for 6 hours. The finished product was cleaned four times with distilled water before being dried overnight at 100 °C in an oven. Using a pestle and mortar, the dry product was crushed into fine powder and stored in a plastic bottle. The whole procedure was repeated until the desired amount of product was obtained. The product was then calcined at 300, 600, and 900 °C for 3 h in a muffle furnace, respectively.

3.4. Characterization

The physicochemical properties such as the crystal structure, surface morphology, crystal size, and percent composition of the synthesized sample were characterized by using XRD, SEM, EDX, DRS, and FTIR spectroscopy. The Debye–Scherrer equation was used to compute the crystallite size of the ZnO-ZrO₂ NC, and the crystalline nature was examined using the XRD model Philips X’Pert PW 3040, manufactured by CAE, Montreal, Canada. The microstructure and surface topology were investigated using a SEM model JEOL JSM-5600LV (made in Tokyo, Japan). An energy-dispersive X-ray (EDX) examination was done with a JEOL JSM-5600LV (made in Tokyo, Japan) combined with a scanning electron microscope (SEM) to confirm the sample’s composition, while surface functional moieties were investigated using an FTIR model Nicolet 560 (Thermo Fisher Scientific Waltham, MA, USA) operating in the 4000–400 cm⁻¹ range. The transmittance edge was measured using a DRS analysis was carried out by DRS (Thermo Fisher Scientific Waltham, MA, USA) in the range of 200–1000 nm, and the band gap energy was estimated using a Tauc’s plot.

3.5. Photocatalytic Activity

For the degradation of Rhodamine 6G, the synthesized ZnO-ZrO₂ NC was employed, and 20 mg of ZnO-ZrO₂ NC was added to 50 mL of Rhodamine 6G solution for each experiment. The experiment was subjected to a simulated sun light lamp, model US800, 250W with the wavelength range of 280–800 nm, after 30 min of stirring in the dark. The variations in absorbance maxima as a function of time were detected using a double beam spectrophotometer after a particular time period.

4. Conclusions

Ficus elastica extract was used for the synthesis of ZnO-ZrO₂ NC due to its non-toxicity and eco-friendly nature. The prepared ZnO-ZrO₂ NC was calcined at different temperatures to determine the effect of calcination on photodegradation and physicochemical properties. The XRD result shows that the degree of crystallinity along the crystallite sizes increases with increasing calcination, and maximum crystallinity was reported at elevated temperatures. The SEM analysis revealed that the variation in the surface properties occurred due to the dehydration and rearrangement of particles under the influence of heat, which resulted in the degeneration of highly agglomerated samples (compact solids) into small particles. The elemental composition study revealed that the desired elements were present in the sample. The physicochemical study revealed the synthesis of a ZnO-ZrO₂ heterojunction where the counterparts (ZnO and ZrO₂) have different crystal and optical properties. The changes in the degradation of dye with increasing calcination temperature are attributed to the stability of the sample, phase transformation from amorphous to crystalline phase, and variation in structural properties. The stability test shows that the ZnO-ZrO₂ calcined at 900 °C was the most stable catalyst, followed by the one calcined at 100 °C, whereas the catalyst calcined at 600 °C showed the lowest photocatalytic activity.