1. Introduction
The use of photocatalytic technology to chemically reduce carbon dioxide (CO2) into hydrocarbons not only transforms this greenhouse gas into reusable fuel, but also helps alleviate global warming [1]. However, CO2 is an extremely stable compound, and photocatalytic CO2 reduction with solar light still remains a challenge, mainly because of low solar energy conversion efficiency, backward reaction phenomenon, uncontrolled product selectivity and rapid electron-hole recombination rate of the photocatalyst [2].
As in many other environmental and energy applications, titanium dioxide has been the photocatalyst more widely used for the conversion of CO2 to fuel, mainly due to its photoactivity, high stability, low cost, and safety [3,4]. However, its application is limited because of its relative wide band gap (3–3.2 eV) and rapid recombination rate of photo-induced electron-hole pairs [5]. To overcome these drawbacks, different strategies have been proposed, such as doping with transition metal cations [6], using enhanced geometries [7] or photocatalyst supporting on carbon materials [8,9].
Non-metal doping is another approach suggested to improve TiO2 performance. Compared with metal doping, non-metal dopants lead to catalysts with higher photo-stability, less environmental contamination, and lower cost [10]. Particularly, doping with N atoms into the TiO2 lattice structure leads to the generation of N 2p energy levels near to the valence band (VB) of TiO2, thus reducing its band gap and extending semiconductor light absorption to the visible spectrum [5]. Moreover, N atoms also prevent the recombination of charge carriers in N-doped TiO2 and can form metastable centers due to their stability, low ionization potential and having an atomic radius comparable with oxygen [5]. However, the increases achieved in visible light absorption and lifetime of the electron-hole pairs photogenerated with this catalytic material are still limited.
Fortunately, this limitation can be alleviated by supporting the upgraded semiconductor on carbon nanotubes (CNTs) or reduced graphene oxide (rGO), since both carbon materials can increase the generation of excitons and reduce their recombination rates; thereby promoting a cooperative and synergistic effect that can enhance the overall efficiency of the photocatalytic process [11,12]. Further, CNT and rGO can provide large specific surface areas for photocatalysis [13]. Even more, the conductive structure of CNT and rGO scaffolds is believed to favor the separation of the photo-generated electron-hole pairs through the formation of heterojunctions (Scottky barrier) at the TiO2/CNT or TiO2/rGO interfaces [13,14]. Finally, from a morphologic point of view, the support of TiO2 over CNT and rGO avoids particle agglomeration [15] and, thus, improves the homogeneous dispersion of this semiconductor and the availability of most active centers.
Considering the above, the combination of N-doped TiO2 with carbon supports has been recently proposed and reported in literature [16,17]. However, for these complex systems, the joint effect of N-doping and carbon supporting of TiO2 on enhancing of sunlight absorption and electron-hole separation still remains unclear [10]. Particularly, there is controversy regarding which type of carbon support can be more beneficial for the photocatalytic reduction of CO2 [18,19]. Thus, the main objective of this work has been to develop N-doped TiO2 nanoparticles supported on CNT and rGO and to investigate the influence of the carbon support of the composites on both physicochemical properties and catalytic performance in CO2 photoreduction. To our best knowledge, this type of analysis is here tackled for the first time.
Regarding the synthesis of N-doped TiO2 nanostructures, it can be accomplished by different methods, such as sputtering, sol-gel process, anodic oxidation, microwave, hydrothermal, microemulsion, chemical vapor deposition, solvothermal, and electrospinning, among other processes. However, these processes usually suffer from scale-up problems and are not environmentally friendly [20]. Providentially, both obstacles may eventually vanish if the catalyst synthesis is carried out in a supercritical CO2 (scCO2) medium, i.e., in CO2 at pressure and temperature conditions above critical point [20]. Moreover, there are several favorable physical properties of the supercritical fluids, such as low viscosity, “zero” surface tension and high diffusivity [21], that enable them to produce superior, ultrafine, and uniform nanomaterials at appropriate operating conditions [22,23]. In addition, scCO2 can be removed completely from the products by venting. Thus, no drying process is required, and the porous structure can be maintained without collapsing of the nanostructure. Further, scCO2 can be easily recycled after decompressing and potential scale-up is feasible.
In view of the above, in this study we report for the first time on the one-pot synthesis of a series of N-doped TiO2 nanoparticles and N-doped TiO2-based composites (N/TiO2/CNT and N/TiO2/rGO) in scCO2 medium. For the nanomaterials synthesis process, titanium (IV) tetraisopropoxide (TTIP) and triethylamine (TEA) or urea were used as precursors of TiO2 and N, respectively, and ethanol was used as the hydrolytic agent, which decomposes to water molecules that react with TTIP to produce TiO2. CNT or rGO were also used in the synthesis of the composites. The characteristics of the synthesized materials, and their activities in CO2 photoreduction with water vapor under simulated solar light irradiation, were investigated. On this base, efficient photocatalytic conversion of CO2 was demonstrated. Further, the differences in selectivity and production rates of CO and CH4 obtained with each catalyst are explained in terms of the physicochemical properties of the catalytic material analyzed.
2. Materials and Methods
2.1. Chemicals
Multi-walled carbon nanotubes (MWCNT, purity > 98%) were supplied by Sigma- Aldrich (Darmstadt, Germany). For graphene oxide synthesis, potassium permanganate (KMnO4, analytical reagent), hydrochloric acid (HCl, 37%) and sulfuric acid (H2SO4, 30 wt. %) were provided by Panreac (Madrid, Spain), graphite powders by Merck (Darmstadt, Germany), and hydrogen peroxide (H2O2, 30 wt. %) by Scharlau (Barcelona, Spain). For the preparation of nitrogen-doped catalysts (N-doped TiO2, N-doped TiO2/CNT and N-doped TiO2/rGO), titanium (IV) tetraisopropoxide (TTIP, 98+%) was provided by Across Organics (Madrid, Spain), ethanol (analytical reagent) and triethylamine (TEA, EssentQ) by Scharlau (Barcelona, Spain), and urea (99–100.5%) by Sigma-Aldrich (Darmstadt, Germany).
CO2 (purities > 99.9% for synthesis and 99.998% for photocatalytic studies) was used as received from Nippon (Madrid, Spain) and Contse (Madrid, Spain).
2.2. Synthesis of Catalysts
The synthesis of rGO was performed by the Hummers’ method, as described in a previous work [9].
In the case of N-doped TiO2 nanoparticles, the one-pot reaction was developed by adding the titanium precursor (TTIP, 1.39 g), the hydrolysis agent (ethanol, 8 mL) and 1–4 mL TEA (0.8–2.9 g) or urea (0.3 g) as nitrogen precursor [20]. The reactions took place in a stainless-steel reactor (volume 100 mL) using scCO2 as solvent at a pressure of 200 bar and a temperature of 300 °C. This procedure was described in more detail in previous works [24]. Later, the solid obtained was dried at 105 °C for 24 h and calcined at 400 °C for 3 h. The catalyst was named NX/TiO2, X being the N content (mg N/g TiO2) in the synthetized N-doped TiO2 nanoparticles. All catalysts were obtained in triplicate.
A similar procedure was used for synthesizing composites of N-doped TiO2 over CNT or rGO (NX/TiO2/CNT and NX/TiO2/rGO, respectively). The quantities of TTIP and ethanol added were the same as those used for N-doped TiO2 nanoparticles but 390 mg of either CNT or GO were also aggregated, thus keeping the TiO2:carbon support mass ratio equal to 1 [8,9]. In this case, 1–4 mL (0.8–2.9 g) of TEA or 0.3 g of urea were employed. The conditions of the drying process of the composites were also the same. However, whereas N-doped TiO2/CNT composites were calcinated at 400 °C for 3 h [8], the conditions for N-doped TiO2/rGO composites were 500 °C for 3 h in a nitrogen atmosphere [9].
2.3. Characterization of Catalysts
The synthesized photocatalysts were characterized with different analytical techniques. The N content was determined in an elemental analyzer (CHNS-932, LECO, Geleen, The Netherlands). A transmission electron microscope (TEM, 2100, Jeol, Croissy-sur-Seine, France) was used to obtain information about the morphology of the catalysts. An X-ray powder diffractometer (XRD, X’Pert MDP, Phillips, Amsterdam, The Netherlands) was used to determine crystallinity, crystallite size and crystalline phases of the catalysts. The specific surface area of the powders was measured using a BET area analyzer (Nova Touch LX2, Quantachrome, Graz, Austria). The presence of certain functional groups was determined by Fourier Transform Infrared spectroscopy (FTIR) analysis with a Spectrum 100 FTIR spectroscope (Perkin-Elmer, Madrid, Spain). The X-ray photoelectron spectroscopy measurement (XPS) was made in an XPS-AES spectrometer (AXIS UltraDLD, Kratos, Manchester, UK). A diffuse reflectance UV-vis spectrophotometer (DRS, V650, Jasco, Croissy-sur-Seine, France) was employed to obtain absorbance thresholds and band gap energies. Electrochemical impedance spectroscopy (EIS) experiments were performed using a PGSTAT302N potentiostat (AUTOLAB, Utrecht, The Netherlands), a 0.1 M KHCO3 solution was used as electrolyte, a calomel electrode as reference electrode, a Pt electrode as counter electrode and a frequency range of 0.005–10,000 Hz.
2.4. Photocatalytic Reaction Tests
For all synthesized catalysts, the photocatalytic reduction of CO2 in gas phase with water vapor was performed, as described in previous works [8,9]. In short, the catalyst (50 mg) was immobilized in a filter and placed inside a stainless-steel reactor with a quartz window. Then, the reactor was filled with the mixture of water vapor and CO2 until the operating conditions were reached. Next, it was illuminated using a Xe arc lamp (450 W, Oriel, Irvine, CA, USA) with an Air Mass 1.5 Global filter to simulate sunlight. Once the experiment was finished, after 3 h of reaction, the reduction products were determined with a GC (490 Micro GC, Agilent, Santa Clara, CA, USA) connected to the reactor.
Control experiments were performed for the evaluation of photocatalysts. Results from these tests showed no appreciable amounts of reduced products in the absence of catalysts or light irradiation, illustrating that the process occurring in the reactor was photocatalytic in nature. Additionally, no reduction products were detected when introducing He into the reactor, instead of CO2, or when adding CO2 in the absence of water under light irradiation, indicating that the CO and CH4 originated from CO2 in the presence of water under light irradiation.
3. Results
3.1. N Content of the N-Doped Catalysts
In the first place, when both supports (CNT and rGO) were doped with N using 1–4 mL of TEA, a N precursor first employed in supercritical doping by Lucky and Charpentier [20], the N loads reached a maximum of 2 mg N/g CNT and 10 mg N/g rGO, respectively (Table 1). When they were doped with 0.3 g of urea (the maximum amount allowed before it precipitates from the ethanol solution in the presence of TTIP), the resulting N concentrations were 2 mg N/g CNT and 42 mg N/g rGO, respectively.
These results illustrate that larger N loads were achieved in the rGO support, regardless of the N precursor used for doping.
Regarding N-doped photocatalysts (Table 2), when they were synthesized with TEA, it can be seen that the N content in N-doped TiO2 nanoparticles, N-doped TiO2/CNT composites and N-doped TiO2/rGO composites was about 1 mg N/g TiO2. N content expressed in mg N/g TiO2 in composites was estimated according to the results in Table 1 for N-doped supports and considering the results in Table 2 for N-doped TiO2 nanoparticles.
On the other hand, it can be appreciated that the N content of the catalysts obtained with 0.3 g urea was always larger than those produced from TEA, this effect being especially noticeable in the presence of rGO.
These results demonstrated the well-known fact that the N content of N-doped TiO2-based catalysts largely depends on the molecular structure of the source of nitrogen and the accessibility of nitrogen atoms to react with the titania precursor and support [25]. In this sense, primary and secondary amines are likely to provide a N-richer catalyst material. For this reason, most works have used urea, since its primary amine structure is likely to introduce the highest amount of N to the catalyst. Triethylamine, as a tertiary amine, was expected to provide less nitrogen atoms to titania than urea. However, it should be noted that this does not necessarily imply that the photoactivity of TEA-doped catalysts will be lower [26,27], as will be shown below.
In the following sections the nature of the nitrogen present in the synthesized catalysts and the catalyst properties it affects will be discerned.
3.2. Photocatalytic Activities
Figure 1 shows the CO2 conversion rates obtained with different synthesized catalysts during its photoreduction with water vapor in the presence of simulated sunlight. The average value and standard deviation of 3 replications for each material are presented. They are expressed in terms of µmol of product per hour and gram of TiO2, which is the photo-active species. As was the case with undoped and metal-doped TiO2 particles [6], TiO2/CNT [8], and TiO2/rGO composites synthesized in supercritical medium [9], the only reduction products detected were CO and methane. Moreover, all the prepared catalysts showed higher photocatalytic activity than the previous bare TiO2 nanoparticles synthesized in supercritical medium, indicating that the presented one-pot method for doping + synthesizing + supporting the photocatalyst is an efficient way to produce photocatalysts with higher activity than that exhibited by TiO2.
Previously, similar experiments with all synthesized N-doped supports were performed, with smaller CO and methane concentrations obtained than the detection limits in all cases.
Specifically, the results obtained in this work can be differentiated into 3 groups. On the one hand, the N-doped TiO2 nanoparticles (N1/TiO2) doubled the CO2 total conversion rates of non-doped TiO2 nanoparticles obtained at supercritical conditions (3.2 µmol products/h/g TiO2) (Figure 1) and tripled that of P25 (2.1 µmol products/h/g TiO2) [8]. Regarding the products obtained, the selectivity towards methane was greatly increased (selectivity 91%) compared to undoped TiO2 particles (selectivity 57%) [8]. This selectivity was calculated according to Fu et al. (2020) [28]. Next, the N-doped TiO2/CNT composites (e.g., N1/TiO2/CNT) exhibited lower results than those corresponding to the non-doped composites, both in total conversion (4 vs. 9.1 µmol products/h/g TiO2) and in selectivity towards methane (9% vs. 40%) [8]. Finally, the N-doped TiO2/rGO composites obtained from TEA as N precursor (N1/TiO2/rGO) showed similar selectivity towards methane as the undoped TiO2 catalysts supported on rGO (around 10%), but the total CO2 conversion rates were about 50% higher (7.7 vs. 5.1 µmol products/h/g TiO2) [9].
On the other hand, it can be appreciated that the results (CO2 conversion and selectivity towards CH4) were slightly lower for the catalysts with higher N content synthesized using urea as N source. Particularly, only the methane selectivity of composite N2/TiO2/rGO (synthesized from urea) (22%) was slightly higher than that of composite N1/TiO2/rGO, a composite obtained from TEA.
In conclusion, it was shown that, whereas supporting on CNT did not improve the results of TiO2 nanoparticles, supporting on rGO improved the CO2 conversion but not CH4 selectivity, when similar N content (in terms of mg N/g TiO2) was employed.
Obviously, the results obtained with CNT composites were unexpected and may be imputed to the lower crystallinity and crystal size of N-doped TiO2/CNT composites when compared with TiO2/CNT composites, as will be shown in corresponding sections. Moreover, XPS analysis suggested that N incorporation took place mainly in the bulk, but not on the surface, in N-doped TiO2/CNT composites, as the N-containing active sites were less accessible. Both phenomena lead to lower charge transfer and, consequently, lower photocatalytic activity.
In the following sections we will further explain these results considering the characteristics of the different catalysts. However, before this, they will be compared to those obtained in similar studies with N-doped catalysts synthesized with traditional methods. In this sense, it can be seen in Table 3 that the results from this work are far higher than those reported in the bibliography for N-doped TiO2 nanoparticles and N-doped TiO2/carbon support composites.
The photocatalytic mechanism of N-doped TiO2 catalysts may be described as follows [14] (Figure 2a). The N 2p energy level, situated above the VB of TiO2, forms a narrower band gap than that of bare TiO2, which extends the absorption of N-doped TiO2 into the visible region. Under solar light irradiation, electron-hole pairs are generated by two different routes. Specifically, electrons from the N 2p level are excited to the TiO2 conduction band (CB) by visible light, while those from the TiO2 valence band (VB) may be excited to the CB of the semiconductor by UV irradiation.
According to Wu et al. (2021) [10], the photocatalytic reduction of CO2 in the gas phase with N-doped TiO2 nanoparticles begins with the adsorption of CO2 molecules on the surface of the catalyst to form carbonate species. Then, electrons produced by the photocatalytic mechanism described above may reduce these adsorbed CO2 molecules to product CO through the protonation of ·COOH intermediate. Density functional theory (DFT) calculations found that enhanced surface polarization, due to N doping and oxygen vacancy, gives rise to significant charge accumulation on CO2 molecules, leading to the activation of CO2, which reduces the energy barrier to generate intermediate products and facilitate electron transfer at the interface [8]. In the case of CH4, the proposed mechanism implies the reaction of adsorbed HCO3− with an electron to form C· radicals, which can convert into CH4 after successive reactions with H· radicals, via CH3· radical intermediate [2].
In the case of N-doped TiO2/carbon support nanocomposites (Figure 2b), as some studies [13,31] have hypothesized, under simulated sunlight radiation electrons and holes may be generated and transferred between the interface of support and N-doped TiO2, leading to charge recombination possibly being effectively retarded in the N/TiO2/CNT and N/TiO2/rGO composites. The holes formed in the VB of N-doped TiO2 may oxidize H2O molecules absorbed on the surface of particles to generate O2 and protons. The photogenerated electrons could be transferred from the CB of N-doped TiO2 to the carbon support via a percolation mechanism [14], where they could reduce CO2 molecules to CO and methane [31]. The absence of CH4 in some supported catalysts (as in our N-doped TiO2/CNT and TiO2/rGO composites) suggests that the protons from water may fail to capture the photogenerated electrons to form H· radicals, because they fall into electron-rich aromatic cycles of support, where they could be stabilized, as it is hard for them to participate in the production of CH4. For this reason, in the case of unsupported N-doped TiO2, due to the absence of the conjugated aromatic system, H+ or H· radicals generated in the photocatalytic reaction may quickly be consumed by CO2 in the photocatalytic process, and CH4 and CO simultaneously detected [31].
To sum up, N-doping reduces the energy necessary to reduce CO2 into CO and CH4 (i.e., it enhances the light absorption of photocatalysts in the visible region), whereas carbon support enlarges the time required for charge recombination. Both measures lead to higher photocatalytic activity of the synthesized catalysts. Regarding selectivity towards CH4, it seems to be influenced by the availability of H· radicals coming from H2O oxidation.
3.3. Surface Morphology Analysis (TEM)
TEM was carried out to analyze the structure and morphology of the samples and the results are shown in Figure 3.
In the case of N-doped TiO2 nanoparticles (Figure 3a), aggregates of polyhedral particles with crystallite sizes in the range of 11–14 nm and well-defined lattice fringes, suggesting a highly crystallized anatase structure, are observed [10]. The morphology is similar to undoped TiO2 [24], except that the crystallite sizes are larger [2]. Lucky and Charpentier (2010) observed that alkylamines used as N dopant in supercritical synthesis can form amine complexes with metal alkoxides, thus favoring the aggregation of the metal oxide particles [20]. All these findings will be corroborated by the results obtained in the next sections.
Regarding the supports (Figure 3b,c), neither N-doped CNT nor N-doped rGO show any difference from undoped supports [8,9]. When these supports are mixed with titania precursor, hydrolysis agent and N precursor in supercritical media, it is evident that N-doped TiO2 nanoparticles are successfully deposited on both CNT and rGO (Figure 3d,e).
Figure 3d shows that TiO2 nanoparticles are uniformly dispersed over CNT, as was found in previous works on N-doped TiO2/CNT composites synthesized with traditional synthesis [32] and undoped TiO2/CNT composites synthesized with supercritical fluids [8]. The crystallite size was about 10 nm, showing a narrower distribution than unsupported N-doped TiO2 nanoparticles (14 nm). In this sense, some works [33] explain that nitrogen-containing groups in the carbon support may serve as favorable nucleation and anchor sites for TiO2 nanocrystals. The smaller size of TiO2 nanoparticles in composites might be due to stronger coupling between TiO2 and N-doped sites on the support [33].
When TiO2/rGO composites are analyzed (Figure 3e), there is no sign of agglomeration of TiO2 nanoparticles, which are well distributed over the rGO support. The crystallite size of these particles is about 13–14 nm, like those of undoped TiO2/rGO composites synthesized with supercritical fluids (13 nm) [9]. Daraee et al. (2020) reached similar results when performing traditional synthesis [34].
If the influence of TiO2 crystallite size on photocatalytic activity is analyzed, it can be observed that photocatalytic activity may be directly related to crystallite size, since N-doped TiO2 nanoparticles and N-doped TiO2/rGO composites lead to higher CO2 reduction rates than N-doped TiO2/CNT composites. This phenomenon can be derived from a higher charge transfer, as will be shown in the corresponding section [9].
Before concluding this section, we should note that the photocatalysts N1/TiO2, N1/TiO2/CNT and N1/TiO2/rGO presented in this and the following sections were synthesized using 1 mL of TEA. This was done because, according to the results presented in Table 2, the N load in N-doped TiO2 nanoparticles and in N-doped TiO2 supported on CNT and rGO was always the same, regardless of the amount of TEA (N precursor) used in the synthesis (Table 2).
3.4. Crystalline Structure Analysis (XRD)
The crystal structure and phase identification of TiO2 in the synthesized catalysts were investigated by using XRD technique. The XRD diffractograms are displayed in Figure 4.
In all samples, no matter if they were bare TiO2 [24] or supported on CNT [8] or rGO [9], the patterns were well matched with anatase-phase TiO2, indicating that the crystalline structure of synthesized TiO2 was not affected by doping [2] and supporting during the one-pot synthesis process [34,35].
Changes were observed in the peak shape and intensity in XRD patterns of N-doped TiO2 particles with respect to that of undoped TiO2 [36]. The increase in peak intensity of N-doped TiO2 catalysts, compared to that of undoped TiO2, indicates that N doping could enhance the crystallinity of TiO2 particles [2].
The crystallite sizes of modified TiO2 catalysts were estimated from XRD patterns using the Scherrer equation and are listed in Table 4. All synthesized catalysts possess smaller crystallite sizes than the reference P25 (20 nm) [37]. In our case, the crystallite sizes of N-doped TiO2 nanoparticles increased from 11 to 14 nm with increasing amounts of nitrogen from 0 to 2 mg N/g TiO2. This trend was observed in N-doped TiO2 catalysts obtained with traditional methods [37]. The values agree with those reported in a former study dealing with the synthesis of N-doped TiO2 catalysts in supercritical fluids [20]. It can be concluded that the presence of nitrogen doping influences the crystallite size of TiO2 grown during the doping process [30], as was observed in TEM images.
No drastic shift or presence of new peaks were observed, indicating that N doping did not lead to the formation of any secondary and impurity phases in the host TiO2, rather than occupancy of oxygen sites or inclusion in TiO2 lattice [5], which will be discerned later.
Regarding composites with CNT, the peaks in N-doped composites were wider than those in the undoped CNT-supported composite [8], which shows that degree of crystallization of TiO2 is slightly weakened by ion implantation [38], contrary to what happened with unsupported catalysts. In this sense, crystallite size decreased from 16 to 10 nm when undoped TiO2/CNT composites were doped with 2 mg N/g TiO2. This finding could be related to stronger coupling between TiO2 and N-doped sites on the support, as was explained in the previous section [33]. No characteristic peaks of CNTs were found in the composites, which may be the result of overlap between the intense peaks of CNTs and anatase at 25.9° and 25.2°, respectively [35]. This could also be attributed to the homogeneous coverage of TiO2 on CNTs [8].
In the case of composites with rGO, it can be observed that peaks of N-doped TiO2/rGO composites were slightly narrower than those of undoped TiO2/rGO composites [9]. This is probably due to altering the crystallite size of base TiO2 crystallites [34]. As a result, a small increase in crystallite size, up to 14 nm, was observed upon 1 mg N/g TiO2 doping. When N content increased (as in N2/TiO2/rGO), crystallite size decreased. Just as happened with CNTs, the main characteristic peak of graphene at about 25° is shadowed by the main peak of anatase TiO2, surely due to the homogeneous dispersion of TiO2 on rGO [39].
To sum up, measurements of crystallize sizes agreed with the results observed by TEM methodology and supported the trends in photocatalytic activity presented in Section 3.2.
3.5. Surface Area Analysis (BET)
Specific surface area is another critical parameter in determining the photocatalytic activity of TiO2. If a catalyst exhibits large surface area, the adsorption of many molecules takes place on its surface and reactions are promoted [37]. However, a large surface area is generally related to more crystalline defects. An excess of defects could assist in recombination processes of charge carriers and induce poor photocatalytic activity. Thus, an adequate surface area is a prerequisite, but not a deciding factor for a higher activity [40].
We observed that all isotherms of bare and N-doped TiO2 nanoparticles (depicted in Figure S1 in Supplementary Materials) displayed the typical structure of type IV isotherms with well-defined H1 hysteresis loops, indicating the characteristic of capillary condensation within uniform mesoporous structures, and confirming that mesoporous structures were well retained in TiO2 nanoparticles during the simultaneous processes of synthesis and nitrogen doping [2].
Table 4 presents the BET areas of the synthesized materials. The values for N-doped TiO2 nanoparticles agree with those reported by Lucky and Charpentier (2010) when this type of catalyst was obtained in supercritical medium [20]. As shown, in the presence of N a decrease in the specific surface area was observed [2]. This could be attributed to the higher crystallite sizes of N-doped TiO2 catalysts described in the previous section and caused by N present in the form of interstitial N (Ti-O-N or Ti-N-O), or substitutional N (Ti-N), since the N3− ion has a larger ionic radius (0.171 nm) than the O2− ion (0.140 nm) [2]. The presence and abundance of these N species will be treated more deeply in Section 3.7.
The supported catalysts exhibit similar or larger specific surface areas than TiO2 nanoparticles due to the presence of carbon supports. The values coincide with those of composites obtained by both traditional [34,41] and high-pressure methods [8,9]. Moreover, there was reduction in support surface area in the TiO2/support composites that suggests the existence of a partial blockage of CNTs inner surface [8] and partial rGO surface coverage [9].
Finally, it can be verified that opposite trends of crystallite sizes and BET areas were fully met in our experimental results, both for unsupported and supported TiO2 catalysts (Table 4).
3.6. Surface Functional Groups Analysis (FTIR)
The FTIR spectra of the synthesized materials are shown in Figure 5. In the case of N-doped TiO2 nanoparticles, the broad band in the region 3600–3200 cm−1 can be ascribed to the stretching vibration of the surface-bonded Ti-OH groups, which may act as proton source to decrease CO2 activation energy during the reduction process [10]. Moreover, this band broadens and shifts to a lower wavenumber in N-doped TiO2 nanoparticles in contrast to undoped TiO2, due to the incorporation of N atoms and N-containing groups into TiO2 [42]. The weak bands at about 2900 cm−1 can be related to the stretching-vibration mode of C-H bonds that could possibly derive from the residues produced during the calcination of the precursors involved [5]. The small peak at around 2340 cm−1 can be associated to the bending vibration modes of the H-H bond, and the peak around 1630 cm−1 to the bending vibration of O-H of the physisorbed water molecules [5]. The band around 750 cm−1 is assigned to the characteristic stretching-vibration mode of Ti-O-Ti bonds of anatase TiO2. This peak is sharper and suffers from a shifting to higher wavenumber in N-doped TiO2 because of the O-Ti-N and N-Ti-N linkage [8,40]. The tiny peak around 1375 cm−1 could correspond to trace N atoms (N-H linkage) that are substituted into the lattices of TiO2, or be due to the presence of molecular residues from triethylamine [5,42].
Regarding N-doped CNT and TiO2/CNT, the presence of OH groups and water on the surface of the catalysts was confirmed by the appearance of a broad band at about 3400 cm−1 [13]. As explained before, the presence of hydroxyl groups on the composite surfaces plays an important role in photocatalytic activity. The band due to the stretching and bending modes of Ti-O and O-Ti-O appears as a broad band at about 600 cm−1 in the spectra of the composites [13]. Some characteristic peaks of CNT are observed in composites due to the large percentage of CNT in the nanocomposites, such as peaks in the region 2980–2880 and 1000 cm−1 (C-C bonds), and at about 1600 cm−1 (carbonyl C=O bonds). The weakening of the intensity of the peaks in the nanocomposites is due to the breaking down of CNT walls to its graphitic fragments and the attachment of these graphitic fragments onto, and into, the TiO2 nanocrystals [42]. This confirms the incorporation of CNT into the nanocomposites. The incorporation of N into carbon material was also demonstrated by the small C-N peak at 1325 cm−1 [42].
In addition to the striking peak at 3400 cm−1 related to OH groups and mentioned in the two previous cases, N-doped rGO and TiO2/rGO composites exhibited signals at 2800, 1625 and 1500 cm−1 associated with the stretching of C-OH, the presence of C=O and the deformation of C-O groups of rGO [43]. The 2800 cm−1 signal could overlap with C-C signals at 2852 and 2919 cm−1 [44]. These surface oxygen-containing functional groups render the possibility of covalent linkage of TiO2 onto the rGO surface [45]. The main difference between N-doped TiO2/rGO composites and rGO is the band at 650 cm−1 related to the Ti-O-Ti bonds. The broadening of this peak may suggest the presence of a peak due to Ti-O-C bond. This confirms that TiO2 nanoparticles could be strongly bonded to graphene sheets [34]. In addition, the peaks at about 1360 and 1550 cm−1 showed the possible presence of C-N bond from pyrrolic nitrogen (interstitial) and C=N from pyridinic nitrogen (substitutional), respectively [46]. Although they can also be related to C-O and C-C bond bands, respectively [47]. N2/TiO2/rGO catalyst does not show any difference with the composite with lower N content.
3.7. Surface Chemical Analysis (XPS)
The chemical state and surface composition of N-doped catalysts were investigated using the XPS technique. The full scan spectra are displayed in Figure 6 and show the existence of N, O, Ti and C in the samples. In the case of N-doped TiO2 nanoparticles, C 1s peak can be ascribed to remnant organic precursors not completely removed during the calcination [37].
The narrow scan Ti 2p spectra of N-doped TiO2, TiO2/CNT and TiO2/rGO (Figure 7) identified two Ti characteristic peaks located at 458.5 and 464.2 eV. They correspond to typical binding energies of Ti4+ (Ti 2p3/2 and Ti 2p1/2 of TiO2) [48]. However, these peaks were 0.65 eV lower than those of bare TiO2, which may be an indication of successful N doping. The N element is less electronegative than the O element. When N atoms are present in the TiO2 lattice, a part of Ti4+ is reduced to Ti3+, which may lead to decrease in the binding energy of Ti 2p [38]. The absence of other non-Ti4+ species or deconvoluted peaks of Ti could also be due to the resolution of XPS, which was unable to detect minor changes of TiO2 or because the Ti3+ species exist in the subsurface or bulk, which is inaccessible by XPS [37]. In any case, according to our results it seems that the replacement of oxygen atoms with nitrogen atoms in the TiO2 structure of both TiO2 nanoparticles and nanocomposites may have not occurred [5]. To sum up, Figure 7 depicts that TiO2 is present in all catalysts, and this TiO2 may be interstitially doped with N.
The deconvoluted O 1s spectra of N-doped TiO2 nanoparticles, TiO2/CNT and TiO2/rGO composites (the latter as example, Figure 8a) showed the peak at 529 eV representing the stoichiometric existence of oxygen network in TiO2 with respect to Ti (Ti-O) as well as the doped N (Ti-O-N) [5]. The peaks at 531 eV and 535 eV corresponded to surface adsorbed oxygen and water, respectively [49,50]. When O 1s spectra of supports and composites were compared (N10/rGO as example, Figure 8b), new peaks at 531 and 533 eV appeared, related to C=O (carbonyl, carboxyl) and C-O (epoxy, hydroxyl) groups, respectively [50]. All these results imply that TiO2 may be doped with N, and the existence of functional groups in supports are susceptible to have bound TiO2 particles.
In the case of N-doped CNT and TiO2/CNT composites (shown N1/TiO2/CNT as example in Figure 9a), the C 1s spectra are deconvoluted into two peaks at 283.6–284.5 and 290.1–290.9 eV [17]. The first one is bigger and due to graphitic carbon in CNT, whereas the second one is related to C=O/C-N bonds [50]. C 1s spectra of N-doped rGO (Figure 9b) and TiO2/rGO composites (Figure 9c) can be deconvoluted into 2 and 4 peaks, respectively. The peaks at 283.8–284.5 eV and 290.9 eV indicate the presence of graphene C-(C,H) and O-C-O bonds in rGO, respectively [43]. The relatively weak signal of the C-O groups indicates that most of the GO oxygen is reduced during the synthesis of catalysts in supercritical medium [51]. The first peak also appears in the N-doped TiO2/rGO composite, proving that the structure of graphene remains after the synthesis of composite catalyst [39]. Moreover, the two small peaks at 286.3 and 288.7 eV in TiO2/rGO composite can be associated with C-O and C=O bonds in support, respectively.
In N-doped TiO2 nanoparticles, CNT, rGO, TiO2/CNT and TiO2/rGO composites (N1/TiO2/CNT for example, Figure 10a), the only peak at 399.4-399.8 eV corresponding to N 1s confirms the existence of interstitial N in TiO2 (Ti-O-N) and the absence of substitutional N (N-Ti-N) [5]. According to Wang et al. (2009), at relatively low calcination temperature (<600 °C), N atoms tend to sit in the interstitial sites, above all if the N atomic percentage is below 1.2 [52]. At a relatively high calcination temperature (600 °C), some of the N atoms are incorporated into the TiO2 lattice substitutionally, in addition to the presence of interstitial N atoms. In the case of N-doped rGO (Figure 10b) two additional peaks at 398.2 and 404.2 eV are present. The first one can be related to pyridinic N, whereas the second one to C-N-O, indicating the successful doping of N atoms into the graphene framework [51].
From XPS analysis, the atomic percentage of N in the TiO2 crystal lattice is about 0.22 in N-doped TiO2 nanoparticles and N-doped TiO2/rGO composite, but 0.13 in N-doped TiO2/CNT composite. There seems to be some kind of correlation with the support used, since N-doped CNT and rGO exhibit 0.06 and 1.06 atomic percentage of N, respectively. If these figures are compared with those obtained in Section 3.1 with elemental analysis, it seems that N incorporation takes place mainly on the surface in the case of TiO2 nanoparticles and TiO2/rGO composites, but in the bulk in the case of bare CNT and TiO2/CNT nanocomposites [27]. This could also have contributed to the lower photocatalytic yield of N-doped TiO2/CNT composites, where N-containing active sites are less accessible.
As a summary, XPS analyses allow us to state that the one-pot supercritical process achieved interstitial N-doping within both the TiO2 lattice structure and carbon support framework, almost complete reduction of GO into rGO, and the preservation of the graphitic structure of the supports.
3.8. Optical Properties Analysis (DRS)
The optical UV-vis light absorption characteristics of the synthesized catalysts were investigated using diffuse reflectance UV-visible absorption spectroscopy. Some of the obtained spectra are displayed in Figure 11. The band gap energy and absorption threshold of the synthesized samples and supports were estimated as in previous works [6] and are given in Table 4.
On the one hand, it can be seen in the absorption spectra that the absorption threshold of undoped TiO2 nanoparticles at 400 nm was shifted to 405 nm in the case of TiO2 nanoparticles with 1 mg N/g TiO2. This indicates that N-doping slightly expanded the optical absorption of TiO2 nanoparticles to the visible light region. Accordingly, the band gap energy of undoped and N-doped TiO2 nanoparticles were 3.10 and 3.06 eV, respectively. This enhancement in optical properties could result from the formation of energy levels near and above the valence band (VB) of TiO2 due to doped N atoms [5]. This slight decrease in band gap energy agrees with works on the traditional synthesis of N-doped TiO2 [2].
As explained before, in the doping procedure N can create space for itself in the bulk or on the surface. If the crystallization of titania occurs while the dopant source is added, the N incorporates in the crystal lattice [53]. The dopant species could be incorporated in the crystal lattice occupying either a substitutional (Ti-N) or an interstitial site (Ti-O-N), which leads to the formation of a new band between the CB and VB of titania, resulting in reduction of the band gap energy [53]. Substitutional doping involves oxygen replacement, whereas interstitial doping involves the addition of nitrogen into TiO2 lattices. Substitutional N introduces localized nitrogen states up to 0.14 eV above the VB and interstitial N forms Π-character states up to 0.74 eV above the VB. The excitation from the occupied high energy levels to the CB is more favorable with interstitial N-doped TiO2, exhibiting higher visible light activity [53]. However, the absorbance of a photocatalyst cannot be directly correlated to its photoactivity, so improvement in photocatalytic activity may not necessarily be observed, due to band gap reduction [40].
Regarding the influence of calcination temperature on light absorption, Sathish et al. (2005) found that the light absorption of N-TiO2 particles in the visible region decreased very significantly as the calcination temperature increased above 400 °C, due to a decrease in the amount of N doping in TiO2 with calcination temperature [54].
On the other hand, it is not surprising that the light absorption spectra of composites and supports (CNT or rGO) are similar since the composite surface is not fully covered with TiO2. The particular shape of absorbance curves for carbon supports and composites has also been observed in other works dealing with traditional synthesis of N-doped TiO2/carbon support composites [39]. Precisely, this very special form prevents us from calculating the band gap energies of composites with the same graphical method described in reference [6], as happened in previous works [8,9]. For this reason, it is necessary to apply Tauc’s graphical procedure (Figure S2) [15]. With it, values of band gap energies of about 2.10 eV and 2.40 eV were obtained for N/TiO2/CNT and N/TiO2/rGO, respectively, proving that the composites have higher visible light absorbance after N-doping and loading of N-TiO2 [55]. In the case of the TiO2/rGO catalyst, with higher N content (N2/TiO2/rGO), the absorbance was slightly higher than that of N1/TiO2/rGO, being the value of the band gap energy 0.05 eV smaller.
These findings may be due to doping of N into TiO2 lattice narrows its band gap whilst the carbon support decoration could also improve photo-absorption in the visible light region and reduce the reflection of light [55]. This shift in the absorption threshold to the visible light range is consistent with the color change observed in powders, from white (undoped TiO2) to light grey (N-doped TiO2) and dark grey/black (N-doped TiO2/CNT and N-doped TiO2/rGO) [56].
3.9. Electrical Properties Analysis
Finally, electrochemical impedance spectroscopy (EIS) was employed to evaluate the photo-excited charge-transfer property of the photocatalysts. Nyquist plots (Z″ vs. Z′) of the different photocatalysts are depicted in Figure 12.
Undoped TiO2 and N-doped TiO2 nanoparticles (N1/TiO2 as example) show a similar semicircular shape (Figure 12a). As the arc radii are alike, this implies similar resistance for charge transfer and similar charge separation efficiency for both photocatalysts. The results are coherent with those corresponding to TiO2 nanoparticles synthesized with traditional methods [57] and it is expected that the arc radius would be reduced if far more N content could be introduced into the photocatalyst [10].
In the case of CNT/TiO2 and rGO/TiO2 composites, all four catalysts show the typical characteristics of one semicircle in the middle-high frequency range and a sloping straight line in the low frequency (Figure 12b). The arc radii of the EIS Nyquist plot of the composites are far smaller than those of TiO2 nanoparticles [33,51], indicating that the interface layer resistance and the charge transfer resistance on the surface are diminished, which reveals that charge migration is facilitated by interfacial interaction between the TiO2 and carbon material (CNT or rGO) occurring in the TiO2-C heterojunction [58].
Regarding N-doping, EIS Nyquist plots show that the arc radius for N1/TiO2/rGO is noticeably smaller than the undoped TiO2/rGO composite (TiO2/rGO weight ratio equal to unity). This is due to the presence of N in both TiO2 nanoparticles [10] and carbon support [59].
On the contrary, N1/TiO2/CNT nanocomposite exhibits larger arc radius (higher resistance for charge transfer and lower charge separation efficiency) than the undoped TiO2/CNT composite. This behavior has already been explained in previous sections in terms of smaller crystallite size and may be due to the presence of N in the bulk but not on the surface of the N-doped TiO2/CNT composite.
Moreover, the order of increasing the arc radius almost fully matches with the order of catalysts according to their decreasing photocatalytic activity: N1/TiO2/rGO = TiO2/CNT > TiO2/rGO > N1/TiO2 > N1/TiO2/CNT > TiO2.
3.10. Summary of Properties
In this section, the different properties exhibited by the N-doped catalysts synthesized in supercritical medium will be summarized and compared with those of catalysts synthesized by traditional methods, as well as those obtained with supercritical fluids but not doped with N.
Generally speaking, N-doped TiO2 nanoparticles obtained with supercritical fluids in this work exhibited an improved photocatalytic activity in terms of both total conversion and methane selectivity than those obtained with traditional methods [29]. This enhanced behavior seems to be derived from a lower degree of aggregation [2], larger crystallite size [2] and slightly higher visible light absorption [2]. Regarding N-doped TiO2/carbon support composites synthesized in supercritical medium, only N-doped TiO2/rGO composites have shown higher photocatalytic activity (but not methane selectivity) than similar composites synthesized with traditional methods [30]. In this case, the main reason is undoubtedly the extraordinarily good ability of the composites obtained in this work to absorb visible light compared to conventional N-doped TiO2/rGO materials [39]. The poorer photocatalytic activity of N-doped TiO2/CNT composites seems to be derived from the smaller crystallite size [32] and BET area [34] of the materials obtained in this work, in contrast to those synthesized with traditional methods.
In the case of the photocatalysts obtained in a supercritical medium by our group in previous studies, the main advantage of the materials described in this work is that N-doping allowed the photocatalytic activity shown by metal-doped catalysts to be maintained, with consequent saving of more expensive raw materials (Cu, Pd, Pt). Even in the case of N-doped TiO2 nanoparticles, methane selectivity was doubled in contrast to undoped [36] and metal-doped nanoparticles [60], probably due to the larger crystallite size of the first ones. Something similar was observed for N-doped TiO2/rGO composites, although methane selectivity of metal-doped TiO2/rGO composites was not improved [9]. N-doped TiO2/rGO composites exhibited higher BET area and lower band gap energy, but smaller crystallite size than metal-doped TiO2/rGO composites [9]. Finally, N-doped TiO2/CNT composites showed lower photocatalytic activity than undoped and metal-doped TiO2/CNT composites [8]. In this case, the small crystallite size seems to hinder its excellent properties related to visible light absorption [8]. Moreover, XPS analysis suggested that N incorporation took place mainly in the bulk, but not on the surface, in N-doped TiO2/CNT composites, as the N-containing active sites were less accessible [27].
4. Conclusions
N-doped TiO2 nanoparticles, N-doped TiO2/CNT and N-doped TiO2/rGO nanocomposites were synthesized by a facile one-pot method in a supercritical medium. The presence of N in both TiO2 and carbon supports endowed them with good visible light sensitization and high separation efficiency of the charges photogenerated after irradiation with solar light. The photocatalysts exhibited good photocatalytic performance in photoreduction of CO2 in the presence of water vapor and the highest conversion rate of 8 µmol/gTiO2/h was achieved with N1/TiO2/rGO composite. The photocatalytic products depended on the catalyst type. CO and CH4 were formed on N-doped TiO2 nanoparticles (CH4/CO ratio 2.5), while almost only CO was produced on both composites (N-doped TiO2 on CNT or rGO) as a result of a lack of H· radicals coming from H2O oxidation. The specific N content of the catalysts could be regulated by varying the N precursor, leading urea to higher N levels in the catalysts than TEA. Nevertheless, similar properties and even lower photocatalytic activity were exhibited by the composites with higher N percentage (N2/TiO2/rGO and N2/TiO2/CNT).
To sum up, in the present work the effect of the carbon support (CNT and rGO) on the activity and selectivity of the N-doped TiO2 nanoparticles in the CO2 photocatalytic reduction reaction was evaluated. Specifically, it was found that maximum CO2 conversion was achieved with the rGO support (N1/TiO2/rGO (b)). It almost doubled that obtained when using CNT (N1/TiO2/CNT (b)). However, no differences in selectivity were achieved with both carbon supports.
The results regarding N-doped nanoparticles and N-TiO2/rGO nanocomposites are of special interest, especially in terms of methane selectivity and total conversion, respectively. Nevertheless, as a promising avenue for future research, we may suggest the modification of N-doped TiO2-based photocatalysts investigated in this work with an additional metallic dopant. The interesting results reported in studies of charge generation and transfer conducted with metal-doped TiO2 support this hypothesis.
Conceptualization, J.R. and R.C.; methodology, J.R. and R.C.; validation, J.R. and R.C.; formal analysis, J.R., R.C. and V.R.; investigation, V.R. and Ó.R.A.; data curation, V.R. and Ó.R.A.; writing-original draft preparation, J.R. and R.C.; writing-review and editing, J.R., R.C.; F.M. and C.J.; visualization, J.R. and R.C.; supervision, J.R. and R.C.; project administration, J.R.; funding acquisition, J.R., R.C., F.M., C.J., V.R. and Ó.R.A. All authors have read and agreed to the published version of the manuscript.
Not applicable.
Not applicable.
Not applicable.
The authors declare no conflict of interest.
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Figure 1. Photocatalytic production rates of different synthesized N-doped photocatalysts.
Figure 2. Photocatalytic mechanism: (a) N–doped TiO2 nanoparticles, (b) N–doped TiO2/carbon support composites.
Figure 3. TEM images of different synthesized materials: (a) N1/TiO2, (b) N2/CNT, (c) N10/rGO, (d) N1/TiO2/CNT, (e) N1/TiO2/rGO.
Figure 4. XRD diffractograms of different synthesized N-doped photocatalysts and supports.
Figure 5. FTIR spectra of different synthesized N–doped TiO2–based photocatalysts and supports.
Figure 6. Full scan XPS spectra of some synthesized N-doped TiO2-based photocatalysts and supports.
Figure 7. Narrow scan XPS spectra of Ti 2p of different synthesized N–doped TiO2–based photocatalysts.
Figure 8. Narrow scan XPS spectra of O 1s of different synthesized materials: (a) N4/TiO2/rGO, (b) N10/rGO.
Figure 9. Narrow scan XPS spectra of C 1s of different synthesized photocatalysts and supports: (a) N1/TiO2/CNT, (b) N10/rGO, (c) N1/TiO2/rGO.
Figure 10. Narrow scan XPS spectra of N 1s of different synthesized photocatalysts and supports: (a) N1/TiO2/CNT, (b) N10/rGO.
Figure 11. DRS spectra of different synthesized N-doped TiO2-based photocatalysts and supports.
Figure 12. Electrochemical impedance spectra: (a) TiO2 nanoparticles and N-doped TiO2 nanoparticles, (b) TiO2/CNT, N-doped TiO2/CNT, TiO2/rGO and N-doped TiO2/rGO composites.
Figure 12. Electrochemical impedance spectra: (a) TiO2 nanoparticles and N-doped TiO2 nanoparticles, (b) TiO2/CNT, N-doped TiO2/CNT, TiO2/rGO and N-doped TiO2/rGO composites.
N content of the different N-doped supports.
Support | Nitrogen Precursor |
N Content |
Material Name (1) |
---|---|---|---|
CNT | 1 mL TEA |
1.0 |
N1/CNT |
rGO | 1 mL TEA |
4.1 |
N4/rGO |
(1): NX/CNT or NX/rGO are materials names, where X is N content in mg N/g carbon support. (a), (b) and (c) are employed to differentiate materials with the same N content.
N content of the different N-doped photocatalysts.
Photocatalyst | Nitrogen Precursor Used in the Synthesis | N Content (Measured by Elemental Analysis) |
N Content (Measured or Estimated) |
Photocatalyst Name (1) |
---|---|---|---|---|
N-doped TiO2 nanoparticles | 1 mL TEA |
1.1 |
1.1 |
N1/TiO2 (a) |
N-doped TiO2 nanoparticles supported on CNT | 1 mL TEA |
1.0 |
1 |
N1/TiO2/CNT (a) |
N-doped TiO2 nanoparticles supported on rGO | 1 mL TEA |
2.6 |
1 |
N1/TiO2/rGO (a) |
(1): NX/TiO2, NX/TiO2/CNT and NX/TiO2/rGO are material names, where X is N content in mg N/g TiO2. (a), (b) and (c) are employed to differentiate materials with the same N content.
Photocatalytic production rates of CO and hydrocarbons with N-doped TiO2-based photocatalysts reported in the bibliography.
Catalyst | Products |
Conditions | Reference |
---|---|---|---|
N1/TiO2 | CO: 1.5 |
See Materials and methods | This work |
5 wt. % N-TiO2 |
CO: 0 |
6 fluorescent bulbs (400–800 nm), 13 W, continuous flow stirred slurry reactor, 250 mL, 10 mL/min, catalyst concentration 1 g/L, 6 h | [ |
N-TiO2 |
CO: 0.1 |
Continuous, catalyst 100–300 mg, CO2:H2O = 30:1, CO2 flow 0.3 mL/min, Xe lamp (315–600 nm), irradiation area 1.08 × 10−3 m2 | [ |
N1/TiO2/CNT | CO: 3.9 |
See Materials and methods | This work |
N1/TiO2/rGO | CO: 7.5 |
See Materials and methods | This work |
N-TiO2/graphene (gas phase) | CO: 0 |
Continuous gas flow reactor, visible light irradiation (15 W), 10 h, CO2 flow 5 mL/min | [ |
g-C3N4-N-TiO2 |
CO: 4.8 |
Gas-closed circulation system, 780 mL, 0.1 g catalyst, 300 W Xe arc lamp | [ |
Tr: Traces. The gray background represents the same type of catalysts.
Results of the characterization of different N-doped TiO2-based photocatalysts and supports.
Samples | N Content |
TiO2 Crystallite Size (nm) | BET Area (m2/g) | Band Gap (eV) | Absorption Threshold (nm) |
---|---|---|---|---|---|
TiO2 | 0 | 11 | 152 | 3.10 | 400 |
N1/TiO2 | 1 | 14 | 82 | 3.06 | 405 |
N2/TiO2 | 2 | 14 | 81 | 3.06 | 405 |
CNT | 0 | - | 216 | - | - |
N1/CNT | 1 mg N/g CNT | - | 284 | - | - |
N2/CNT | 2 mg N/g CNT | - | 280 | - | - |
N1/TiO2/CNT | 1 | 10 | 145 | 2.12 | - |
N2/TiO2/CNT | 2 | 10 | 140 | 2.10 | - |
rGO | 0 | - | 163 | - | - |
N4/rGO | 4 mg N/g rGO | - | 173 | - | - |
N10/rGO | 10 mg N/g rGO | - | 171 | - | - |
N1/TiO2/rGO | 1 | 14 | 85 | 2.45 | - |
N2/TiO2/rGO | 2 | 13 | 84 | 2.40 | - |
The gray background represents the same type of materials.
Supplementary Materials
The following supporting information can be downloaded at:
References
1. Yaqoob, A.A.; Mohd Noor, N.H.; Serrà, A.; Ibrahim, M.N.M. Advances and Challenges in Developing Efficient Graphene Oxide-Based ZnO Photocatalysts for Dye Photo-Oxidation. Nanomaterials; 2020; 10, 932. [DOI: https://dx.doi.org/10.3390/nano10050932] [PubMed: https://www.ncbi.nlm.nih.gov/pubmed/32408530]
2. Phongamwong, T.; Chareopanich, M.; Limtrakul, J. Role of chlorophyll in Spirulina on photocatalytic activity of CO2 reduction under visible light over modified N-doped TiO2 photocatalysts. Appl. Catal. B-Environ.; 2015; 168–169, pp. 114-124. [DOI: https://dx.doi.org/10.1016/j.apcatb.2014.12.022]
3. Camarillo, R.; Rincón, J. Photocatalytic discoloration of dyes: Relation between effect of operating parameters and dye structure. Chem. Eng. Technol.; 2011; 34, pp. 1675-1684. [DOI: https://dx.doi.org/10.1002/ceat.201100063]
4. Yaqoob, A.A.; Ahmad, A.; Ibrahim, M.N.M.; Karri, R.R.; Rashid, M.; Ahamd, Z. Chapter 23—Synthesis of metal oxide–based nanocomposites for energy storage application. Micro and Nano Technologies, Sustainable Nanotechnology for Environmental Remediation; Koduru, J.R.; Karri, R.R.; Mubarak, N.M.; Bandala, E.R. Elsevier: Amsterdam, The Netherlands, 2022; pp. 611-635.
5. Divyasri, Y.V.; Reddy, N.L.; Lee, K.; Sakar, M.; Rao, V.N.; Venkatramu, V.; Shankar, M.V.; Reddy, N.C.G. Optimization of N doping in TiO2 nanotubes for the enhanced solar light mediated photocatalytic H2 production and dye degradation. Environ. Pollut.; 2021; 269, 116170. [DOI: https://dx.doi.org/10.1016/j.envpol.2020.116170]
6. Tostón, S.; Camarillo, R.; Martínez, F.; Jiménez, C.; Rincón, J. Supercritical synthesis of planitum-modified titanium dioxide for solar fuel production from carbon dioxide. Chin. J. Catal.; 2017; 38, pp. 636-650. [DOI: https://dx.doi.org/10.1016/S1872-2067(17)62766-9]
7. Camarillo, R.; Rizaldos, D.; Jiménez, C.; Martínez, F.; Rincón, J. Enhancing the photocatalytic reduction of CO2 with undoped and Cu-doped TiO2 nanofibers synthesized in supercritical medium. J. Supercrit. Fluids; 2019; 147, pp. 70-80. [DOI: https://dx.doi.org/10.1016/j.supflu.2019.02.013]
8. Rodríguez, V.; Camarillo, R.; Martínez, F.; Jiménez, C.; Rincón, J. CO2 photocatalytic reduction with CNT/TiO2 based nanocomposites prepared by high-pressure technology. J. Supercrit. Fluids; 2020; 163, 104876. [DOI: https://dx.doi.org/10.1016/j.supflu.2020.104876]
9. Rodríguez, V.; Camarillo, R.; Martínez, F.; Jiménez, C.; Rincón, J. High-pressure synthesis of rGO/TiO2 and rGO/TiO2/Cu catalysts for efficient CO2 reduction under solar light. J. Supercrit. Fluids; 2021; 174, 105265. [DOI: https://dx.doi.org/10.1016/j.supflu.2021.105265]
10. Wu, D.; Guo, J.; Wang, H.; Zhang, X.; Yang, Y.; Yang, C.; Gao, Z.; Wang, Z.; Jiang, K. Green synthesis of boron and nitrogen co-doped TiO2 with rich B-N motifs as Lewis acid-base couples for the effective artificial CO2 photoreduction under simulated sunlight. J. Colloid Interf. Sci.; 2021; 585, pp. 95-107. [DOI: https://dx.doi.org/10.1016/j.jcis.2020.11.075]
11. Yaqoob, A.A.; Ibrahim, M.N.M.; Ahmad, A.; Reddy, A.V.B. Toxicology and Environmental Application of Carbon Nanocomposite. Environmental Remediation through Carbon Based Nano Composites; Springer: Berlin/Heidelberg, Germany, 2021; pp. 1-18.
12. De la Flor, M.P.; Camarillo, R.; Martínez, F.; Jiménez, C.; Quiles, R.; Rincón, J. Removal of emerging pollutant dibutylhydroxytoluene from water with CNT/TiO2 catalysts in a visible LED photoreactor. Environ. Sci. Pollut. Res.; 2021; 28, pp. 23720-23730. [DOI: https://dx.doi.org/10.1007/s11356-020-11126-y]
13. Kuvarega, A.T.; Krause, R.W.M.; Mamba, B.B. Multiwalled carbon nanotubes decorated with nitrogen, palladium co-doped TiO2 (MWCNT/N, Pd co-doped TiO2) for visible light photocatalytic degradation of Eosin Yellow in water. J. Nanopart. Res.; 2012; 14, 776. [DOI: https://dx.doi.org/10.1007/s11051-012-0776-x]
14. Zhang, Y.; Yang, H.M.; Park, S.-J. Synthesis and characterization of nitrogen-doped TiO2 coatings on reduced graphene oxide for enhancing the visible light photocatalytic activity. Curr. Appl. Phys.; 2018; 18, pp. 163-169. [DOI: https://dx.doi.org/10.1016/j.cap.2017.12.001]
15. De la Flor, M.P.; Camarillo, R.; Martínez, F.; Jiménez, C.; Quiles, R.; Rincón, J. Synthesis and characterization of bimetallic TiO2/CNT/Pd-Cu for efficient remediation of endocrine disruptors under solar light. J. Environ. Chem. Eng.; 2022; 10, 107245. [DOI: https://dx.doi.org/10.1016/j.jece.2022.107245]
16. Bramhaiah, K.; Bhattacharyya, S. Challenges and future prospects of graphene-based hybrids for solar fuel generation: Moving towards next generation photocatalysts. Mater. Adv.; 2022; 3, pp. 142-172. [DOI: https://dx.doi.org/10.1039/D1MA00748C]
17. Li, J.; Hou, X.; Sun, T.; Han, J.; Liu, H.; Li, D. Hydrophilic, antibacterial and photocatalytic properties of TiO2 composite films modified by the methods of N+ ion implantation and doping of CNTs. Surf. Coat. Technol.; 2019; 365, pp. 123-128. [DOI: https://dx.doi.org/10.1016/j.surfcoat.2018.07.063]
18. Rengifo-Herrera, J.A.; Osorio-Vargas, P.; Pulgarin, C.A. A critical review on N-modified TiO2 limits to treat chemical and biological contaminants in water. Evidence that enhanced visible light absorption does not lead to higher degradation rates under whole solar light. J. Hazard. Mater.; 2022; 425, 127979. [DOI: https://dx.doi.org/10.1016/j.jhazmat.2021.127979]
19. Lee, W.J.; Lee, J.M.; Kochuveedu, S.T.; Han, T.H.; Jeong, H.Y.; Park, M.; Yun, J.M.; Kwon, J.; No, K.; Kim, D.H. et al. Biomineralized N-doped CNT/TiO2 core/shell nanowires for visible light photocatalysis. ACS Nano; 2012; 6, pp. 935-943. [DOI: https://dx.doi.org/10.1021/nn204504h]
20. Lucky, R.A.; Charpentier, P.A. N-doped ZrO2/TiO2 bimetallic materials synthesized in supercritical CO2: Morphology and photocatalytic activity. Appl. Catal. B-Environ.; 2010; 96, pp. 516-523. [DOI: https://dx.doi.org/10.1016/j.apcatb.2010.03.013]
21. Rincón, J.; Martínez, F.; Rodríguez, L.; Ancillo, V. Recovery of triglycerides from used frying oil by extraction with liquid and supercritical ethane. J. Supercrit. Fluids; 2011; 56, pp. 72-79. [DOI: https://dx.doi.org/10.1016/j.supflu.2010.11.010]
22. Mumin, M.A.; Moula, G.; Charpentier, P.A. Supercritical CO2 synthesized TiO2 nanowires covalently linked with core-shell CdS-ZnS quantum dots: Enhanced photocatalysis and stability. RSC Adv.; 2015; 5, pp. 67767-67779. [DOI: https://dx.doi.org/10.1039/C5RA08914J]
23. de la Flor, M.P.; Camarillo, R.; Martínez, F.; Jiménez, C.; Quiles, R.; Rincón, J. Synthesis and characterization of TiO2/CNT/Pd: An effective sunlight photocatalyst for neonicotinoids degradation. J. Environ. Chem. Eng.; 2021; 9, 106278. [DOI: https://dx.doi.org/10.1016/j.jece.2021.106278]
24. Camarillo, R.; Tostón, S.; Martínez, F.; Jiménez, C.; Rincón, J. Enhancing the photocatalytic reduction of CO2 through engineering of catalyst with high pressure technology: Pd/TiO2 photocatalysts. J. Supercrit. Fluids; 2017; 123, pp. 18-27. [DOI: https://dx.doi.org/10.1016/j.supflu.2016.12.010]
25. Ananpattarachai, J.; Kajitvivhyanukul, P.; Seraphin, S. Visible light absorption ability and photocatalytic oxidation activity of various interstitial N-doped TiO2 prepared from different nitrogen dopants. J. Hazard. Mater.; 2009; 168, pp. 253-261. [DOI: https://dx.doi.org/10.1016/j.jhazmat.2009.02.036] [PubMed: https://www.ncbi.nlm.nih.gov/pubmed/19282105]
26. Senthilnathan, J.; Philip, L. Photocatalytic degradation of lindane under UV and visible light using N-doped TiO2. Chem. Eng. J.; 2010; 161, pp. 83-92. [DOI: https://dx.doi.org/10.1016/j.cej.2010.04.034]
27. Cong, Y.; Zhang, J.; Chen, F.; Anpo, M. Synthesis and characterization of nitrogen-doped TiO2 nanophotocatalyst with high visible light activity. J. Phys. Chem.; 2007; 111, pp. 6976-6982. [DOI: https://dx.doi.org/10.1021/jp0685030]
28. Fu, J.; Jiang, K.; Qiu, X.; Yu, J.; Liu, M. Production selectivity of photocatalytic CO2 reduction reactions. Mater. Today; 2020; 32, pp. 222-243. [DOI: https://dx.doi.org/10.1016/j.mattod.2019.06.009]
29. Bjelajac, A.; Kopac, D.; Fecant, A.; Tavernier, E.; Petrovic, R.; Lizokar, B.; Janackovic, D. Micro-kinetic modelling of photocatalytic CO2 reduction over undoped and N-doped TiO2. Catal. Sci. Technol.; 2020; 10, pp. 1688-1698. [DOI: https://dx.doi.org/10.1039/C9CY02443C]
30. Ong, W.-J.; Tan, L.-L.; Chai, S.-P.; Yong, S.-T.; Mohamed, A.R. Self-assembly of nitrogen-doped TiO2 with exposed {001} facets on a graphene scaffold as photo-active hybrid nanostructures for reduction of carbon dioxide to methane. Nano Res.; 2014; 7, pp. 1528-1547. [DOI: https://dx.doi.org/10.1007/s12274-014-0514-z]
31. Zhou, S.; Liu, Y.; Li, J.; Wang, Y.; Jiang, G.; Zhao, Z.; Wang, D.; Duan, A.; Liu, J.; Wei, Y. Facile in situ synthesis of graphitic carbon nitride (g-C3N4)-N-TiO2 heterojunction as an efficient photocatalyst for the selective photoreduction of CO2 to CO. Appl. Catal. B-Environ.; 2014; 158–159, pp. 20-29. [DOI: https://dx.doi.org/10.1016/j.apcatb.2014.03.037]
32. Belkhanchi, H.; Ziat, Y.; Hammi, M.; Laghlimi, C.; Moutcine, A.; Benyounes, A.; Kzaiber, F. Nitrogen doped carbon nanotubes grafted TiO2 rutile nanofilms: Promising material for dye sensitized solar cell application. Optik; 2021; 239, 166234. [DOI: https://dx.doi.org/10.1016/j.ijleo.2020.166234]
33. Mou, Z.; Wu, Y.; Sun, J.; Yang, P.; Du, Y.; Lu, C. TiO2 nanoparticles-functionalized N-doped graphene with superior interfacial contact and enhanced charge separation for photocatalytic hydrogen generation. ACS Appl. Mater. Interfaces; 2014; 6, pp. 13798-13806. [DOI: https://dx.doi.org/10.1021/am503244w]
34. Daraee, M.; Ghasemy, E.; Rashidi, A. Effective absorption of hydrogen sulfide by intercalation of TiO2 and N-doped TiO2 in graphene oxide. J. Environ. Chem. Eng.; 2020; 8, 103836. [DOI: https://dx.doi.org/10.1016/j.jece.2020.103836]
35. Hou, X.; Yao, K.; Wang, X.; Li, D.; Liao, B. Enhanced superhydrophilicity of N+ implanted multiwalled carbon nanotubes-TiO2 composite thin films. Vacuum; 2014; 100, pp. 74-77. [DOI: https://dx.doi.org/10.1016/j.vacuum.2013.06.009]
36. Camarillo, R.; Tostón, S.; Martínez, F.; Jiménez, C.; Rincón, J. Preparation of TiO2-based catalysts with supercritical fluid technology: Characterization and photocatalytic activity in CO2 reduction. J. Chem. Technol. Biotechnol.; 2017; 92, pp. 1710-1720. [DOI: https://dx.doi.org/10.1002/jctb.5169]
37. Yang, G.; Jiang, Z.; Shi, H.; Xiao, T.; Yan, Z. Preparation of highly visible-light active N-doped TiO2 photocatalyst. J. Mater. Chem.; 2010; 20, pp. 5301-5309. [DOI: https://dx.doi.org/10.1039/c0jm00376j]
38. Ji, L.; Zhou, S.; Liu, X.; Gong, M.; Xu, T. Synthesis of carbon- and nitrogen-doped TiO2/carbon composite fibers by a surface-hydrolyzed PAN fiber and their photocatalytic property. J. Mater. Sci.; 2020; 55, pp. 2471-2481. [DOI: https://dx.doi.org/10.1007/s10853-019-04109-z]
39. Gao, N.; Wan, T.; Xu, Z.; Ma, L.; Ramakrishna, S.; Liu, Y. Nitrogen doped TiO2/graphene nanofibers as DSSCs photoanode. Mater. Chem. Phys.; 2020; 255, 123542. [DOI: https://dx.doi.org/10.1016/j.matchemphys.2020.123542]
40. Yadav, V.; Saini, V.K.; Sahrma, H. How different dopants leads to difference in photocatalytic activity in doped TiO2?. Ceram. Internat.; 2020; 46, pp. 27308-27317. [DOI: https://dx.doi.org/10.1016/j.ceramint.2020.07.216]
41. Masa, J.; Bordoloi, A.; Muhler, M.; Schuhmann, W.; Xia, W. Enhanced electrocatalytic stability of platinum nanoparticles supported on a nitrogen-doped composite of carbon nanotubes and mesoporous titania under oxygen reduction conditions. ChemSusChem; 2012; 5, pp. 523-525. [DOI: https://dx.doi.org/10.1002/cssc.201100643]
42. Zikalala, S.A.; Selvaraj, R.; Al Marzouqi, F.; Kuvarega, A.T.; Mamba, B.B.; Mhlanga, S.D.; Nxumalo, E.N. Tailoring TiO2 through N doping and incorporation of amorphous carbon nanotubes via a microwave-assisted hydrothermal method. J. Environ. Chem. Eng.; 2020; 8, 104082. [DOI: https://dx.doi.org/10.1016/j.jece.2020.104082]
43. Carreño-Lizcano, M.I.; Guarldrón-Reyes, A.F.; Rodríguez-González, V.; Pedraza-Avella, J.A.; Niño-Gómez, M.E. Photoelectrocatalytic phenol oxidation employing nitrogen doped TiO2-rGO films as photoanodes. Catal. Today; 2020; 341, pp. 96-103. [DOI: https://dx.doi.org/10.1016/j.cattod.2019.02.006]
44. Tan, L.L.; Ong, W.J.; Chai, S.P.; Mohamed, A.R. Reduced graphene oxide-TiO2 nanocomposite as a promising visible light-active photocatalyst for the conversion of carbon dioxide. Nanoscale Res. Lett.; 2013; 8, pp. 465-473. [DOI: https://dx.doi.org/10.1186/1556-276X-8-465] [PubMed: https://www.ncbi.nlm.nih.gov/pubmed/24195721]
45. Khalid, N.R.; Ahmed, E.; Hong, Z.; Zhang, Y.; Ahmad, M. Nitrogen doped TiO2 nanoparticles decorated on graphene sheets for photocatalysis applications. Curr. Appl. Phys.; 2012; 12, pp. 1485-1492. [DOI: https://dx.doi.org/10.1016/j.cap.2012.04.019]
46. Ida, S.; Wilson, P.; Neppolian, B.; Sathish, M.; Mahammed Shanheer, A.R.; Ravi, P. Turning the type of nitrogen on N-RGO supported on N-TiO2 under ultrasonication/hydrothermal treatment for efficient hydrogen evolution—A mechanistic overview. Ultrason. Sonochem.; 2020; 64, 104866. [DOI: https://dx.doi.org/10.1016/j.ultsonch.2019.104866]
47. Shehzad, N.; Tahir, M.; Johari, K.; Murgesan, T.; Hussain, M. Improved interfacial bonding of graphene-TiO2 with enhanced photocatalytic reduction of CO2 into solar fuel. J. Environ. Chem. Eng.; 2018; 6, pp. 6947-6957. [DOI: https://dx.doi.org/10.1016/j.jece.2018.10.065]
48. Cao, G.; Aaron Deskins, N.; Yi, N. Carbon monoxide oxidation over copper and nitrogen modified titanium dioxide. Appl. Catal. B-Environ.; 2021; 285, 119748. [DOI: https://dx.doi.org/10.1016/j.apcatb.2020.119748]
49. Nada, A.A.; El Rouby, W.M.A.; Bekheet, M.F.; Antuch, M.; Weber, M.; Miele, P.; Viter, R.; Roualdes, S.; Millet, P.; Bechelany, M. Highly textured boron/nitrogen co-doped TiO2 with honeycomb structure showing enhanced visible-light photoelectrocatalytic activity. Appl. Surf. Sci.; 2020; 505, 144419. [DOI: https://dx.doi.org/10.1016/j.apsusc.2019.144419]
50. Thirugnanam, L.; Palanisamy, M.; Kavery, S.; Ramaprabhu, S.; Pol, V.G.; Dutta, M. TiO2 nanoparticle embedded nitrogen doped electrospun helical carbon nanofiber-carbon nanotube hybrid anode for lithium-ion batteries. Int. J. Hydrogen Energy; 2021; 46, pp. 2464-2478. [DOI: https://dx.doi.org/10.1016/j.ijhydene.2020.10.149]
51. Han, Z.; Peng, J.; Liu, L.; Wang, G.; Yu, F.; Guo, X. Few-layer TiO2-B nanosheets with N-doped graphene nanosheets as a highly robust anode for lithium-ion batteries. RSC Adv.; 2017; 7, pp. 7864-7869. [DOI: https://dx.doi.org/10.1039/C6RA26929J]
52. Wang, J.; Tafen, D.N.; Lewis, J.P.; Hong, Z.; Manivannan, A.; Zhi, M.; Li, M.; Wu, N. Origin of photocatalytic activity of nitrogen-doped TiO2 nanobelts. J. Am. Chem. Soc.; 2009; 131, pp. 12290-12297. [DOI: https://dx.doi.org/10.1021/ja903781h]
53. Kaur, N.; Shani, S.K.; Shani, J.S.; Sandhu, S.; Sharma, R.; Singh, V. Comprehensive review and future perspectives of efficient N-doped, Fe-doped and (N,Fe)-co-doped titania as visible light active photocatalysts. Vacuum; 2020; 178, 109429. [DOI: https://dx.doi.org/10.1016/j.vacuum.2020.109429]
54. Sathish, M.; Viswanathan, B.; Viswanath, R.P.; Gopinath, C.S. Synthesis, characterization, electronic structure, and photocatalytic activity of nitrogen-doped TiO2 nanocatalyst. Chem. Mater.; 2005; 17, pp. 6349-6353. [DOI: https://dx.doi.org/10.1021/cm052047v]
55. Song, J.; Wang, X.; Huang, J.; Ma, J.; Wang, X.; Wang, H.; Ma, R.; Xia, P.; Zhao, J. High performance of N-doped TiO2-magnetic activated carbon composites under visible light illumination: Synthesis and application in three-dimensional photoelectrochemical process. Electrochim. Acta; 2016; 222, pp. 1-11. [DOI: https://dx.doi.org/10.1016/j.electacta.2016.11.011]
56. Wang, D.-H.; Jia, L.; Wu, X.-L.; Lu, L.-Q.; Xu, A.-W. One-step hydrothermal synthesis of N-doped TiO2/C nanocomposites with high visible light photocatalytic activity. Nanoscale; 2012; 4, pp. 576-584. [DOI: https://dx.doi.org/10.1039/C1NR11353D]
57. Tan, D.; Zhang, J.; Shi, J.; Li, S.; Zhang, B.; Tan, X.; Zhang, F.; Liu, L.; Shao, D.; Han, B. Photocatalytic CO2 transformation to CH4 by Ag/Pd bimetals supported on N-doped TiO2 nanosheet. ACS Appl. Mater. Interfaces; 2018; 10, pp. 24516-24522. [DOI: https://dx.doi.org/10.1021/acsami.8b06320]
58. Lei, Z.; Xiong, Z.; Wang, Y.; Chen, Y.; Cao, S.; Zhao, Y.; Zhang, J.; Zheng, C. Photocatalytic reduction of CO2 over facet engineered TiO2 nanocrystals supported by carbon nanofibers under simulated sunlight irradiation. Catal. Commun.; 2018; 108, pp. 27-32. [DOI: https://dx.doi.org/10.1016/j.catcom.2018.01.025]
59. Min, Y.; He, G.; Li, R.; Zhao, W.; Chen, Y.; Zhang, Y. Doping nitrogen anion enhanced photocatalytic activity on TiO2 hybridized with graphene composite under solar light. Sep. Purif. Technol.; 2013; 106, pp. 97-104. [DOI: https://dx.doi.org/10.1016/j.seppur.2012.12.023]
60. Camarillo, R.; Tostón, S.; Martínez, F.; Jiménez, C.; Rincón, J. Improving the photo-reduction of CO2 to fuels with catalysts synthesized under high pressure: Cu/TiO2. J. Chem. Technol. Biotechnol.; 2018; 93, pp. 1237-1248. [DOI: https://dx.doi.org/10.1002/jctb.5477]
You have requested "on-the-fly" machine translation of selected content from our databases. This functionality is provided solely for your convenience and is in no way intended to replace human translation. Show full disclaimer
Neither ProQuest nor its licensors make any representations or warranties with respect to the translations. The translations are automatically generated "AS IS" and "AS AVAILABLE" and are not retained in our systems. PROQUEST AND ITS LICENSORS SPECIFICALLY DISCLAIM ANY AND ALL EXPRESS OR IMPLIED WARRANTIES, INCLUDING WITHOUT LIMITATION, ANY WARRANTIES FOR AVAILABILITY, ACCURACY, TIMELINESS, COMPLETENESS, NON-INFRINGMENT, MERCHANTABILITY OR FITNESS FOR A PARTICULAR PURPOSE. Your use of the translations is subject to all use restrictions contained in your Electronic Products License Agreement and by using the translation functionality you agree to forgo any and all claims against ProQuest or its licensors for your use of the translation functionality and any output derived there from. Hide full disclaimer
© 2022 by the authors. Licensee MDPI, Basel, Switzerland. This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license (https://creativecommons.org/licenses/by/4.0/). Notwithstanding the ProQuest Terms and Conditions, you may use this content in accordance with the terms of the License.
Abstract
The objective of this work was to analyze the effect of carbon support on the activity and selectivity of N-doped TiO2 nanoparticles. Thus, N-doped TiO2 and two types of composites, N-doped TiO2/CNT and N-doped TiO2/rGO, were prepared by a new environmentally friendly one-pot method. CNT and rGO were used as supports, triethylamine and urea as N doping agents, and titanium (IV) tetraisopropoxide and ethanol as Ti precursor and hydrolysis agent, respectively. The as-prepared photocatalysts exhibited enhanced photocatalytic performance compared to TiO2 P25 commercial catalyst during the photoreduction of CO2 with water vapor. It was imputed to the synergistic effect of N doping (reduction of semiconductor band gap energy) and carbon support (enlarging e−-h+ recombination time). The activity and selectivity of catalysts varied depending on the investigated material. Thus, whereas N-doped TiO2 nanoparticles led to a gaseous mixture, where CH4 formed the majority compared to CO, N-doped TiO2/CNT and N-doped TiO2/rGO composites almost exclusively generated CO. Regarding the activity of the catalysts, the highest production rates of CO (8 µmol/gTiO2/h) and CH4 (4 µmol/gTiO2/h) were achieved with composite N1/TiO2/rGO and N1/TiO2 nanoparticles, respectively, where superscript represents the ratio mg N/g TiO2. These rates are four times and almost forty times higher than the CO and CH4 production rates observed with commercial TiO2 P25.
You have requested "on-the-fly" machine translation of selected content from our databases. This functionality is provided solely for your convenience and is in no way intended to replace human translation. Show full disclaimer
Neither ProQuest nor its licensors make any representations or warranties with respect to the translations. The translations are automatically generated "AS IS" and "AS AVAILABLE" and are not retained in our systems. PROQUEST AND ITS LICENSORS SPECIFICALLY DISCLAIM ANY AND ALL EXPRESS OR IMPLIED WARRANTIES, INCLUDING WITHOUT LIMITATION, ANY WARRANTIES FOR AVAILABILITY, ACCURACY, TIMELINESS, COMPLETENESS, NON-INFRINGMENT, MERCHANTABILITY OR FITNESS FOR A PARTICULAR PURPOSE. Your use of the translations is subject to all use restrictions contained in your Electronic Products License Agreement and by using the translation functionality you agree to forgo any and all claims against ProQuest or its licensors for your use of the translation functionality and any output derived there from. Hide full disclaimer