Citrus sinensis and Musa acuminata Peel Waste Extract Mediated Synthesis of TiO2/rGO Nanocomposites for Photocatalytic Degradation of Methylene Blue under Visible Light Irradiation

Water pollution caused by various natural and artificial sources such as expansion of industrialization, rapid increment in population size, the threat of climate change, and development in urbanization takes a serious attention. Due to this fact, various protocols and techniques were adopted for the treatment of such polluted water. In the present findings, TiO2 nanoparticles (NPs) and TiO2/rGO nanocomposites (NCs) were synthesized using titanium tetra butoxide in the presence of Citrus sinensis (CS) and Musa acuminata (MA) peel waste extract as a capping, reducing, and stabilizing agent. The synthesized NPs and NCs were characterized using thermogravimetric-differential thermal analysis (TGA/DTA), X-ray diffraction (XRD), scanning electron microscope (SEM), high resolution transmission electron microscopy (HR-TEM), selected area electron diffraction (SAED) pattern, ultraviolet diffuse reflectance spectroscopy (UV-DRS), and Fourier transform infrared (FTIR) spectroscopy. The synthesized NPs and NCs were investigated as green alternative photocatalyst for the degradation of methylene blue (MB) dye under visible light irradiation. Thermal analysis results confirmed that the green synthesized TiO2 NPs were found to be too stable above 550°C. XRD analysis result showed that the average crystalline size of CS and MA mediated synthesized TiO2 NPs with various volume ratios was in the range of 7.3–27.3 nm and 13.4–22.4 nm, respectively. The average crystalline size of CS and MA peel extract template synthesized TiO2/rGO NCs was found to be in the range of 7.5–15.3 and 11.2–12.5 nm, respectively. The band gap energy was calculated to be in the range of 3.17–3.29 eV and 3.10–3.38 eV for the CS and MA mediated synthesized TiO2 NPs, respectively. Eg of CS and MA peel extract template formed TiO2/rGO NCs was found to be in the range of 2.85–3.11 eV and 3.07–3.11 eV, respectively. SEM analysis proved that the various synthesized TiO2 NPs and TiO2/rGO NCs were spherical in shape and the absence of any other foreign materials confirmed the purity of the corresponding nanocatalysts. In addition, TEM, HRTEM, and SAED analysis confirmed that the structures of the synthesized nanocatalysts were spherical in shape and the catalysts were too crystalline and the result was found to fit with the XRD result. Among the synthesized various volume ratios of TiO2 nanocatalysts, high percentage of degradation (62% and 58.2%) was achieved using TiO2-2c and TiO2-2 m, respectively. Moreover, 94.28% and 94.25% of MB degradation were achieved in the presence of TiO2/rGO-1.5c and TiO2/rGO-1.5c nanocomposite photocatalysts, respectively.


Introduction
e natural ecosystem has been exposed to various natural and artificial hazardous problems due to overpopulation growth, advancements in urbanization, accumulation of agricultural fruit and vegetable wastes and industrial wastes including organic dyes, pesticides, inorganic contaminants and detergents, and heavy and toxic metal ions, and the decomposition of toxic and poisonous gases and chemical species produced from various chemical industries. Among these, the discharge of various types and nature of dye effluents from various chemical industries and sources such as dye stuffs, textiles, paint and varnishes, inks, plastics, pulp and paper, food, rubber, and cosmetics to the environment is a prime cause of concern nowadays worldwide [1 -3]. us, it has been reported that developing and designing of an efficient and convenient removal protocol of these various types of pollutants from wastewater is becoming an urgent and challenging issue worldwide [4,5].
Currently, various semiconductor-based nanomaterials have attracted a significant interest for the purification and treatment of wastewater. Among these, nanosized metal oxide photocatalysts such as TiO 2 , CuO, Co 3 O 4 , ZnO, ZnS, CdS, Fe 2 O 3 , MgO, Mn 2 O 3 , ZrO 2 , V 2 O 5 , Nb 2 O 5 , and WO 3 have been investigated and used in the process of wastewater decontamination. Particularly, wastewater decontamination using high surface area semiconductor nanocomposite photocatalysts prepared via numerous techniques has shown improved potential. Previously, it has been reported that TiO 2 NPs has been abundantly used and selected as the most reliable candidate as an environmentally clean and pristine photocatalyst due to its desired chemical properties, favorable optical effects, chemically balanced and photochemical stability, dielectric properties, biological and chemical inertness, high redox potential, and good photocatalytic efficiency and nontoxicity [6][7][8][9]. Even though TiO 2 NPs is a material of choice as effective photocatalyst candidate for the purification of water contains pollutants, several limitations such as fast recombination of photo excited electron-hole pairs, wide band gap energy ( ≈ 3.2 eV), and agglomeration have been reported [10]. is intern implies that single TiO 2 nanocatalyst could tend to aggregate, agglomerate, narrow spectral band, and show high photo-generated charge recombination rate and this results in shrinking surface area and inferior photocatalytic performance and so lower degradation efficiency [11].
In order to improve and enhance the photocatalytic activity of TiO 2 NPs, several approaches have been revised such as metallic and nonmetallic doping, conductive polymer doping, dye sensitization, and formation of composite by using various synthesis methods. Among these adapted techniques of preventing the electron-hole recombination rate, TiO 2 -based composite nanophotocatalysts are the most reliable and cost-effective candidates. Previously, TiO 2based nanocomposite materials such as TiO 2 /ZnO, g/TiO 2 , Bi 4 Ti 3 O 12 /Bi 2 Ti 2 O 7 , and Au/TiO 2 were synthesized via various chemical synthetic protocols for photocatalytic applications [12,13]. Various physicochemical synthesis protocols for TiO 2 -based nanocomposites including the green approach were also reported. Among these techniques, the green synthesis approach is ecofriendly, inexpensive, and easily manageable as it involves the use of green alternative starting materials (extract of plants, bacteria, algae, and fungi) as a template and green solvents such as ethanol and distilled water and nontoxic and less toxic precursors/salts [14].
Citrus sinensis represents the largest citrus cultivar groups grown around the world, accounting for 70% of the total annual production of Citrus species. Citrus sinensis peel waste is a rich source of various secondary metabolites which include flavonoids, steroids, hydroxyamides, alkanes, and fatty acids, coumarins, peptides, carbohydrates, carbamates, alkylamines, and carotenoids [15]. Similarly, Musa acuminate which is commonly called banana is herbaceous plant and belongs to the family of Musaceae. e plant is well known by its various bioactive compounds such as enzymes, polyphenol oxidase, pectin as gelling agent, vitamin A, gallocatechol, dopamine, vitamin E, vitamin B6, sitosterol, malic acid, succinic acid, and palmitic acid [16]. In addition to their medicinal usage for the treatment of various alignments and as sources of food, the peel part of the fruits could be accessed with zero cost and employed as a capping and reducing agent for the synthesis of various metal, metal oxides, composites, and doped nanomaterials for various applications.
Previously, several studies and reports have been focused on investigating the photocatalytic activity of chemically synthesized and to some extent green mediated obtained single TiO 2 oxide NPs for the degradation of various organic pollutants for the remediation of polluted water caused by various sources. Moreover, earlier reports show that TiO 2 /rGO nanocomposites were synthesized by various chemical synthesis protocols for the remediation and recovery of wastewater contaminated by numerous sources. However, to the knowledge of us as researchers, still now there is not any scientific report on the green synthesis of TiO 2 /rGO nanocomposites in the presence of peel extract of Citrus sinensis and Musa acuminata as cost-effective capping and reducing agent for the efficient photocatalytic degradation of methylene blue dye. Furthermore, no previous comparative works were presented on the effect of Citrus sinensis and Musa acuminata peel waste extracts on the green alternative synthesis of TiO 2 /rGO NCs and their effect on the degradation of water pollutants. erefore, the present work focuses and intensifies on the synthesis of TiO 2 NPs and TiO 2 /rGO NCs within various volume ratios characterization and investigates the photocatalytic degradation of methylene blue dye under visible light irradiation.

Collection and Extraction of the Peel Wastes.
e fresh and healthy fruits of Citrus sinensis (sweet orange) and Musa acuminata (banana) were collected from the local available market of Adama City, Oromia Region, Ethiopia. e collected samples were washed several times using distilled water to remove surface dust particles. en, the peel parts were taken using knife and were allowed shadow drying. e peels were then grinded and packed in a glass bottle followed by covering with aluminum foil to avoid photooxidation.
e extraction was carried out by taking 15 g of fine peel powder of each peel and then added into 500 mL conical flask separately followed by adding 250 mL of distilled water. Each of the mixtures of water and peel powder present in the separated conical flask was then boiled at a constant temperature of 70°C for 45 minutes and stirred using a magnetic stirrer at 1000 rpm and cooled to room temperature and filtered using watchman filter paper. Finally, the filtrates were stored at 4°C in a refrigerator for the synthesis of TiO 2 NPs TiO 2 /rGO nanocomposites [17].

Citrus sinensis and Musa acuminata Peel Extract
Mediated Synthesis of TiO 2 NPs. TiO 2 nanoparticles were synthesized via sol-gel method using titanium tetra butoxide as a precursor in the presence of Citrus sinensis and Musa acuminata as capping and reducing agent in three different volume ratios (1 : 2, 1 : 1, and 2 : 1). In typical reaction, 0.25 M of 40, 50, and 60 mL of C 16 H 36 O 4 titanium precursor solutions were added into three different Erlenmeyer flasks followed by stirring for 30 minutes to maintain homogeneity. en, in each Erlenmeyer flask containing the precursor solution, 60, 50, and 40 mL of Citrus sinensis peel extract were added drop by drop, respectively, and labeled as 1 : 2 (TiO 2 -0.5c), 1 : 1 (TiO 2 -1c), and 2 : 1 (TiO 2 -2c). e reaction mixtures were stirred for 5 hours using magnetic stirrer at room temperature. en, afterward, 17 mL of 1 M NaOH solution was added dropwise to facilitate precipitation and was stirred for 30 minutes in order to maintain the homogeneity of the solution and the formed suspensions were kept at 4°C in a refrigerator overnight for further use. e three different volume ratio suspensions were then centrifuged three times at 4000 rpm followed by washing three times using distilled water and absolute ethanol followed by collecting using crucible ceramic dish and then oven dry. e thermal stability of the dried samples was tested by taking the 1 : 1 ratio from each of the peel waste mediated synthesized TiO 2 samples. Based on the thermal stability result, the three ratios of Citrus sinensis peel extract mediated synthesized TiO 2 NPs were calcined at 500°C for 4 hours [18]. e same protocol was followed for the Musa acuminata peel extract mediated synthesis of TiO 2 NPs and labeled as 1 : 2 (TiO 2 -0.5 m), 1 : 1 (TiO 2 -1 m), and 2 : 1 (TiO 2 -2 m). Figure 1 shows the schematic synthetic procedure of TiO 2 NPs in the presence of Citrus sinensis peel waste extract.

Synthesis of Graphene Oxide (GO).
Synthesis of GO was carried out following the modified tour method [19]. e synthesis procedure involved oxidation of graphite using strong oxidizing agent (KMnO 4 ) in the presence of H 3 PO 4 to prevent further possible oxidation [20]. en, afterwards, 0.5 g of graphite powder was exfoliated using 90 mL of H 2 SO 4 followed by addition of 50 mL Citrus sinensis peel waste extract in the presence of H 3 PO 4 at 0°C in ice bath followed by gradual and stepwise addition of 4.5 g KMnO 4 .
en, the components were stirred for 8 hours while heating at 50°C using a temperature-controlled water bath. As the reaction time was extended and increased, the mixture turned out to paste. e reaction was then terminated by the addition of 250 mL of distilled water followed by addition of 10 mL H 2 O 2 (30%) solution to reduce residual KMnO 4 to soluble manganese sulfate (MnSO 4 ) in an acidic medium. e formed suspension was then filtered to remove the metal sulfate and a graphite oxide filter cake was produced. e cake was then again washed using 5% of HCl until the sulfate ions are completely removed, which was confirmed using BaCl 2 solution. e formed graphite oxide was washed three times at each centrifugation process at 1000 rpm for 30 minutes. e collected graphite oxide was added to 100 mL of distilled water and stirred followed by heating at 60°C for 8 hours in water bath. e brown colored GO solution was dried at 60°C for 6 hours in oven drier. Figure 2 displays the resulting schematic synthesis protocol of rGO in the presence of peel waste extract of Citrus sinensis as a green alternative template.

Citrus sinensis and Musa acuminata Peel Extract Mediated Synthesis of TiO 2 /rGO Nanocomposites.
e TiO 2 /rGO nanocomposites were prepared using synthesized GO and TiO 2 via precipitation method in the presence of peel waste extract of Citrus sinensis (CS) and Musa acuminata (MA) as both reducing and stabilizing agent [21]. In a typical procedure, GO suspension was prepared by dispersing dried 30, 60, and 90 mg powders in 100 mL of distilled water by the process of sonication. Subsequently, 60 mg of TiO 2 and 50 mL of CS extract were added into the GO slurry and stirred for 8 h at room temperature.
en, the solution turned to gray from brown colors indicating the reduction of GO to reduced graphene oxide (rGO). e gray residue of the formed rGO/TiO 2 -0.5c, rGO/TiO 2 -1c, and rGO/TiO 2 -1.5c nanocomposites was then centrifuged for a minimum of 30 minutes followed by washing three times using distilled water and absolute ethanol sequentially at each step of centrifugation to remove impurities. e obtained nanocomposites were then kept in vacuumed oven at 100°C for 24 hours for further analysis. e same procedure was followed for the Musa acuminata peel extract mediated synthesis and labeled as TiO 2 /rGO-0.5 m, TiO 2 /rGO-1 m, and TiO 2 /rGO-1.5 m nanocomposites.

Characterization.
e thermal stability analysis study was done using a simultaneous TGA-DAT (DTG-60H, SHI-MADZU Corporation, Japan). e crystal structure, average crystalline size, and phase stability of synthesized TiO 2 NPs and TiO 2 /rGO nanocomposites were analyzed by XRD (XRD-7000, SHIMADZU Corporation, Japan) equipped with a Cu target for generating a Cu Kα radiation with λ � 0.15406 nm and recorded in the range from 10°C to 80°. e morphological structure of each type of synthesized NPs and NCs was investigated using SEM. For further analysis and insights, the synthesized TiO 2 NPs and TiO 2 /rGO nanocomposites were characterized using TEM, HRTEM, and SAED techniques. e optical property of both TiO 2 NPs and TiO 2 /rGO nanocomposites was studied using UV-DRS (OPTIMA UV-Vis spectrometer SP-3000 Plus, SHIMADZU Corporation, Japan). Functional group analysis was studied using FTIR (FT/IR-6600 type A, JASCO Company, Japan) characterization techniques. e photocatalytic degradation studies of TiO 2 and TiO 2 /rGO nanocomposites were carried out in 125 ml of Pyrex flask type reactor under 150W halogen lamp irradiation. e degradation analysis was followed and recorded using double beam UV-visible spectrophotometer (SM-1600 spectrometer MAALAB, India).    e first stage weight loss observed between 40 and 194°C was attributed to the removal of physically and chemically entrapped water and other moisture contents from the surface of the synthesized TiO 2 nanoparticles. e second stage weight loss observed in the range of 195-503°C could be attributed to the losses of organic residues and organic molecules/compounds as a result of combustion and carbonization of biomass materials from the synthesized TiO 2 NPs. Furthermore, no considerable weight loss was observed above 510°C which proved that the synthesized TiO 2 NPs using Citrus sinensis (Figure 3(a)) and Musa acuminata (Figure 3(b)) peel waste extract was found to be nearly pure and thermally stable and hence temperature of 550°C was selected as a calcination temperature [22][23][24].  (215), respectively. is corresponds to the standard pattern of the anatase crystalline phase form of TiO 2 NPs with JCPDS card number of 21-1272 with tetragonal structure. e absence of any foreign materials and secondary phases is an indication of the high purity and stability of the NPs and NCs synthesized using fruit peel waste extracts. e various volume ratios of TiO 2 NPs, TiO 2 -0.5c, and TiO 2 -0.5 m NPs showed less crystalline nature as compared to the other volume ratios due to the large amount of the peel extracts used which is in good agreement with previous report [25]. e average crystalline size of the synthesized NPs from various volume ratios was calculated using Debye Scherrer equation [26] and was found to be 27.  respectively. It was found that the synthesized TiO2-rGO NCs possess a diffraction pattern similar to that of a single TiO 2 NPs. Due to the small quantity and low intensity of rGO, there was no separate peak for the rGO within the TiO 2 -rGO NCs [27]. Previously, similar results were reported for the TiO 2 -activated carbon nanocomposites [28]. In addition to this, in both of the peel waste extracted mediated syntheses, the low peak intensity was due to the incomplete oxidation of graphite oxide and the cluster of bioactive constituents of the peel waste extract of Citrus sinensis and Musa acuminata added during the synthesis process [27][28][29][30].

XRD Analysis.
Figures 4(e) and 4(f ) present Citrus sinensis and Musa acuminata mediated synthesized TiO 2 , TiO 2 -rGO, and GO. e resulting diffraction pattern of GO showed a broad and relatively strong characteristic peak at 2θ ≈ 10.1°, corresponding to the (001) plane, and this indicates the formation of GO sheets. e calculated average crystalline size of GO was found to be 9.8 nm. e spacing between GO sheets was attributed to the presence of oxygen functional groups such as hydroxyl, carboxyl, and epoxide groups on the carbon backbones as supported by the previously reported work [29]. In both of the peel waste extract mediated synthesized GO sheets, an incomplete oxidation of graphite powder was exhibiting a strong and sharp diffraction peak at 26.1°, which in turn is corresponding to the (002) plane [30]. Figures 5(a) and 5(b) clearly depict that the obtained rGO shows a wrinkled and crumpled morphology which is stacked together and forms a typical multilayer structure.

SEM Analysis.
is multilayer structure of rGO is important in providing additional rough surface for the deposition of Citrus sinensis and Musa acuminate template synthesized TiO 2 NPs into rGO [31].    NPs, respectively, and the images were found to possess spherical shaped surface morphology in the presence of distinct edges having wide rough surface. In both of the peel waste extract mediated synthesized TiO 2 NPs using different volume ratios, the particle size was found to be increased with an increase in the amount of the peel waste extracts, which is in agreement with the calculated average crystalline size from the XRD analysis. Furthermore, homogenized and small particle size TiO 2 NPs was obtained while using peel extract of Citrus sinensis due to its richness in biomolecules [32][33][34]. e uniform distribution of TiO 2 NPs is due to very small amount of rGO with respect to TiO 2 NPs and intercalation of rGO inside the TiO 2 NPs matrix [33]. However, as the content of rGO is increased from 30 to 90 mg, the size becomes clearly visible and this provides more surfaces for the deposition of green synthesized TiO 2 NPs, which in turn is necessary for the photocatalytic degradation of MB dye. e differences in the photocatalytic performance of those various compositions of TiO 2 /rGO NCs obtained in the presence of peel waste extracts of Citrus sinensis and Musa acuminata could be attributed to the amount of rGO to TiO 2 composition ratio, in addition to the differences in the morphological structure [34]. e TEM images of these peels waste extracted mediated synthesized TiO 2 NPs using various volume ratios reveal that the nanoparticles were found to have good crystalline nature without aggregations and agglomerations.

TEM-HRTEM and SAED Pattern Analysis.
is is in agreement with the XRD results and in turn confirms the formation of pure TiO 2 NPs [35,36]. e absence of aggregations and agglomerations was achieved due to the presence of bioactive capping and reducing agents from the peel waste extract of Citrus sinensis and Musa acuminata. Furthermore, it can be observed from Figures 5(c) and 5(d) that rGO is found to be covered with the green synthesized spherical anatase TiO 2 nanoparticles. e presented figures also showed crumpled, hexagonal, and rhombic-like large surface morphological structure due to the presence of the high surface area of the rGO sheets. It is also observed that the surface of rGO sheets was found to be packed densely with the green obtained TiO 2 NPs which showed good combination of rGO sheets and TiO 2 NPs and efficient TiO 2 NPs loading on the surface sheet of rGO [37,38]. e corresponding HRTEM images in Figures 5(e)-5(h) clearly showed that the lattice fringes of the rGO were parallel to the edges of the anatase TiO 2 nanoparticles. e lattice fringes also clearly indicate that the particles are nanocrystalline with an anatase phase form as it is also confirmed from the XRD data. e figures indicated that the reduced graphene particles were well doped in the presence of the peel waste extracts with a dense layer of TiO 2 nanocomposites having d-spacing value of 0.3, 0.33, 0.35, and 0.31 nm for the TiO 2 /Musa acuminata (e), TiO 2 /Citrus sinensis (f ), TiO 2 /rGO/Musa acuminata NCs (g), and TiO 2 /rGO/Citrus sinensis NCs, respectively, corresponding to the d 101 of TiO 2 anatase structured NPs. e slight variation in the d-spacing value of TiO 2 NPs and TiO 2 /rGO NCs may result from the presence of various bioactive molecules of the Musa acuminata and Citrus sinensis [39].

UV-DRS Analysis. Figures 7(a)-7(f ) show the UV-DRS
absorption spectra of TiO 2 NPs prepared using different volume ratios of titanium precursor salt and peel waste extract of Citrus sinensis (a-c) and Musa acuminata (d-f ). e optical band gap energy for each of the volume ratios of TiO 2 NPs was calculated using Tauc plot method. e band gap energy (E g ) was found to be 3.17, 3.28, 3.29, 3.10, 3.33, and 3.38 eV for the TiO 2 -0.5c, TiO 2 -1c, TiO 2 -2c, TiO 2 -0.5 m, TiO 2 -1 m, and TiO 2 -2 m, respectively. is is again found to be in close agreement with the work reported by Bekele [25].
As presented in Figure 7, it was found that increasing rGO concentrations in the composite tends to decrease energy band gap in each of the peel waste extract mediated synthesized TiO 2 /rGOs. In addition to this, it is noted that the presence of rGO influences light absorption properties of the composite significantly showing increase in light absorption intensity in the UV region and a red shift in the absorption edge around 400 nm as supported by the previous report [42]. Furthermore, the TiO 2 /rGO nanocomposites show a red shift in the absorption edge compared to single TiO 2 NPs. Similar phenomenon related to the present study was also reported by Zhang et al. [43]. Figure 8 e bands centered at 2920.53 and 2920.50 cm -1 represent H-C-H, C-H bond stretching of alkanes and -C-H groups associated with H-bond [44]. e week band observed at 1639.52 and 1641.73 cm −1 is attributed to the amide group vibration, which could be a characteristic peak of both proteins and enzymes present in both of the peel extracts [45].  Bioinorganic Chemistry and Applications prepared sample. e band corresponding to 1056 cm −1 and 1248 cm −1 are credited to C-O (carboxylates) and C-O-C (epoxide) stretching modes, respectively. e sp 2 hybridized carbon (C � C) skeleton vibration peak could be seen in GO around 1633 cm −1 . Compared to GO, rGO shows significant reduction in absorption intensities due to the presence of oxygen containing functional groups like carboxylates, epoxide, and carbonyl compounds, indicating the green reduction of GO to rGO by both Citrus sinensis and Musa acuminata peel waste extracts. As can be presented in Figures 8(a) and 8(b), the peaks centered at 2854.33 and 2921 76 cm −1 in the spectrum of rGO are due to the stretching vibration of H-C-H and -C-H groups of alkanes associated with H-bond as well [44].

FT-IR Analysis. As depicted in
FT-IR spectra of TiO 2 showed the broad band around and below 1000 cm −1 , which indicates replicate Ti-O-Ti linkage within the TiO 2 nanopours. Furthermore, the spectra of TiO 2 /rGO exhibited low intensity band frequency compared to the Citrus sinensis and Musa acuminata stabilized GO and rGO, which is formed by the amalgamation of (Ti-O-Ti) and (Ti-O-C) linkages, owing to the chemical interaction of TiO 2 with rGO sheets. is analysis confirms the green reduction of GO and coupling with TiO 2 NPs on the green obtained rGO sheets. In addition to this, the Citrus sinensis and Musa acuminata template obtained TiO 2 NPs could be susceptible to the interactions with the functional groups of rGO in the formation of TiO 2/ rGO nanocomposites [47].   Figures 9(a) and (e) show the changes in the MB absorption spectra during photocatalytic degradation with TiO 2 -2c (a) and TiO 2 -2 m (e) nanophotocatalyst at different solar irradiation times varying from 0 to 60 min. As it can be observed from the figures, the degradation of MB using TiO 2 only nanophotocatalyst is very low indicating low photocatalytic activity of TiO 2 only NPs [48]. From the results presented, only 62% and 58.5% of the dye were degraded in the presence of TiO 2 -2c and TiO 2 -2 m nanophotocatalysts, respectively. e low photocatalyst degradation efficiency of TiO 2 only NPs could be attributed to the high electron-hole recombination rate [49]. Figure 9 also depicts photocatalyst degradation of MB of Citrus sinensis peel extract mediated synthesized TiO 2 /rGO (b-d) and Musa acuminata mediated synthesized TiO 2 /rGO (f-h) nanophotocatalysts using different volume ratios. Among the various TiO 2 /rGO nanocomposite photocatalysts, TiO 2 /rGO-1.5c and TiO 2 /rGO-1.5 m showed the highest degradation efficiency of 94.28% and 94.25%, respectively, after 60 min irradiation. e results showed that the visible light photocatalytic degradation of MB is dependent on the concentration of rGO composited with TiO 2 nanophotocatalyst. As supported by the previous report [50], high surface area of the nanocomposite photocatalysts promotes increased dye adsorption on its surface. Furthermore, the improvement in photocatalytic performance of TiO 2 /rGO nanophotocatalysts might also be due to the decrease in the electron-hole recombination rate since rGO in TiO 2 /rGO nanocomposites can act as an electron acceptor.

Visible Light Photocatalytic Degradation Study of MB.
Reaction kinetics study models for the photocatalytic degradation of MB dye using both TiO 2 nanocatalysts and TiO 2 /rGO composite nanocatalysts were tested by using first and second order pseudokinetic models. As it can be observed from Figure 10(a), the photocatalytic degradation of MB fit pseudo-first order model with the correlation constant of R 2 � 0.95 min −1 for the TiO 2 -2c and R 2 � 0.953 for the TiO 2 -m nanophotocatalysts. Table 1 represents the corresponding calculated parameters for first order and second order kinetic data model of MB dye degraded by green formed TiO 2 nanocatalyst and TiO 2 /rGO nanocomposites under visible light irradiation.
Furthermore, the photocatalytic degradation of MB in the presence of green template TiO 2 /rGO green nanocatalysts was found to be fit with pseudo-second order kinetics with rate constant of 0.974 min −1 for TiO 2 /rGO-1.5 m [51].
Figures 11(a)-11(c) showed the influence of pH of the solution on the degradation efficiency of methylene blue using TiO 2 /rGO nanophotocatalysts at pH 1, 7, and 13 (strong acid, neutral, and strong base media), respectively. e change in the pH of the solution influences the surface of the nanocomposite catalyst, thereby causing a change in adsorption and the reaction rate [52]. e point of zero charges of the TiO 2 /rGO-1.5c was estimated to be at pH 7 and as a result the photocatalyst surface could possess negative charge at pH > 7 and positive charge at pH < 7. It was observed that when the pH of solution changed from pH 1 to pH 7, the degradation efficiency of the NC increased from 18.1 to 90.7, respectively. e low degradation efficiency of MB in the presence of TiO 2 /rGO nanophotocatalysts at pH 1 could be due to the electrostatic repulsion between the positively charged green nanophotocatalysts surface and the cationic methylene blue, while no such repulsion occurs at pH 7 [10]. e photocatalytic degradation of MB dye in the presence of green template synthesized TiO 2 /rGO  Wavelength (nm) stock nanophotocatalysts was found to be dependent on the pH value. is pH dependence of photocatalyst activity of the NC might be due to its effect on the NC's surface charge, size, and valance and conductance bond positions [53]. As could be depicted in Figure 11(c), the highest degradation of MB dye was obtained at pH 13 with degradation efficiency of 99.4%. is indicates that alkaline pH favored the adsorption of the dye due to the electrostatic attraction between the negatively charged catalyst surface and cationic methylene blue dye. Furthermore, the neutral pH is known as the zero point of charge where the surface of CS mediated synthesized TiO 2 /rGO NCs has no dye concentration [53]. Figure 12 shows the effect of initial MB dye concentration in the presence of Citrus sinensis fruit peel extract template synthesized TiO 2 /rGO-1.5c NCs photocatalyst. e effect of initial MB dye concentrations on the photocatalytic efficiency of the TiO 2 /rGO-1.5c was investigated by varying the concentration of MB dye (10, 20, and 30 ppm) while fixing the amount of the photocatalyst NC (30 mg/L) at pH of 7. It has been found that a significant decrease in the percentage of degradation was observed with an increase in the initial dye concentration of MB dye [54]. is might be caused by the saturation of the surface of the green TiO 2 / rGO nanocomposite catalysts. In addition, the decrease in photodegradation with increase in initial concentration of MB might also be caused by the interference for visible light to penetrate and reach the catalyst surface, thereby lowering the production of OH − radicals [55,56]. Furthermore, the reaction rates were found to be decreased with an increase in concentration of MB with rate constants of 0.04 min −1 for 10 mg/L, 0.03 min −1 for 20 mg/L, and 0.02 min −1 for 30 mg/L (Figure 12(d)).
In order to gain further information on the degradation removal of MB dye, the dosage of green template TiO 2 /rGO-1.5c nanocomposite photocatalyst was also altered in the range of 20 mg/L, 30, and 50 mg/L while keeping the pH and the dye concentration being 7 and 10 mg/L, respectively. As it is depicted from Figures 13(a)-13(c), maximum degradation efficiency of 90.92% and 90.70% was obtained with 50 and 30 mg TiO 2 /rGO-1.5c dosage, respectively, due to increase in the total number of active sites as the dosage of the photocatalyst is increased [57]. e effect of visible light illumination contact time from 0 to 60 min interval was carried out using 20 mg/L aqueous solution of MB dye at pH 7 in the presence of 30 mg TiO 2 /rGO-1.5c. Figure 14 depicts the effect of contact time on the degradation of MB dye using the optimized pH. e reaction was started in dark condition for 10 minutes to attain sorption-desorption equilibrium between the catalytic surface and the dye. e result showed a noticeable gradual increase of photocatalytic rate with increasing illumination time. After 60 min, the rate reached its optimum removal efficiency, 94.4%, and a linear relationship between degradation of MB dye and increase in contact time was observed.
is is because prolonging irradiation time allows light to fall on the catalyst surfaces and induce formation of photon excited species and enhances the photocatalytic activities [58].

Conclusions
In the present findings, TiO 2 NPs and TiO 2 /rGO NCs were effectively synthesized in the presence of peel waste extract of Musa acuminata and Citrus sinensis as both a green reducing and stabilizing agent. e synthesized NPs and NCs were characterized using TGA/DTA, XRD, SEM, TEM, HRTEM, SAED, UV-DRS, and FTIR analysis. e thermal stability study proved that the synthesized NPs were found to be stable above 550°C. e XRD analysis shows that the average crystalline size of TiO 2 NPs was calculated as 27.3, 12.1, and 7.3 nm for the TiO 2 -0.5c, TiO 2 -1c, and TiO 2 -2c and 22.4, 16.3, and 13.4 nm for the volume ratios of TiO 2 -0.5 m, TiO 2 -1 m, and TiO 2 -2 m, respectively. e average crystalline size for the various TiO 2 /rGO NCs was found to be 8.4, 15.3, and 7.5 nm and 12.5, 11.4, and 11.2 nm for the TiO 2 /rGO-0.5c, TiO 2 /rGO-1c, TiO 2 /rGO-1.5c, and TiO 2 /rGO-0.5 m, TiO 2 /rGO-1 m, and TiO 2 /rGO-1.5m, respectively. e UV-DRS analysis showed that the energy band gaps were found in the range of 3.17-3.29 and 3.10-3.38 eV for the Citrus sinensis and Musa acuminata peel waste extract mediated synthesized TiO 2 NPs, respectively. e energy band gaps of the various TiO 2 /rGO NCs were found in the range of 2.85-3.11 eV and 3.07-3.11 eV for the Citrus sinensis and Musa acuminata peel waste extract template synthesized TiO 2 /rGO NCs, respectively. Furthermore, FTIR analysis proved the presence of various bioactive molecules in the peel waste extract of the Citrus sinensis and Musa acuminata such as phenols, flavonoids, carboxylic acids, alcohols, and saturated and unsaturated hydrocarbons. Citrus sinensis template obtained TiO 2 nanocatalyst showed degradation efficiency of 62%, while Musa acuminate obtained TiO 2 nanocatalyst shows a degradation efficiency of 58.2%. Of the various Citrus sinensis and Musa acuminata peel waste extract based synthesized TiO 2 /rGO nanocomposites, TiO 2 /rGO-1.5c and TiO 2 /rGO-1.5 m showed degradation efficiency of 94.28% and 94.25%, respectively, making the NCs material of interest for environmental remediation applications.

Data Availability
e necessary data such as TGA/DTA, XRD, UV-DRS, UVvisible absorption spectra, FTIR spectra, SEM, TEM images, HRTEM images, SAED patters, and the photocatalytic degradation study used to support the findings of this study are included in the article.
Disclosure e funder of this study has not been involved in the editing, approval, or decision in publishing this manuscript.

Conflicts of Interest
All the authors fully declare that they have no conflicts of interest.
Acknowledgments e present work was fully supported by the Adama Science and Technology University (ASTU) under 14 th ASTU's research cycle, and the authors gratefully appreciate the financial support of ASTU.