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Article

Laser-Assisted Preparation of TiO2/Carbon/Ag Nanocomposite for Degradation of Organic Pollutants

by
Shahin Almasi Nezhad
1,
Babak Jaleh
2,*,
Elham Darabi
1 and
Davoud Dorranian
1
1
Plasma Physics Research Center, Science and Research Branch, Islamic Azad University, Tehran 1477893855, Iran
2
Department of Physics, Faculty of Science, Bu-Ali Sina University, Hamedan 6517838695, Iran
*
Author to whom correspondence should be addressed.
Materials 2024, 17(16), 4118; https://doi.org/10.3390/ma17164118
Submission received: 29 June 2024 / Revised: 7 August 2024 / Accepted: 8 August 2024 / Published: 20 August 2024
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Abstract

:
The ever-increasing expansion of chemical industries produces a variety of common pollutants, including colors, which become a global and environmental problem. Using a nanocatalyst is one of the effective ways to reduce these organic contaminants. With this in mind, a straightforward and effective method for the production of a novel nanocatalyst based on lignin-derived carbon, titanium dioxide nanoparticles, and Ag particles (TiO2/C/Ag) is described. The preparation of carbon and Ag particles (in sub-micro and nano size) was carried out by laser ablation in air. The nanocomposite was synthesized using a facile magnetic stirrer of TiO2, C, and Ag. According to characterization methods, a carbon nanostructure was successfully synthesized through the laser irradiation of lignin. According to scanning electron microscope images, spherical Ag particles were agglomerated over the nanocomposite. The catalytic activities of the TiO2/C/Ag nanocomposite were tested for the decolorization of methylene blue (MB) and Congo red (CR), employing NaBH4 in a water-based solution at 25 °C. After adding fresh NaBH4 to the mixture of nanocomposite and dyes, both UV absorption peaks of MB and CR completely disappeared after 10 s and 4 min, respectively. The catalytic activity of the TiO2/C/Ag nanocomposite was also examined for the reduction of 4-nitrophenol (4-NP) using a NaBH4 reducing agent, suggesting the complete reduction of 4-NP to 4-aminophenol (4-AP) after 2.30 min. This shows excellent catalytic behavior of the prepared nanocomposite in the reduction of organic pollutants.

1. Introduction

Growing population and human activity have provided important environmental issues. Water pollution, which can create fundamental problems for living organisms, has become one of the most discussed problems in the world. Consuming water sources in industrial, domestic, and agricultural sections has led to water pollution consisting of different combinations, such as dyes, heavy metals, and pesticides [1]. The released dye effluents from the textile, paper and pulp section, leather tanning, and dye production industries provide significant dangerous impacts on the environment and human well-being [2]. Dyes are colored molecules consisting of chromophores and auxochromes and have complex structures [3]. Dyes can cause respiratory and skin disorders, as well as contact dermatitis [1]. Since Congo red (CR) is commonly utilized across various sections, including textiles, paper production, and printing, it can be significantly released into aquatic systems as pollution. It is also highly toxic and carcinogenic. This anionic dye cannot easily degrade through common methods because of its benzene and naphthalene rings. It has significant optical, thermal, and physicochemical stability because of its aromatic structure. Therefore, its removal needs effective methods [4]. Methylene blue (MB) is the predominant dye found in the textile and pharmaceutical sections, recognized widely as a cationic dye. Although it does not have high toxic effects, it can provide significant issues, such as breathing difficulties, puking, runs, and qualms [1,5]. Hence, the development of environmentally friendly, easy, applicable, and high-efficiency methods for the elimination of dye residues from industrial effluents and other water sources is necessary to mitigate the adverse impacts of dyes on the environment and organisms. In brief, several chemical, physical, and biological methods have been used for dye removal from water sources, in which electrochemical treatment, adsorption, oxidation, and membrane filtration stand as the crucial techniques for achieving this objective [3,6]. Physical methods are common methods because of their simple set up and efficiency, in which the least amount of chemicals is needed compared with chemical and biological methods. In chemical methods, chemistry theories are utilized for dye removal. Biological methods are affordable and facile to operate as an alternative for dye removal, in which bacteria, fungi, yeast, and algae are used for the bacterial degradation of dyes. However, these methods are not enough to completely remove hazardous particles from dye wastewater. Therefore, colored water can still be seen. These methods are eco-friendly, produce a lower amount of sludge, and can treat the chemical oxygen demand (COD) in wastewater. The main disadvantage of biological methods is their growth rate, because they deal with living things. In comparison with physical and biological methods, chemical methods are not common in industries due to their costly setup and operation. Another disadvantage of chemical methods is the production of toxic pollutions during the dye removal process, creating additional disposal problems [2,7]. The removal percentage range was reported as 88.8–99, 76–90.1 and 86.8–99% for chemical, biological and physical methods, respectively [2]. One of the most practical methods is catalytic dye reduction through the reducing agent of NaBH4, which can effortlessly be carried out in medium conditions using suitable catalysts [8]. Nitroarene derivatives are widely employed to produce textile dyes, pharmaceutical drugs, and pesticides. Among them, 4-nitrophenol (4-NP) is a highly hazardous organic contaminant for human health and the environment. This can release into the environment as wastewater of dyeing and pharmaceutical industries. The reduction of 4-NP to a less toxic amine derivative of 4-aminophenol (4-AP) using nanocatalysts is a well-known approach for converting pollution into a high-value product [9,10].
Aiming to further reduce 4-NP and remove/degrade toxic dyes, using metal nanoparticles such as platinum, gold, palladium, silver, and copper has garnered recent attention due to their remarkable physical and chemical properties, as well as their efficacy in color removal [11,12,13,14]. Ag NPs have been shown to have high catalytic activity and optical properties. The main advantage of using Ag NPs compared with other metallic NPs is their cost-effectiveness and high stability under ambient conditions. They can also be synthesized through various chemical, physical, and biological methods. Although chemical methods can produce Ag NPs at a high yield, these methods need detrimental chemicals, while physical methods do not need to use any chemicals [15,16]. Laser ablation is a rapid, affordable, controllable, and eco-friendly physical method for preparing Ag NPs. The shape and size of the synthesized nanoparticles can be controlled by adjusting laser parameters, including wavelength, power, pulse number, and repetition rate. It can be carried out in water and air environments. Unlike the air environment, the laser ablation of the Ag target in water produces a mixture of metallic Ag NPs and Ag oxide NPs [9]. Accordingly, laser ablation in the air is employed as a physical method for preparing Ag NPs in this research. Recently, loading metallic NPs on inorganic supports such as TiO2 NPs, graphene oxide, and Fe3O4 has been developed to prepare heterogeneous catalytic systems [17,18]. Among these, TiO2 NPs, stable metal oxides with significant properties, such as nontoxicity, hydrophilicity, and low cost, are appropriate for removing hazardous compounds from water [19,20]. TiO2 consists of three crystallin phases of anatase, rutile, and brookite. Among these phases, anatase has attracted much attention due to its tendency to absorb different organic compounds [21].
Lignin constitutes a significant portion of the cell walls in natural lignocellulosic plants and is recognized as the second most abundant natural polymer on Earth, following cellulose. It has a complex structure that is relevant to its source. In addition, it can be produced through pulp and paper industries with a high yield. In the industrial process, lignin has been burnt to produce power. In addition, lignin has received widely attention for producing high-value materials due to its biocompatibility, negligible toxicity, and environmental friendliness [22,23]. Lignin consists of a high ratio of carbon to oxygen and can be employed as an ideal carbon precursor [22,24,25]. Since lignin is a soft polymer, it can be used to prepare carbon with an adjusted porous structure and morphologies. This process produces high-value products and generates income for the pulping industry and biorefineries [26,27]. According to reports, template methods have been employed to fabricate porous carbon derived from lignin [27,28]. In this research, a simple and single-step method, the laser ablation of lignin, was utilized for generating carbon in ambient conditions. It was reported that the composition of TiO2 NPs with carbon-based materials has significant applications, such as the detection of vapors [29], biomedical applications [30], photocatalyst preparation [31,32], and catalysts [33,34]. The preparation of nanocatalysts, including TiO2 NPs, Ag NPs, and carbon-based materials, has provided significant performance toward dye removal. For example, Nasrollahzadeh et al. reported that Ag/RGO/TiO2 nanocomposites show higher catalytic activity for MB (immediately), CR (116 s), and 4-NP (3.15 min) removal in aqueous media at an ambient temperature than that of GO/TiO2 [35]. In fact, the composition of TiO2 NPs with carbon materials can create support with a high surface area and high adsorption ability of dyes and other pollutants, leading to more reactant molecules near to Ag NPs.
In this work, simple and eco-friendly methods were employed to fabricate nanocomposite, including TiO2 NPs, lignin-derived carbon, and Ag particles. Laser ablation in air was used as a fast and straightforward method for preparing Ag particles and lignin-derived carbon. To prepare the nanocomposite, TiO2 NPs, Ag particles, and C were exclusively sonicated and then mixed with a magnetic stirrer to obtain a uniform suspension. The characterization of the nanocomposite represents that the amorphous carbon and metallic Ag particles can be successfully generated using a laser ablation process at ambient conditions. The nanocomposite’s catalytic activity was assessed in the removal process of MB and CR, with the presence of a NaBH4 reduction agent. The catalytic reduction of 4-NP was examined in the presence of TiO2/C/Ag catalyst.

2. Materials and Methods

2.1. Materials and Equipment

To prepare carbon, lignin was prepared from Iran. To generate Ag nanoparticles, a high-purity silver plate (99.9%) served as the target for the laser ablation process. TiO2 nanoparticles containing biphasic anatase and rutile phases in an 80 to 20 ratio were procured from Degussa Co. (Essen, North Rhine-Westphalia, Germany). A fiber laser (RFLP30Q, Raycus, Wuhan, China, 1064 nm, 100 ns, 30 W) was employed for the laser ablation process. The crystalline structure of samples was examined via X-ray diffraction (XRD, Philips, PW 1730, λ = 1.54 Å). Fourier transform infrared (FT-IR, Thermo Nicolet 370 pellet spectrometer, USA) spectra of samples were detected to evaluate the chemical bonds and functional groups. To identify detailed information about the chemical structure of samples, the Raman spectrum was measured with Raman device (Teksan, Takram P50C0R10, Tehran, Iran), with laser beam wavelength of 532 nm. X-ray photoelectron spectroscopy (XPS, SPECS, Berlin, Germany) was utilized to identify chemical bonding state and elements on the nanocomposite surface. The morphology and dispersion of the particles were examined using a field emission scanning electron microscope (FESEM, TESCAN-MIRA3-XMU, Brno, Czech Republic) and a scanning electron microscope (SEM, JEOL-JSM-840A, Tokyo, Japan). The surface area and pore diameter of the nanocomposite were analyzed using Brunauer–Emmett–Teller (BET) and Barret–Joyner–Halenda (BJH) techniques, respectively, with the BELSORP-mini II instrument (Japan). UV-Vis spectral analysis (Hitachi, Tokyo, Japan, U-2900) was used to assess the catalytic degradation of organic dyes.

2.2. Preparation of Carbon Powder

To fabricate the carbon structure, laser ablation in air was used. First, 0.1 g of lignin powder was poured into a beaker with a volume of 5 mL and covered with an appropriate glass container. Then, it was subjected to fiber laser irradiation with a scanning speed of 400 mm/s and 15 W laser output power. In order to prevent excessive temperature increase and maintain the uniformity of the laser effect on the target material, this process was stopped every 1 min, the powder was stirred with the help of a spatula, and laser irradiation was repeated, resulting in a black powder. To remove the retained lignin or impurities in the final product, the black powder was dispersed in an appropriate volume of deionized (DI) water and then centrifuged at 3000 rpm for 5 min. The colloidal carbon obtained was subsequently dried at room temperature. A schematic illustration of the carbon preparation process is depicted in Figure 1.

2.3. Preparation of TiO2/Carbon/Ag Nanocomposite

The laser ablation in the air process was used to prepare Ag particles. Firstly, the Ag plate was placed in a closed glass container. The laser beam (27 W and scanning speed of 200 mm/s) was focused on an area of 9 mm × 9 mm on the silver plate. After 30 min irradiation, the gray Ag particles powder was formed on the container wall and could be collected.
To prepare the nanocomposite, 0.02 g of Ag particles was uniformly dispersed in 10 mL of deionized (DI) water through sonication for 30 min. In addition, 0.08 g of TiO2 NPs was dispersed in 20 mL of DI water for 30 min under sonication. The dispersed Ag particles were then added to TiO2 NPs suspension. After that, 0.01 g of the prepared carbon was added to the TiO2/Ag suspension, then stirred for one day to obtain a uniform suspension, and finally dried at ambient conditions. The prepared nanocomposites were introduced as TiO2/C/Ag. Figure 2 depicts a schematic of the nanocomposite preparation process.

2.4. Investigation of the Dye Removal Efficiency of TiO2/C/Ag Nanocomposite

2.4.1. The Catalytic Reduction of Methylene Blue (MB)

The reduction of MB was conducted under ambient conditions. A total of 0.008 g of the TiO2/C/Ag nanocomposite was added to a 25 mL solution of MB (3.1 × 10−5 M). Subsequently, 25 mL of fresh NaBH4 aqueous solution (5.3 × 10−3 M) was rapidly introduced into the mixture at 25 °C. The progress of the catalytic reduction of MB was tracked using UV-Vis spectroscopy at a wavelength of 664 nm. Reduction of MB in the presence of TiO2/C and without catalyst (in the presence of NaBH4) was also performed.

2.4.2. The Catalytic Reduction of Congo Red (CR)

For the catalytic reduction of CR using the TiO2/C/Ag nanocomposite, 25 mL of NaBH4 solution (5.3 × 10−3 M) was added to an aqueous medium containing 0.008 g of TiO2/C/Ag and 25 mL of CR solution (1.44 × 10−5 M) at room temperature. The catalytic reduction of CR was assessed through UV-Vis spectroscopy, where a decrease in absorbance intensity at λmax = 498 nm indicated the reduction of CR. To investigate catalyst recyclability, the nanocomposite was washed with H2O several times and then used for another cycle. Reduction of CR was also tested without catalyst and in the presence of TiO2/C.

2.4.3. The Catalytic Reduction of 4-NP

A total of 0.008 g of the TiO2/C/Ag nanocomposite was added to aqueous solution of 4-NP (2.5 × 10−3 M, 25 mL). Then, freshly produced NaBH4 (250 mM, 25 mL) was added into the mixture. The reduction of 4-NP was observed through changing solution’s yellow color and studied using UV-Vis spectroscopy at wavelengths of 300 and 400 nm. It is worth mentioning that 4-NP reduction was also investigated without catalyst and in the presence of TiO2/C.

3. Results

3.1. Characterization

A morphological investigation of Ag particles and carbon was performed using FESEM and SEM images, as illustrated in Figure 3. The prepared Ag particles are almost spherical (Figure 3a,b). According to Figure 3b, Ag particles in nano and sub-micro size can be obtained using the laser ablation process. Figure 3c indicates the SEM image of the prepared carbon, which confirms the carbon’s porous structure.
The FESEM analysis shown in Figure 4 examines the morphology of the nanocomposite. A rough and agglomerated structure can be observed in Figure 4a. As shown in Figure 4b, the white spots indicate the precipitated Ag particles, which are spherical and agglomerated in some places. Figure 4d shows TiO2 NPs with a diameter of about 30 nm, which have been connected to each other. Based on the EDS spectrum (Figure 5a), the emission peaks of Ag, C, O, and Ti elements only indicate the presence of carbon, TiO2, and Ag in the sample. The elemental mapping analysis (Figure 5b) shows the elemental distribution, where the Ag particles are almost regularly distributed in the sample.
The crystallographic structure of lignin, carbon, and the prepared nanocomposite was evaluated through XRD patterns, as depicted in Figure 6a–c. The lignin XRD pattern shows two sharp peaks at 32.67° and 45.97° due to diffraction from (100) and (101) planes, indicating the crystal nature of lignin [36,37,38]. According to Figure 6b, the laser ablation process creates amorphous carbon, which can be confirmed with a shoulder appearing at the 2θ range of 18–29°, related to the (002) plane [39]. The XRD pattern of the as-prepared TiO2/C/Ag nanocomposite is shown in Figure 6c. Four sharp peaks at 38.46°, 44.49°, 64.64°, and 77.80° are characteristic of Ag particles, which are attributed to the diffraction of (111), (200), (220), and (311) planes (JCPDS card no. 04-0783), respectively. The presence of the anatase phase of TiO2 NPs (JCPDS card no. 04-0477) can be confirmed through diffraction peaks at 25.61°, 48.46°, 54.19°, 55.28°, and 75.36°, corresponding to the planes of (101), (200), (105), (211), and (215), respectively, while weak peaks located at 27.80°, 69.33°, 63.18°, and 70.66° show rutile phase of TiO2 (JCPDS card no. 21-1276), corresponding to (110), (301), (002), and (112), respectively. The high-intensity peak observed at 25.61° indicates that anatase is the primary phase present in the TiO2 NPs.
To identify chemical bonds and functional groups, FT-IR analysis was carried out at a wavenumber of 500–4000 cm−1. A broad absorption peak appeared at 3672–3048 cm−1, indicating -OH stretching [40]. Absorption peaks at the wavenumber range of 2990–2909 cm−1 and 969 cm−1 exhibit the presence of C-H bonding vibration. A peak located at 1120 cm−1 is characteristic of C-O stretching vibration [36]. Four absorption peaks at 1364 cm−1, 1416 cm−1, 1599 cm−1, and 1603 cm−1 are attributed to the C=C vibration bond [41,42]. The presence of TiO2 NPs indicates a broad absorption peak at the wavenumber range of 890-524 cm−1 attributed to Ti-O vibration [43,44]. According to Figure 6d(III), no absorption peak related to Ag particles is observed, indicating non-chemical interaction between nanostructures.
As shown in Figure 6e, Raman spectroscopy was performed to provide detailed information about the chemical structure of lignin, lignin-derived carbon, and the TiO2/C/Ag nanocomposite. The peaks located at 1366 cm−1 and 1561 cm−1 are due to the C-H and aromatic ring stretching of lignin [45]. As shown in Figure 6e(II), a broad peak located in the range of 960–1761 cm−1 can be fitted with three peaks exhibiting T, D, and G bands. The peak located at 1380 cm−1 is attributed to the D band, suggesting double-resonance related to a chaotic carbonaceous structure (or A1g vibration mode that is characteristics of sp3 defects). The G band (1592 cm−1) is due to the in-plane vibration of E2g in sp2-bonded graphitic carbon [46,47]. A T band is also present at 1140 cm−1, which is related to impurities or heteroatoms [48,49]. After the laser ablation of lignin, a 2D peak with low intensity appeared at about 2720 cm−1, showing graphitic domains in the lignin-derived carbon [50]. According to the fitted peaks, the content of the D band (54.82%) was higher than the G band (32.55%), suggesting a disordered structure with defects for the prepared carbon [49,51]. As shown in the TiO2/C/Ag Raman spectrum, two peaks at 170 cm−1 and 397 cm−1 are attributed to Eg and B1g, respectively, indicating Raman’s active mode of the anatase phase, while the rutile phase of TiO2 NPs is determined through a peak at 597 cm−1 related to A1g [52,53]. Two peaks located at 751 cm−1 and 942 cm−1 are assigned to Ag particles [54].
XPS analysis was employed to determine the chemical states of the elements and compositions of the sample (Figure 7). Figure 7a indicates the survey spectra of TiO2/C/Ag nanocomposite that confirm the presence of C, O, Ti, and Ag elements. The high-resolution spectrum of C1s can be deconvoluted into four peaks at binding energies of 285.2, 286.8, 288.8, and 291.0 eV, consisting of C-C/C=C, C-O, O-C=O, and π-π binding, respectively (Figure 7b) [55,56,57]. According to Figure 7c, the deconvolution of O1s suggests the presence of lattice oxygen of Ti-O (530.7 eV), C=O (532.1 eV), and C-O (533.5 eV) bonding [58,59]. As shown in Figure 7d, two sharp peaks located at 459.7 and 465.4 eV indicate Ti2p3/2 and Ti2p1/2 of Ti4+, respectively, suggesting the presence of the anatase phase, while a shoulder at 460.8 eV is due to the presence of Ti3+ species [60,61,62,63]. According to the Ag3d spectrum, two strong peaks at 374.4 and 368.4 eV attributed to Ag3d3/2 and Ag3d5/2 can be observed, indicating Ag(0) [64,65].
To evaluate the surface area and pore size distribution of samples, BET and BJH analyses were performed (Figure 8). As depicted in Figure 8a–c, the N2 adsorption/desorption isotherm of the samples can be presented as type IV, indicating a type H3 hysteresis loop. This confirms a mesoporous structure for all samples [66,67,68,69]. The maximum pore diameters of 1.2, 7.9, and 29.5 nm were achieved for lignin, lignin-derived carbon, and the TiO2/C/Ag nanocomposite, respectively. Information about the surface structure of the samples is further detailed in Table 1. Using lignin as a carbon source can be effective for preparing porous carbon structures with significant surface areas. It is noteworthy to mention that the composition of lignin-derived carbon with TiO2 NPs and Ag particles can increase surface properties, especially surface area. It can provide active sites for dye removal.
The zeta potential of the TiO2/C/Ag nanocomposite was measured to identify the surface charge of the catalyst, respectively. As shown in Figure 9, the zeta potential of the TiO2/C/Ag was obtained as −25.5 mV, suggesting a high dispersity and good colloidal nature of the catalyst. It indicates that the catalyst surface is negatively charged [70,71].
The optical band gap of TiO2 and the TiO2/C/Ag nanocomposite can be calculated through the Tauc equation as follows [72,73]:
( α h ν ) r = E D ( h ν − E g )
Here, α, hν, Eg, and ED are the optical absorption coefficient, photon energy, optical band gap, and a constant, respectively. r indicates the nature of the electron transition and can be 2 or 1/2 for the direct or indirect transition band openings, respectively. The optical band gap can be obtained by generalizing the linear part of the (αhν)r-hν plot to zero optical absorption. Figure 10a shows UV-Vis absorption spectra of TiO2 and the prepared TiO2/C/Ag nanocomposite, in which no difference is observed between the two spectra. According to the Tauc plot of TiO2 and the TiO2/C/Ag nanocomposite, the direct band gap was obtained as 3.13 eV and 3.20 eV for TiO2 and TiO2/C/Ag samples, respectively. Therefore, the presence of carbon and Ag particles does not have an impact on the band gap values.

3.2. The Ability of TiO2/C/Ag Nanocomposite in the Reduction of MB, CR, and 4-NP

Developing a facile and fast method is necessary for reducing MB and CR from water resources. For this purpose, the catalytic reduction of MB and CR was examined using a hydrogen source of NaBH4 and a small amount of the TiO2/C/Ag nanocomposite at ambient conditions. This process was investigated by detecting the reduction of UV-Vis absorption peaks at λmax of ~664 nm (MB) and ~498 nm (CR). By adding fresh NaBH4 to the mixture of the nanocomposite and dyes, both UV absorption peaks completely disappeared after 10 s and 4 min, respectively (Figure 11a,b), suggesting a reduction/degradation of dyes. It is clear that the catalyst has better performance for MB reduction. According to the zeta potential result, MB can be adsorbed on the negative surface of TiO2/C/Ag due to the attraction of electrostatic interaction, improving the catalytic degradation/reduction reaction [74]. CR is a negatively charged dye that can reduce its adsorption on the TiO2/C/Ag nanocomposite compared with MB [75]. Figure 11c exhibits a mechanism for the catalytic reduction/degradation of MB and CR. The reduction of the dyes can occur through two steps by a TiO2/C/Ag nanocatalyst [9,76,77]: in the first step, dissociation of NaBH4 produces borohydride ions (BH4−), which can adsorb on the nanocatalyst. In the second step, the nanocatalyst accepts electrons from BH4− and transfers them to dyes adsorbed onto the nanocatalyst through π-π stacking interactions, leading to the reduction of dyes. Eventually, the reduced dye is released from the nanocatalyst. The presence of Ag particles reduces the kinetic barrier in the dye reduction process by transferring electrons from BH4− to MB or CR dye. In Table 2, the catalytic performance of the as-fabricated nanocomposite for reducing MB and CR dyes was compared with other nanocomposites, including Ag particles and TiO2 NPs. As is clear in Table 2, the TiO2/C/Ag nanocomposite indicates better catalytic activity, and the reduction of MB and CR with the prepared nanocomposite was performed in a shorter time.
Nitroaromatic molecules are toxic organic compounds that are widely applied in laboratories and industries. These compounds can create serious hazardous problems in the human health and environment at even low concentrations. The catalytic reduction of nitrophenols to aminophenols is important, especially for pharmacology industries. Aminophenol is a fundamental precursor for preparing drugs such as acetanilide and phenacetin. Therefore, the catalytic activity of the TiO2/C/Ag nanocomposite was examined for the reduction of 4-NP using a NaBH4 reducing agent. The reduction reaction was surveyed through UV-Vis measurements, as shown in Figure 12a. According to Figure 12a, a maximum absorption peak at 320 nm is observed for aqueous 4-NP with a yellow color [86,87]. After adding a fresh NaBH4 solution, the light yellow color of 4-NP changed to dark yellow and the absorption peak shifted to 400 nm, suggesting 4-nitrophenolate ions formation in alkaline conditions [88,89]. After adding the TiO2/C/Ag nanocomposite, the absorption peak at 400 nm was reduced and a peak at 300 nm appeared, which is characteristic of 4-aminophenol (4-AP). The absorption peak at 400 nm completely disappeared after 2.30 min and the dark yellow color turned to colorless. Figure 12b displays a schematic for the 4-NP reduction reaction. When the TiO2/C/Ag nanocomposite is added to the reaction system, Ag particles accept the electron from BH4− and it is transferred to the absorbed 4-NP on the nanocomposite. Finally, the produced 4-AP is desorbed from the nanocomposite surface and a free surface will be provided for another run of the catalytic reaction [9,35,77,90]. The catalytic performance of the TiO2/C/Ag nanocomposite for 4-NP reduction was compared with other reported catalysts, including Ag particles (Table 3).
TiO2 NPs are commonly used in dye removal because of their adsorption ability, increasing the removal rate [91,92,93]. In addition, the composition of carbon with TiO2 NPs can provide a synergetic effect on the adsorption of dyes. It can also create a porous structure with a high surface area for the adsorption of dye molecules and 4-NP [35,94,95].
The catalytic reduction/degradation of CR, MB, and 4-NP was tested in the absence of a catalyst (Table 4). It was found that the reaction between 4-NP and NaBH4 was not complete even after 2 h. In addition, using TiO2/C as the catalyst leads to a longer catalytic reduction/degradation of CR, MB, and 4-NP compared with TiO2/C/Ag, suggesting that the presence of Ag particles can speed up the catalytic reaction.
Table 3. Comparison of the catalytic performance of the TiO2/C/Ag nanocomposite with other reported nanocomposites, including Ag particles, for the reduction of 4-NP.
Table 3. Comparison of the catalytic performance of the TiO2/C/Ag nanocomposite with other reported nanocomposites, including Ag particles, for the reduction of 4-NP.
CatalystConcentration of 4-NPConcentration of NaBH4Reduction TimeRef.
Ag/N-RGO0.2 mM0.2 M400 s[96]
Ag/MWCNTs–chitosan0.10 mM5 mM5 min[97]
Calcinated TiO2/Ag core–shell5 mM0.02 M13 min[98]
Ag/TiO215 mg/L0.02 M50 min[99]
TiO2/C/Ag2.5 × 10−3 M250 mM2.30 minThis work

3.3. Catalyst Recyclability

The reusability of the TiO2/C/Ag nanocomposite was investigated through CR reduction. After each run, the catalyst was collected from the reaction mixture using centrifugation, washed with DI water three times, and dried at 80 °C. A slight reduction in catalyst efficiency was observed after three times (Figure 13). After the catalytic reaction, the presence of Ag particles and morphology of the nanocomposite were investigated through SEM images and elemental mapping analysis (Figure 14). The presence of Ag particles can be observed in SEM images. In addition, the Ti, C, O, and Ag elements are present even after the catalytic reaction.

4. Conclusions

In the present work, laser ablation in ambient air was used as a simple and fast method to prepare lignin-derived carbon and Ag particles, and then they were composited with TiO2 NPs (TiO2/C/Ag) through a stirring method. The morphology and structure of the catalyst were characterized using XRD, EDS, FT-IR, Raman, BET, and SEM analyses. The observations deduced from the Raman spectrum and FESEM micrographs substantiated the formation of a hybrid of Ag particles and TiO2 NPs. It was found that lignin can be successfully used as a carbon resource for preparing carbon nanostructures with significant surface areas. The composition of Ag particles and lignin-derived carbon with TiO2 NPs improved the surface area and average pore diameter. It can provide active sites for catalytic reactions. The catalytic efficacy of the prepared nanocomposite was examined in MB and CR reduction process. It was found that the nanocomposite can successfully reduce both dyes during 10 s (MB) and 4 min (CR). The catalytic activity of the TiO2/C/Ag nanocomposite was also examined for the reduction of 4-NP using a NaBH4 reducing agent, suggesting the complete reduction of 4-NP to 4-AP after 2.30 min. The TiO2/C/Ag heterogeneous catalyst is easy to recycle and the catalytic activity has not decreased significantly and has maintained its structure after three times of recycling. This study will shed light on the environmental applications of nanocatalysts and also the valorization of lignin as a natural source for the preparation of carbon. According to reports, TiO2-based nanocomposites are widely used for photocatalytic wastewater reactions, which occur over a long time. These nanocomposites are also used for the catalytic reduction/degradation of MB, CR, and 4-NP, which provides lower reaction times compared with photocatalytic reactions.

Author Contributions

Conceptualization, S.A.N. and B.J.; methodology, S.A.N. and B.J.; writing—original draft, S.A.N., B.J., E.D. and D.D.; writing—review and editing, S.A.N., B.J., E.D. and D.D.; validation, S.A.N. and B.J.; formal analysis, S.A.N. and B.J.; supervision, B.J.; investigation, S.A.N. and B.J. All authors have read and agreed to the published version of the manuscript.

Funding

We gratefully acknowledge Bu-Ali Sina University and Islamic Azad University Science and Re-search Branch for the support of this work.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

The original contributions presented in the study are included in the article.

Conflicts of Interest

The authors declare no conflicts of interest.

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Figure 1. Schematic of the preparation of carbon powder using laser ablation of lignin.
Figure 1. Schematic of the preparation of carbon powder using laser ablation of lignin.
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Materials 17 04118 g002
Figure 2. Schematic of TiO2/C/Ag nanocomposite preparation process.
Figure 2. Schematic of TiO2/C/Ag nanocomposite preparation process.
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Materials 17 04118 g003
Figure 3. (a,b) FESEM images of Ag particles and (c) SEM image of carbon.
Figure 3. (a,b) FESEM images of Ag particles and (c) SEM image of carbon.
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Materials 17 04118 g004
Figure 4. FESEM micrographs of the TiO2/C/Ag nanocomposite on different scales of (a) 10 µm, (b) 5 µm, (c) 500 nm and (d) 200 nm.
Figure 4. FESEM micrographs of the TiO2/C/Ag nanocomposite on different scales of (a) 10 µm, (b) 5 µm, (c) 500 nm and (d) 200 nm.
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Materials 17 04118 g005
Figure 5. (a) EDS spectrum and (b) elemental mapping images of the TiO2/C/Ag nanocomposite.
Figure 5. (a) EDS spectrum and (b) elemental mapping images of the TiO2/C/Ag nanocomposite.
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Materials 17 04118 g006
Figure 6. XRD patterns of (a) lignin, (b) carbon, and (c) TiO2/C/Ag nanocomposite; (d) FT−IR and (e) Raman spectra of (I) lignin, (II) carbon, and (III) TiO2/C/Ag nanocomposite.
Figure 6. XRD patterns of (a) lignin, (b) carbon, and (c) TiO2/C/Ag nanocomposite; (d) FT−IR and (e) Raman spectra of (I) lignin, (II) carbon, and (III) TiO2/C/Ag nanocomposite.
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Materials 17 04118 g007
Figure 7. (a) XPS survey spectra and high-resolution XPS spectra of (b) C1s, (c) O1s, (d) Ti2p, and (e) Ag3d of TiO2/C/Ag nanocomposite.
Figure 7. (a) XPS survey spectra and high-resolution XPS spectra of (b) C1s, (c) O1s, (d) Ti2p, and (e) Ag3d of TiO2/C/Ag nanocomposite.
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Materials 17 04118 g008
Figure 8. (a–c) N2 adsorption/desorption at 77 k and (d–f) pore structure of samples.
Figure 8. (a–c) N2 adsorption/desorption at 77 k and (d–f) pore structure of samples.
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Materials 17 04118 g009
Figure 9. Zeta potential analysis of TiO2/C/Ag nanocomposite.
Figure 9. Zeta potential analysis of TiO2/C/Ag nanocomposite.
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Materials 17 04118 g010
Figure 10. (a) UV-Vis spectra of TiO2 and TiO2/C/Ag nanocomposite, and (b) the Touc plot for TiO2 and TiO2/C/Ag nanocomposite.
Figure 10. (a) UV-Vis spectra of TiO2 and TiO2/C/Ag nanocomposite, and (b) the Touc plot for TiO2 and TiO2/C/Ag nanocomposite.
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Materials 17 04118 g011
Figure 11. (a) UV-Vis spectra of (a) MB and (b) CR reduction by TiO2/C/Ag catalyst and NaBH4. Conditions: 25 mL of NaBH4 (5.3 × 10−3 M), 25 mL of MB (3.1 × 10−5 M), 25 mL of CR (1.44 × 10−5 M), and 0.008 g of TiO2/C/Ag. (c) Mechanism for the reduction/degradation of CR and MB with the TiO2/C/Ag nanocomposite.
Figure 11. (a) UV-Vis spectra of (a) MB and (b) CR reduction by TiO2/C/Ag catalyst and NaBH4. Conditions: 25 mL of NaBH4 (5.3 × 10−3 M), 25 mL of MB (3.1 × 10−5 M), 25 mL of CR (1.44 × 10−5 M), and 0.008 g of TiO2/C/Ag. (c) Mechanism for the reduction/degradation of CR and MB with the TiO2/C/Ag nanocomposite.
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Materials 17 04118 g012
Figure 12. (a) UV-Vis spectra of 4-NP reduction. Conditions: 25 mL of NaBH4 (250 mM), 25 mL of 4-NP (2.5 × 10−3 M). (b) Mechanism for the 4-NP reduction using TiO2/C/Ag nanocomposite.
Figure 12. (a) UV-Vis spectra of 4-NP reduction. Conditions: 25 mL of NaBH4 (250 mM), 25 mL of 4-NP (2.5 × 10−3 M). (b) Mechanism for the 4-NP reduction using TiO2/C/Ag nanocomposite.
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Materials 17 04118 g013
Figure 13. The reusability of the TiO2/C/Ag nanocomposite for the reduction of CR using NaBH4.
Figure 13. The reusability of the TiO2/C/Ag nanocomposite for the reduction of CR using NaBH4.
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Materials 17 04118 g014
Figure 14. (a,b) SEM images and elemental mapping analysis of the TiO2/C/Ag nanocomposite after catalytic reaction.
Figure 14. (a,b) SEM images and elemental mapping analysis of the TiO2/C/Ag nanocomposite after catalytic reaction.
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Table 1. Surface area and porosity information of the samples.
Table 1. Surface area and porosity information of the samples.
SampleSurface Area
(m2/g)		Total Pore Volume
(cm3/g)		Mean Pore Diameter
(nm)
Lignin0.770.002512.9
Carbon25.530.167126.2
TiO2/C/Ag39.490.475148.1
Table 2. Comparison of the catalytic performance of the TiO2/C/Ag nanocomposite with other reported nanocomposites, including Ag particles, for the reduction of MB and CR.
Table 2. Comparison of the catalytic performance of the TiO2/C/Ag nanocomposite with other reported nanocomposites, including Ag particles, for the reduction of MB and CR.
PollutantCatalystConcentration of PollutantConcentration of NaBH4Dye Removal TimeRef.
MBAg NPs/silica spheres2 × 10−5 M1 × 10−2 M7.5 min[78]
Ag NPs0.001 M0.1 M13 min[79]
Ag/GO0.030 mM500 mM7 min[80]
Ag/silicon zeolite nanoparticle0.06 mM60 mM4 min[81]
Ag/RGO30 mg/L0.1 M10 min[82]
TiO2/C/Ag3.1 × 10−5 M5.3 × 10−3 M10 sThis work
CRAg NPs@hollow mesoporous carbon spheres0.086 mM0.5 M10 min[83]
Ag NPs1 mM10 mM15 min[84]
AgNPs/holocellulose nanofibrils30 mg/L400 mg/L30 min[85]
TiO2/C/Ag1.44 × 10−5 M5.3 × 10−3 M4 minThis work
Table 4. The effect of the presence of the catalyst and NaBH4 on the catalytic reduction/degradation of MB, CR, and 4-NP.
Table 4. The effect of the presence of the catalyst and NaBH4 on the catalytic reduction/degradation of MB, CR, and 4-NP.
PollutantCatalystNaBH4Time
4-NP-250 mM120 min a
TiO2/C (8 mg)250 mM120 min a
TiO2/C/Ag (8 mg)250 mM2.30 min
CR-5.3 mM35 min
TiO2/C (8 mg)5.3 mM20 min
TiO2/C/Ag (8 mg)5.3 mM4 min
MB-5.3 mM2 min
TiO2/C (8 mg)5.3 mM1 min
TiO2/C/Ag (8 mg)5.3 mM10 s
a Not complete.
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Almasi Nezhad, S.; Jaleh, B.; Darabi, E.; Dorranian, D. Laser-Assisted Preparation of TiO2/Carbon/Ag Nanocomposite for Degradation of Organic Pollutants. Materials 2024, 17, 4118. https://doi.org/10.3390/ma17164118

AMA Style

Almasi Nezhad S, Jaleh B, Darabi E, Dorranian D. Laser-Assisted Preparation of TiO2/Carbon/Ag Nanocomposite for Degradation of Organic Pollutants. Materials. 2024; 17(16):4118. https://doi.org/10.3390/ma17164118

Chicago/Turabian Style

Almasi Nezhad, Shahin, Babak Jaleh, Elham Darabi, and Davoud Dorranian. 2024. "Laser-Assisted Preparation of TiO2/Carbon/Ag Nanocomposite for Degradation of Organic Pollutants" Materials 17, no. 16: 4118. https://doi.org/10.3390/ma17164118

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