Fabrication of 3D Gelatin Hydrogel Nanocomposite Impregnated Co-Doped SnO2 Nanomaterial for the Catalytic Reduction of Environmental Pollutants

In the catalytic reduction of various environment pollutants, cobalt-doped tin oxide, i.e., Co-SnO2 intercalated gelatin (GL) hydrogel nanocomposite was prepared via direct mixing of Co-SnO2 doped with GL. Then, it was crosslinked internally using formaldehyde within a viscous solution of gelatin polymer, which led to the formation of GL/Co-SnO2 hydrogel nanocomposite. GL/Co-SnO2 hydrogel nanocomposite was fully characterized by using field-emission scanning electron microscopy (FESEM), energy dispersive X-ray spectroscopy (EDX), powder X-ray diffraction (XRD), and attenuated total reflection–Fourier transform infrared spectroscopy (ATR-FTIR). The FESEM images indicate that the Co-SnO2 composite has a spherical structure on the GL matrix while EDX elucidates the elemental composition of each atom in the crosslinked GL/Co-SnO2 hydrogel nanocomposite. The GL/Co-SnO2 nanocomposite was checked for the reduction of various pollutants, including 2-nitro-phenol (2-NP), 2,6-dinitro-phenol (2,6-DNP), 4-nitro-phenol (4-NP), Congo red (CR), and methyl orange (MO) dyes with a strong sodium borohydride (NaBH4) reducing agent. The GL/Co-SnO2 nanocomposite synergistically reduced the MO in the presence of the reducing agent with greater reduction rate of 1.036 min−1 compared to other dyes. The reduction condition was optimized by changing various parameters, such as the catalyst amount, dye concentration, and the NaBH4 amount. Moreover, the GL/Co-SnO2 nanocomposite catalyst can be easily recovered, is recyclable, and revealed minimal loss of nanomaterials.


Introduction
Generally, polymers have been part of the lives of human beings from the beginning, because of their wide application in daily uses and unique properties. Due to their largescale contribution in engineering resins, polyolefins, epoxies from tar to shellac, as well as tortoise, they provide basic and high-priority construction materials, transportation, commerce, and digestive products. Globally, polymers produce a large amount of money in the range of GBP 250-400 billion. Therefore, biopolymers, such as cellulose, chitins, lipids, proteins, and gelatin are an extensive part of the organic nature of sediments [1]. Biopolymer films are environmentally friendly and can be used in catalysis and food packaging [2][3][4][5][6][7][8]. Considering biopolymers, it reveals the feeble mechanical strength that limits their application in the catalyst field [9]. Gelatin is a biopolymer obtained from natural polymer collagen using hydrolysis. It is a flavorless, translucent, light yellowish, brittle, solid substance, derived under both acidic and basic conditions. Due to its universal properties, such as biocompatibility, cell-adhesion ability, modification, biodegradability, Figure 1 reveals the FESEM images of Co-SnO 2 nanomaterials and GL/Co-SnO 2 hydrogel nanocomposite materials. The fabricated nanomaterials were analyzed before and after crosslinking with the biopolymer. The first two images (Figure 1a,b) show the pure micrograph of Co-SnO 2 nanomaterial at low and high magnifications. Both images at low and high magnifications revealed the spherical shape of the nanomaterials. Further, Gels 2022, 8,479 3 of 17 these magnified nanocomposite materials are presented in Figure 1b,b , respectively. In this case, the GL/Co-SnO 2 nanomaterials are crosslinked with formaldehyde via in situ formation, which remains firm within the hydrogel for long time and plays a vital role in the field of catalysis. This process is fit for entrapping NPs inside polymeric chains. It was observed that Co-SnO 2 nanomaterials are found in dispersed forms inside hydrogel networks. The SEM images clearly revealed that Co-SnO 2 nanomaterials are well dispersed inside the gelatin matrix. The average diameter of Co-SnO 2 is 17.5 nm in the range of 15-25 nm. Figure 1 reveals the FESEM images of Co-SnO2 nanomaterials and GL/Co-SnO2 hydrogel nanocomposite materials. The fabricated nanomaterials were analyzed before and after crosslinking with the biopolymer. The first two images (Figure 1a,b) show the pure micrograph of Co-SnO2 nanomaterial at low and high magnifications. Both images at low and high magnifications revealed the spherical shape of the nanomaterials. Further, these magnified nanocomposite materials are presented in Figure 1b,b′, respectively. In this case, the GL/Co-SnO2 nanomaterials are crosslinked with formaldehyde via in situ formation, which remains firm within the hydrogel for long time and plays a vital role in the field of catalysis. This process is fit for entrapping NPs inside polymeric chains. It was observed that Co-SnO2 nanomaterials are found in dispersed forms inside hydrogel networks. The SEM images clearly revealed that Co-SnO2 nanomaterials are well dispersed inside the gelatin matrix. The average diameter of Co-SnO2 is 17.5 nm in the range of 15-25 nm. Here, the energy dispersive X-ray spectroscopy (EDX) method was utilized to analyze the elemental composition of the synthesized nanomaterial catalyst. The stoichiometry is shown in Figure 2. Oxygen (O), cobalt (Co), and tin (Sn) are the key elements of this prepared nanomaterial, while carbon contents appeared in the nanocomposite due to the involvement of the polymer. The EDX spectrum is displayed as 23.41%, 25.95%, and 55.00% by weight of Co, O, and Sn, respectively. This amount is decreased in GL/Co-SnO2 nanocomposite material. The amount is reduced to 9.83% and 35.96% for Co and Sn, respectively. Before analysis, the sample was coated with GL, that is why the carbon peaks Here, the energy dispersive X-ray spectroscopy (EDX) method was utilized to analyze the elemental composition of the synthesized nanomaterial catalyst. The stoichiometry is shown in Figure 2. Oxygen (O), cobalt (Co), and tin (Sn) are the key elements of this prepared nanomaterial, while carbon contents appeared in the nanocomposite due to the involvement of the polymer. The EDX spectrum is displayed as 23.41%, 25.95%, and 55.00% by weight of Co, O, and Sn, respectively. This amount is decreased in GL/Co-SnO 2 nanocomposite material. The amount is reduced to 9.83% and 35.96% for Co and Sn, respectively. Before analysis, the sample was coated with GL, that is why the carbon peaks appeared as shown in the EDX spectra of the GL/Co-SnO 2 catalyst. Therefore, Figure 2b reveals the homogenous mixing of the Co-SnO 2 nanomaterial in the 3D-hydrogel network. appeared as shown in the EDX spectra of the GL/Co-SnO2 catalyst. Therefore, Figure 2b reveals the homogenous mixing of the Co-SnO2 nanomaterial in the 3D-hydrogel network.
The crystallinity of GL/Co-doped SnO2 nanomaterial was calculated using Debye-Scherrer's equation as follows.

XRD
X-ray diffraction (XRD) was investigated to reveal the crystallinity of Co-doped SnO 2 and crosslinked Co-doped SnO 2 with GL. The XRD peaks for both Co-doped SnO 2 and GL/Co-doped SnO 2 hydrogel nanocomposite were obtained in the 2-theta range of 10-80 • as shown in  [43]. One additional peak appeared at 2 theta 37.58 • which can be indexed to 200. This peak might be due to the Co-doped SnO 2 composite structure. The cobalt (Co)-doped oxide revealed a peak at 2 theta at 18.63 • , 30.27 • , 32.10 • , 45.75 • , and 57.68 • , which could be indexed to (111), (220), (311), (400), and (511), respectively. Additionally, the high intensity peak that appeared at 32.10 • could be indexed to (101) which could be corresponding to SnO 2 , which is in good agreement with the given literature [44][45][46][47]. These peaks are in good agreement with the JCPDS card no: 073-1701 file, which indicates the cubic structure of Co(NO 3 ) 2 ·6H 2 O [48]. The dry hydrogel nanocomposite material (GL/Co-doped SnO 2 ) verifies two crystalline peaks at 34.17 • and 52.07 • , corresponding to (101) and (211), respectively. A broader peak was observed at 25.20 • , which showed the amorphous form of the polymer. The fabricated nanocomposite shows no peaks in the catalyst that may be owing to the small quantity of cobalt oxide compared to the tin dioxide. (1) In the above equation, D is the average diameter of the crystallites (nm), λ is the wavelength of CuKα1 radiation (1.542 Å), β is the full width at half maximum in radians (FWHM), and q is the Bragg angle in the plane of the diffraction peak. The average crystalline diameter of the Co-doped SnO2 nanomaterial was calculated as 10.19 nm.

ATR-IR
The composition of prepared NPs and fabricated nanocomposite catalyst was analyzed using ATR-IR spectroscopy, as shown in Figure 4. The ATR-IR spectrum of Co-SnO2 nanomaterial shows their characteristic peaks at 1639 and 3371 cm −1 which are attributed to OH bending, and OH stretching, respectively. The peak that appeared at a lower wavenumber corresponds to the stretching of the M-O (metal-oxygen stretching), which is in accordance with the given literature [49]. Further, the GL/Co-SnO2 hydrogel nanocomposite provides stretching of the N-H functional group present in gelatin at 3270 cm −1 . The peak that appeared in the nanocomposite at 1639 and 1539 cm −1 presents amide I and asymmetric stretching vibration of the carboxyl group, respectively. Moreover, peaks located at 1452, 1404, and 1331 cm −1 are attributed to C-H aliphatic vibration of the carboxyl group, C-H bending vibration, and stretching vibration of the C-N bond. In Figure 4b, the region from 475 to 510 cm −1 is related to metal oxide, and hence confirms the presence of the prepared nanomaterial, i.e., gelatin-matrix/Co-SnO2 nanomaterials. The crystallinity of GL/Co-doped SnO 2 nanomaterial was calculated using Debye-Scherrer's equation as follows.
In the above equation, D is the average diameter of the crystallites (nm), λ is the wavelength of CuKα1 radiation (1.542 Å), β is the full width at half maximum in radians (FWHM), and q is the Bragg angle in the plane of the diffraction peak. The average crystalline diameter of the Co-doped SnO 2 nanomaterial was calculated as 10.19 nm.

ATR-IR
The composition of prepared NPs and fabricated nanocomposite catalyst was analyzed using ATR-IR spectroscopy, as shown in Figure 4. The ATR-IR spectrum of Co-SnO 2 nanomaterial shows their characteristic peaks at 1639 and 3371 cm −1 which are attributed to OH bending, and OH stretching, respectively. The peak that appeared at a lower wavenumber corresponds to the stretching of the M-O (metal-oxygen stretching), which is in accordance with the given literature [49]. Further, the GL/Co-SnO 2 hydrogel nanocomposite provides stretching of the N-H functional group present in gelatin at 3270 cm −1 . The peak that appeared in the nanocomposite at 1639 and 1539 cm −1 presents amide I and asymmetric stretching vibration of the carboxyl group, respectively. Moreover, peaks located at 1452, 1404, and 1331 cm −1 are attributed to C-H aliphatic vibration of the carboxyl group, C-H bending vibration, and stretching vibration of the C-N bond. In Figure 4b, the region from 475 to 510 cm −1 is related to metal oxide, and hence confirms the presence of the prepared nanomaterial, i.e., gelatin-matrix/Co-SnO 2 nanomaterials.

Catalytic Reduction
The reduction of dyes was recorded using time-dependent absorbance with a UVvisible spectrometer from the 200-700 nm absorbance range, at room temperature. The reduction time for all the dyes was evaluated for 30 min. Moreover, the dye that took less time was used for further analysis. To study the effect of changing different parameters, such as different dosage of the catalyst, different concentrations of the dye and amounts of NaBH4 were checked further against the dye. Additionally, at the end the major property of the catalyst, i.e., recyclability, was checked three times.

Catalytic Reduction of GL/Co-SnO2 Nanocomposite Material
Hydrogel is a hydrophilic polymer, which is crosslinked by chemical or physical interactions containing a large amount of water [50][51][52][53][54][55][56]. It swells in the aqueous solution by absorbing water in its three-dimensional network. Therefore, the dye molecules can easily filter through it. Herein, the prepared GL/Co-SnO2 was used against nanomaterial and chemical/azo dyes. The nitro groups containing compounds are widely implemented in pharmacology goods, dyes, and pigment industries, and aromatic products for colored dye [57]. For example, analgesic as well as antipyretic medicines (Acetanilide, Paracetamol, and Phenacetin) are synthesized in industries from 4-amino-phenol that can be acquired through catalytic-reduction of 4-NP [58,59]. Additionally, the products obtained from 2-NP and 2,6-DNP are mostly used as herbicides and dye pigments, respectively. Besides their importance, they also pollute the ecosystem due to their toxic nature, being released from various industries. Thus, their catalytic reduction is important to reduce their toxicity and convert them into safer products. Therefore, catalytic reduction is a significant process for the reduction of these pollutants. With the catalytic reduction, 4-NP, 2-NP, and 2,6-DNP were transferred into their corresponding amines and the reduction process was monitored with UV-vis. spectroscopy by using the uninterrupted decline in

Catalytic Reduction
The reduction of dyes was recorded using time-dependent absorbance with a UVvisible spectrometer from the 200-700 nm absorbance range, at room temperature. The reduction time for all the dyes was evaluated for 30 min. Moreover, the dye that took less time was used for further analysis. To study the effect of changing different parameters, such as different dosage of the catalyst, different concentrations of the dye and amounts of NaBH 4 were checked further against the dye. Additionally, at the end the major property of the catalyst, i.e., recyclability, was checked three times.

Catalytic Reduction of GL/Co-SnO 2 Nanocomposite Material
Hydrogel is a hydrophilic polymer, which is crosslinked by chemical or physical interactions containing a large amount of water [50][51][52][53][54][55][56]. It swells in the aqueous solution by absorbing water in its three-dimensional network. Therefore, the dye molecules can easily filter through it. Herein, the prepared GL/Co-SnO 2 was used against nanomaterial and chemical/azo dyes. The nitro groups containing compounds are widely implemented in pharmacology goods, dyes, and pigment industries, and aromatic products for colored dye [57]. For example, analgesic as well as antipyretic medicines (Acetanilide, Paracetamol, and Phenacetin) are synthesized in industries from 4-amino-phenol that can be acquired through catalytic-reduction of 4-NP [58,59]. Additionally, the products obtained from 2-NP and 2,6-DNP are mostly used as herbicides and dye pigments, respectively. Besides their importance, they also pollute the ecosystem due to their toxic nature, being released from various industries. Thus, their catalytic reduction is important to reduce their toxicity and convert them into safer products. Therefore, catalytic reduction is a significant process for the reduction of these pollutants. With the catalytic reduction, 4-NP, 2-NP, and 2,6-DNP were transferred into their corresponding amines and the reduction process was monitored with UV-vis. spectroscopy by using the uninterrupted decline in spectra. Thermodynami- cally, these proposed reactions are reasonable in the aqueous phase of the reducing agent (NaBH 4 ). Significant changes between dye compounds and a good reducing agent (NaBH 4 ) generates a large kinetic barrier, which reduces the reduction at very slow rate even with a large quantity of reducing agent (NaBH 4 ) [60][61][62][63][64][65]. By introducing an efficient catalyst, it exceeds this energy barrier and allows the catalytic reaction to occur.
Herein, the 2-NP, 2,6-DNP, and 4-NP were investigated with a strong reducing agent, i.e., NaBH 4 , which did not show considerable reduction even after a long time. While, the experiment was repeated by introducing the fabricated catalyst, i.e., Co-doped SnO 2 , and reduced all dyes within 30 min. For the catalytic reduction of nitro aromatic compounds, such as 2-NP, 2,6-DNP, and 4-NP, 25.0 mL of each pollutant was used with a strong reducing agent (NaBH 4 ) and 0.2 gm hydrogel nanocomposite. The catalyst facilitates hastening of electron transfer from donor BH 4 − to the acceptor, nitro-compounds, and the reduction of the reaction proceeds [66]. The catalytic reduction was carried out by tracking the decrease in the absorbance peak in different time intervals, which is presented in Figure 5a-c. The catalytic reduction was carried out in the excess of NaBH 4 . The reaction was supposed to follow the first-order reaction condition. Therefore, to calculate the apparent rate constant (K app ) of nitro aromatic compounds, pseudo-first-order kinetics were used. The slope of the straight line provides the magnitude for apparent rate constant plotted between ln(C t /C 0 ) against time. The reduction process was investigated using the following pseudo-firstorder equation. ln where C 0 and C t are the initial concentration and final concentration of the dye at any given interval of time. A 0 is the absorbance of the dye at the start and A t is the absorbance value taken after introducing NaBH 4 and catalyst to the reaction media. K app represents the apparent rate constant, while 't' represents the rate of the reaction.

Catalytic Reduction of Azo Dyes
The photocatalytic reduction of azo dyes (CR and MO) was studied with an excess amount of NaBH4 (model reaction), which are presented in Figure 6a-d. The NaBH4 acts as an electron source for the reduction of dye molecules. Generally, the borohydride ion and dye molecule adsorb simultaneously on the surface of NPs, where the transfer of electrons takes place from BH4 -to the surface of the GL/Co-SnO2 nanomaterial, which trans-  The % reduction of the dyes was expressed using Equation (2).
where A 0 and A t correspond to the initial absorbance of the dye '0 min' and absorbance at time 't', respectively. The reduction reactions were performed in a beaker by introducing 25.0 mL of each nitrophenol (2-NP, 2,6-DNP, and 4-NP), 0.4 gm of NaBH 4 . A fixed concentration of 0.07 mM of the dye was used for each run. The catalytic reduction was initiated by introducing 0.2 gm of Co-SnO 2 photocatalyst. The UV-vis spectrum of the 2-NP, 2,6-DNP, and 4-NP exhibits absorption peaks at 412, 426, and 397 nm, respectively. The nitrophenols were reduced in 8, 14, and 30 min, respectively. Additionally, the catalytic reduction rate of the reaction was reported as 3.31 × 10 −1 , 2.01 × 10 −1 , and 8.9 × 10 −2 min −1 , respectively. Among which, the reduction rate for 4-NP was very slow. The catalytic reduction rate, K app , of nitrophenols between ln(C t /C 0 ) verses time are shown in Figure 5d.

Catalytic Reduction of Azo Dyes
The photocatalytic reduction of azo dyes (CR and MO) was studied with an excess amount of NaBH 4 (model reaction), which are presented in Figure 6a-d. The NaBH 4 acts as an electron source for the reduction of dye molecules. Generally, the borohydride ion and dye molecule adsorb simultaneously on the surface of NPs, where the transfer of electrons takes place from BH 4 − to the surface of the GL/Co-SnO 2 nanomaterial, which transfers it to dye molecules and reduces it. Here, we fabricated GL/Co-SnO 2 and used it for reduction of CR and MO with (λ max ) at 475 and 461 nm, respectively. The same condition was used for the reduction of the dyes, as discussed above. With the addition of NaBH 4 it did not cause fading, while slightly decreased the intensity of its color. The introduction of hydrogel nanocomposite to the aqueous media containing dye and NaBH 4 starts the reduction of the dye molecules. The catalyst acts as an electron relay system, it takes the electron from the donor BH 4 − and conveys it to the dyes [67]. The UV spectrum illustrates the two broad peaks of CR and MO, owing to the presence of the -N=N-double bond. The CR and MO were reduced in 5 and 3 min, respectively. The photocatalytic reduction rate constants of these dyes were reported (Figure 6c,d) as 6.61 × 10 −1 and 1.036 min −1 , respectively. The MO reduction rate was higher than CR. As MO is one of the persistent and toxic dyes its catalytic reduction was studied further in detail.
The effect of catalyst dosage was also investigated against MO, keeping other parameters constant. Three different hydrogel nanocomposites (Co-SnO 2 ), i.e., 0.1, 0.2, and 0.4 gm were analyzed against 0.07 mM of MO with 0.4 g of NaBH 4 . The reduction rate was calculated as 0.713, 1.036, and 2.287 min −1 , respectively. Compared to the amount of the catalyst, it showed a direct effect on the catalytic reduction of the dye (Figure 7a). For example, MO was reduced in 04, 03, and 02 min, respectively. The K app value for the catalytic reduction of MO with the hydrogel nanocomposite was calculated from the slope of the linear line plotted between ln(C t /C 0 ) verses time, as shown in Figure 7b.
The optimization of the effect of different amounts of catalytic reducing agents (NaBH 4 ) on the catalytic reduction rate of the MO was examined. By increasing the amount of NaBH 4 the reduction rate, K app , increased, as can be seen from the slope between ln(C t /C 0 ) verses time in Figure 7c. Three different weights of 0.2, 0.4, and 0.8 gm of NaBH 4 were added to the MO. The 25.0 mL of 0.07 mM MO was reduced in 05, 02, and 01 min, respectively. The rate of the reduction was recorded as 0.722, 1.036, and 3.033 min −1 , respectively. The increase in the amount of NaBH 4 has a positive effect on the efficient reduction rate of the fabricated catalyst. This is due to the availability of more BH 4 − ions. The reason is that these electron-rich species accelerate quickly in the reaction phase and as a result promptly provide electrons towards hydrogel nanocomposites which convey them to the dye molecules. The effect of catalyst dosage was also investigated against MO, keeping other parameters constant. Three different hydrogel nanocomposites (Co-SnO2), i.e., 0.1, 0.2, and 0.4 gm were analyzed against 0.07 mM of MO with 0.4 g of NaBH4. The reduction rate was calculated as 0.713, 1.036, and 2.287 min −1 , respectively. Compared to the amount of the catalyst, it showed a direct effect on the catalytic reduction of the dye (Figure 7a). For example, MO was reduced in 04, 03, and 02 min, respectively. The Kapp value for the catalytic reduction of MO with the hydrogel nanocomposite was calculated from the slope of the linear line plotted between ln(Ct/Co) verses time, as shown in Figure 7b.
The optimization of the effect of different amounts of catalytic reducing agents (NaBH4) on the catalytic reduction rate of the MO was examined. By increasing the amount of NaBH4 the reduction rate, Kapp, increased, as can be seen from the slope between ln(Ct/Co) verses time in Figure 7c. Three different weights of 0.2, 0.4, and 0.8 gm of NaBH4 were added to the MO. The 25.0 mL of 0.07 mM MO was reduced in 05, 02, and 01 min, respectively. The rate of the reduction was recorded as 0.722, 1.036, and 3.033 min −1 , respectively. The increase in the amount of NaBH4 has a positive effect on the efficient reduction rate of the fabricated catalyst. This is due to the availability of more BH4 -ions. The reason is that these electron-rich species accelerate quickly in the reaction phase and as a To analyze the photocatalytic reduction of Co-doped SnO 2 catalyst for different concentrations of MO, three different concentrations of MO were prepared, such as 0.05, 0.07, and 0.09 mM, keeping other parameters constant. Figure 7d clearly illustrates that with the increase in concentration of the dye, it took more time to be reduced. Therefore, MO with the above concentration was reduced in 02, 03, and 04 min, respectively. Finally, it is understood from the experimental results that the catalytic reaction rate of the reaction increases by decreasing the concentration of the colored dye. Then, the reaction rate was reported as 1.656, 1.036, and 0.921 min −1 , respectively. The reduction of all dyes gives a linear straight line between ln(C t /C 0 ) verses time followed by pseudo-first-order reaction. Then, the rate constant K app of the reaction was calculated using equation 1. Thus, the catalytic efficiency of the hydrogel nanocomposite showed a direct effect with the amount of NaBH 4 , concentration of MO dye, and the amount of catalyst, as illustrated in Figure 7a-d. stood from the experimental results that the catalytic reaction rate of the reaction increases by decreasing the concentration of the colored dye. Then, the reaction rate was reported as 1.656, 1.036, and 0.921 min −1 , respectively. The reduction of all dyes gives a linear straight line between ln(Ct/Co) verses time followed by pseudo-first-order reaction. Then, the rate constant Kapp of the reaction was calculated using equation 1. Thus, the catalytic efficiency of the hydrogel nanocomposite showed a direct effect with the amount of NaBH4, concentration of MO dye, and the amount of catalyst, as illustrated in Figure 7a-d.

Recyclability
In this approach, one of the challenging properties of the catalyst is its recyclability because this property reduces the re-scale operations, costs, and economic value. In this case, after completion of the reaction, the catalyst is recovered simply by filtration. It is washed three times with distilled water before using it for the next cycle. Herein, the catalyst was

Recyclability
In this approach, one of the challenging properties of the catalyst is its recyclability because this property reduces the re-scale operations, costs, and economic value. In this case, after completion of the reaction, the catalyst is recovered simply by filtration. It is washed three times with distilled water before using it for the next cycle. Herein, the catalyst was consecutively recycled three times. Figure 8 showed that 25.0 mL of the 0.07 mM of dye was reduced in 03, 05, and 07 min, with the reduction rates of 1.036, 0.616, and 0.455 min −1 , respectively. The dye was reduced nearly up to 97.67, 96.99, and 96.88%, respectively. In each cycle, there is a small loss of effectiveness of nanocomposites. In Figure 8, (C/C 0 ) % shows the percentage of reduction in each cycle, while Kapp represents the apparent rate constant on the right-hand side of the bar graph. It is evident that the percentage of the reaction is almost the same, while the rate of the reaction changes with time.
consecutively recycled three times. Figure 8 showed that 25.0 mL of the 0.07 mM of dye was reduced in 03, 05, and 07 min, with the reduction rates of 1.036, 0.616, and 0.455 min −1 , respectively. The dye was reduced nearly up to 97.67, 96.99, and 96.88%, respectively. In each cycle, there is a small loss of effectiveness of nanocomposites. In Figure 8, (C/C0) % shows the percentage of reduction in each cycle, while Kapp represents the apparent rate constant on the right-hand side of the bar graph. It is evident that the percentage of the reaction is almost the same, while the rate of the reaction changes with time.

Mechanism of Reduction
MO is a water-soluble azo dye widely utilized in various dyes and pigment industries. Besides the importance of this dye in terms of application, it is also unsafe and carcinogenic in nature. Therefore, from the environmental and ecological points of view, MO's reduction is very important and significant. Catalytic reduction of the MO cannot be supported by the reducing agent (NaBH4) because the reaction kinetics are not viable. Therefore, in this approach, the reduction of MO molecules was carried out in the presence of the GL/Co-SnO2 nanocomposite catalyst with the reducing agent, NaBH4. Here, Figure 9 exhibits the catalytic reduction of MO molecules, that are converted into their corresponding small constituents of MO. After introducing the GL/Co-SnO2 catalyst into the reactors, the higher concentration of sodium borohydride was implemented to the aqueous solution of MO, that increased the pH of the resultant solution mixture. In this catalytic process, the reducing agent gives BH4 − which acts as an electron donor in the system. In the presence of the prepared GL/Co-SnO2 catalyst, the BH4 − and MO dye molecules are adsorbed onto the surface of the GL/Co-SnO2 catalyst. The surface of the GL/Co-SnO2 nanomaterial acts as mediator for transferring electrons from the BH4 − ion towards MO dye molecules. The GL/Co-SnO2 catalyst introduces an efficient pathway to transfer electrons to the MO dye molecules, which reduced it in a short amount of time. Finally, the MO dye molecule was converted into small constituents.

Mechanism of Reduction
MO is a water-soluble azo dye widely utilized in various dyes and pigment industries. Besides the importance of this dye in terms of application, it is also unsafe and carcinogenic in nature. Therefore, from the environmental and ecological points of view, MO's reduction is very important and significant. Catalytic reduction of the MO cannot be supported by the reducing agent (NaBH 4 ) because the reaction kinetics are not viable. Therefore, in this approach, the reduction of MO molecules was carried out in the presence of the GL/Co-SnO 2 nanocomposite catalyst with the reducing agent, NaBH 4 . Here, Figure 9 exhibits the catalytic reduction of MO molecules, that are converted into their corresponding small constituents of MO. After introducing the GL/Co-SnO 2 catalyst into the reactors, the higher concentration of sodium borohydride was implemented to the aqueous solution of MO, that increased the pH of the resultant solution mixture. In this catalytic process, the reducing agent gives BH 4 − which acts as an electron donor in the system. In the presence of the prepared GL/Co-SnO 2 catalyst, the BH 4 − and MO dye molecules are adsorbed onto the surface of the GL/Co-SnO 2 catalyst. The surface of the GL/Co-SnO 2 nanomaterial acts as mediator for transferring electrons from the BH 4 − ion towards MO dye molecules. The GL/Co-SnO 2 catalyst introduces an efficient pathway to transfer electrons to the MO dye molecules, which reduced it in a short amount of time. Finally, the MO dye molecule was converted into small constituents.

Conclusions
In this experimental procedure, we fabricated Co/Sn nanomaterial using a facile and one-step mechanism known as the co-precipitation method. The Co-SnO2 catalyst nanomaterial was simply prepared by direct mixing of SnCl2.2H2O and Co(NO3)2.6H2O at high pH > 10. The nanomaterials with an average diameter size of 10.19 nm were dispersed in the viscous solution of the GL polymer and crosslinked chemically using formaldehyde. In order to easily recover them from the reaction media and prevent them from aggregation, these nanomaterials were crosslinked with the GL polymer. Additionally, owing to the presence of a large number of functional groups on the main chain of the GL polymer, such as -OH, -COOH helps with packing nanomaterial inside the polymer chains. The prepared nanocomposite was investigated for the reduction of different chemicals and dyes (2-NP, 2,6-DNP, 4-NP, CR, and MO). The catalytic reduction rate of the reaction followed the order, MO > CR > 4-NP > 2,6-DNP > 2-NP. Among which, MO was reduced efficiently with a strong reducing agent (NaBH4) with a reduction rate of 1.036 min −1 . MO was further studied in detail changing different parameters. The catalytic efficiency of the GL/Co-SnO2 was very significant due to the production of H2 gas, which kept the surface clean for the coming dye molecules. It introduced a new route for the mineralization of unsafe chemicals and colored dyes using the reduction method with newly introduced GL/Co-SnO2 nanocomposite materials for the safety in environmental and ecological fields on a broad scale.

Conclusions
In this experimental procedure, we fabricated Co/Sn nanomaterial using a facile and one-step mechanism known as the co-precipitation method. The Co-SnO 2 catalyst nanomaterial was simply prepared by direct mixing of SnCl 2 ·2H 2 O and Co(NO 3 ) 2 ·6H 2 O at high pH > 10. The nanomaterials with an average diameter size of 10.19 nm were dispersed in the viscous solution of the GL polymer and crosslinked chemically using formaldehyde. In order to easily recover them from the reaction media and prevent them from aggregation, these nanomaterials were crosslinked with the GL polymer. Additionally, owing to the presence of a large number of functional groups on the main chain of the GL polymer, such as -OH, -COOH helps with packing nanomaterial inside the polymer chains. The prepared nanocomposite was investigated for the reduction of different chemicals and dyes (2-NP, 2,6-DNP, 4-NP, CR, and MO). The catalytic reduction rate of the reaction followed the order, MO > CR > 4-NP > 2,6-DNP > 2-NP. Among which, MO was reduced efficiently with a strong reducing agent (NaBH 4 ) with a reduction rate of 1.036 min −1 . MO was further studied in detail changing different parameters. The catalytic efficiency of the GL/Co-SnO 2 was very significant due to the production of H 2 gas, which kept the surface clean for the coming dye molecules. It introduced a new route for the mineralization of unsafe chemicals and colored dyes using the reduction method with newly introduced GL/Co-SnO 2 nanocomposite materials for the safety in environmental and ecological fields on a broad scale.

Preparation of Co-Doped SnO 2 Nanomaterial with Hydrogel Nanocomposite
In this approach, Co-doped SnO 2 nanocomposite was synthesized using the coprecipitation method, which is presented in the Figure 10. Firstly, 50.0 mL of two salt solutions of SnCl 2 ·2H 2 O of 0.1 M and Co(NO 3 ) 2 ·6H 2 O of 0.1 M were prepared in distilled water, respectively. In the second step, total volume of the solution of SnCl 2 ·2H 2 O was discharged into 50.0 mL of Co(NO 3 ) 2 ·6H 2 O solution, which made the total volume of the solution 100.0 mL, while the pH of the solution was adjusted to 10 by slowly adding 0.2 M solution of NaOH. The homogenous mixture of solution was vigorously stirred. Further, the solution was heated at 70.0 • C under constant stirring for 24 h. Then, the resultant solution was cooled at room temperature and the black precipitate (pellet) was separated at 6000 rpm. The supernatant solution remaining above the pellet was discarded and the obtained precipitate was washed three times with distilled water. The prepared sample in powder-form was dried at 60 • C and stored in a plastic vial when not in use.

Preparation of Co-Doped SnO2 Nanomaterial with Hydrogel Nanocomposite
In this approach, Co-doped SnO2 nanocomposite was synthesized using the co-precipitation method, which is presented in the Figure 10. Firstly, 50.0 mL of two salt solutions of SnCl2·2H2O of 0.1 M and Co(NO3)2·6H2O of 0.1 M were prepared in distilled water, respectively. In the second step, total volume of the solution of SnCl2·2H2O was discharged into 50.0 mL of Co(NO3)2·6H2O solution, which made the total volume of the solution 100.0 mL, while the pH of the solution was adjusted to 10 by slowly adding 0.2 M solution of NaOH. The homogenous mixture of solution was vigorously stirred. Further, the solution was heated at 70.0 °C under constant stirring for 24 h. Then, the resultant solution was cooled at room temperature and the black precipitate (pellet) was separated at 6000 rpm. The supernatant solution remaining above the pellet was discarded and the obtained precipitate was washed three times with distilled water. The prepared sample in powder-form was dried at 60 °C and stored in a plastic vial when not in use.
Further, the hydrogel was prepared by dissolving 0.24 gm of gelatin in enough water to make 30 mL of hydrogel solution. The solution was stirred for 40 min continuously. Further, 4% of 0.8 gm of the prepared nanomaterials (i.e., Co-doped SnO2) was mixed with 30 mL of gelatin aqueous solution. This mixture of hydrogel and nanomaterial was kept stirring for 25 min, to completely impregnate the Co-doped SnO2 nanomaterials in the gelatin matrix. To crosslink these nanomaterials within gelatin polymer, a crosslinker formaldehyde was added dropwise with a syringe. Within a few minutes, the solution stopped stirring and a semi-solid structure was formed. This was kept overnight at room temperature for complete hydrogel formation.

Catalytic Performance of Co-Doped SnO2 Nanocomposite
In this experimental work, a fixed amount of 0.2 gm fabricated hydrogel nanocomposite, as a catalyst (GL/Co-SnO2), was added to 25.0 mL of each dye, such as 2-NP, 2,6-DNP, 4-NP, and CR, as well as MO, while 0.4 gm of NaBH4 was added before the catalyst. The catalytic performance of Co-doped SnO2 nanocomposite was checked against different nanomaterials and azo dyes. Five different chemical and dyes, such as 4-NP, 2-NP, 2,6-DNP, CR, and MO were analyzed in the presence of fabricated catalyst, to investigate its catalytic efficiency. An aqueous solution of 0.07 mM was prepared for all these chemicals and dyes, using 0.2 gm hydro-gel nanocomposite as well as 0.4 gm NaBH4. All Further, the hydrogel was prepared by dissolving 0.24 gm of gelatin in enough water to make 30 mL of hydrogel solution. The solution was stirred for 40 min continuously. Further, 4% of 0.8 gm of the prepared nanomaterials (i.e., Co-doped SnO 2 ) was mixed with 30 mL of gelatin aqueous solution. This mixture of hydrogel and nanomaterial was kept stirring for 25 min, to completely impregnate the Co-doped SnO 2 nanomaterials in the gelatin matrix. To crosslink these nanomaterials within gelatin polymer, a crosslinker formaldehyde was added dropwise with a syringe. Within a few minutes, the solution stopped stirring and a semi-solid structure was formed. This was kept overnight at room temperature for complete hydrogel formation.

Catalytic Performance of Co-Doped SnO 2 Nanocomposite
In this experimental work, a fixed amount of 0.2 gm fabricated hydrogel nanocomposite, as a catalyst (GL/Co-SnO 2 ), was added to 25.0 mL of each dye, such as 2-NP, 2,6-DNP, 4-NP, and CR, as well as MO, while 0.4 gm of NaBH 4 was added before the catalyst. The catalytic performance of Co-doped SnO 2 nanocomposite was checked against different nanomaterials and azo dyes. Five different chemical and dyes, such as 4-NP, 2-NP, 2,6-DNP, CR, and MO were analyzed in the presence of fabricated catalyst, to investigate its catalytic efficiency. An aqueous solution of 0.07 mM was prepared for all these chemicals and dyes, using 0.2 gm hydro-gel nanocomposite as well as 0.4 gm NaBH 4 . All reactions were carried out under constant stirring. For spectral analysis of dyes, 5.0 mL of the syringe was half-filled with dye solution and poured into a quartz cell. The solution in the cuvette was poured into the beaker solution. This process was repeated until the dye reduced completely.

Characterizations
For the morphology of Co-doped SnO 2 hydrogel nanocomposite material, fieldemission scanning electron microscopy (FESEM) was performed with the JEOL instrument (JSM-7600F, Tokyo, Japan) at an accelerating voltage of 5.0 KV (magnification: ×40,000 Max). Before analysis of prepared samples, the dried sample was coated onto platinum, and a 1.5 cm-diameter cut was made with sticky black tape. The elemental composition of the prepared nanocomposite was analyzed using Oxford energy dispersive X-ray spectroscopy (EDX) equipment, which was connected directly with the FESEM instrument. Field-emission scanning electron microscopy (FESEM) is an instrumental technique utilized for the morphology of the prepared sample. A high energy beam is focused on the surface of the specimen to obtain the external morphology of the materials. Herein, the 3D hydrogel nanocomposite was dried at room temperature and investigated with FESEM. Crystallinity of the prepared sample was further investigated with powder X-ray diffraction (XRD) by using a PANalytical diffractometer with a Kα radiation (λ = 0.154 nm) source. The apparatus current of 50.0 mA and voltage of 40.0 KV were set for the investigation. The data was recorded in the range of 10-80 • at a scan rate of 2 • 2θ min −1 . Attenuated total reflection-Fourier transform infrared (ATR-FTIR) was used to characterize different functional groups in the Co-doped SnO 2 nanocomposite hydrogel. The spectra were recorded in the range of 40,000 to 500 cm −1 during 64 scans using FTIR.