Abstract
Photocatalytic conversion of CO2 into solar fuels has gained increasing attention due to its great potential for alleviating the energy and environmental crisis at the same time. The low-cost TiO2 with suitable band structure and high resistibility to light corrosion has proven to be very promising for photoreduction of CO2 using water as the source of electrons and protons. However, the narrow spectral response range (ultraviolet region only) as well as the rapid recombination of photo-induced electron-hole pairs within pristine TiO2 results in the low utilization of solar energy and limited photocatalytic efficiency. Besides, its low selectivity toward photoreduction products of CO2 should also be improved. Combination of TiO2 with other photoelectric active materials, such as metal oxide/sulfide semiconductors, metal nanoparticles and carbon-based nanostructures, for the construction of well-defined heterostructures can enhance the quantum efficiency significantly by promoting visible light adsorption, facilitating charge transfer and suppressing the recombination of charge carriers, resulting in the enhanced photocatalytic performance of the composite photocatalytic system. In addition, the adsorption and activation of CO2 on these heterojunctions are also promoted, therefore enhancing the turnover frequency (TOF) of CO2 molecules, so as to the improved selectivity of photoreduction products. This review focus on the recent advances of photocatalytic CO2 reduction via TiO2-based heterojunctions with water oxidation. The rational design, fabrication, photocatalytic performance and CO2 photoreduction mechanisms of typical TiO2-based heterojunctions, including semiconductor-semiconductor (S-S), semiconductor-metal (S-M), semiconductor-carbon group (S-C) and multicomponent heterojunction are reviewed and discussed. Moreover, the TiO2-based phase heterojunction and facet heterojunction are also summarized and analyzed. In the end, the current challenges and future prospects of the TiO2-based heterostructures for photoreduction of CO2 with high efficiency, even for practical application are discussed.
Introduction
Energy and environmental crizes are two major bottlenecks restricting the sustainable development of human society. For a long time, the excessive consumption of fossil fuels has caused severe energy shortages, and the CO2 released during the combustion process has become the main factor leading to global warming (Stott et al., 2000; Meinshausen et al., 2009; Solomon et al., 2009; ). It is urgent to develop and utilize renewable clean energy while reducing the concentration of CO2 in the atmosphere (; Shindell and Smith, 2019). Notably, as a simple form of carbon storage, the rich carbon resources contained in CO2 have huge development potential. Using CO2 as a carbon feedstock to prepare carbon-based fuels can help alleviate the energy crisis and global warming at the same time, and has become a current research hotspot in the fields of both energy and environment (Olah et al., 2011; ; ; ; ). However, the liner molecule with high thermodynamic stability and kinetic inertness makes it a great challenge for the activation and conversion of CO2 (Ola and Maroto-Valer, 2015; Wei L. et al., 2018; ; Nguyen et al., 2020). A lot of energy needs to be injected to break the C=O bond (dissociation energy about 750 kJ mol−1) in CO2 (). Moreover, the extremely low water solubility of CO2 (about 30 mM under 25°C at 1 atm) results in the low conversion efficiency of CO2 in the aqueous reaction system (Xie et al., 2014). Therefore, a highly efficient reaction mode is also in great demand.
Fortunately, the natural photosynthesis motivated by solar energy to covert CO2 into carbonhydrates as well as the release of O2 by water oxidation provides a very promising solution to reduce the CO2 level in atmosphere, which inspires the development of artificial photosynthesis systems (; ; Zhang and Sun, 2019). As shown in Figure 1A, the water oxidation process takes place in the photosystem II (PSII) of green plants to provide electrons and protons for the CO2 fixation and conversion in the photosystem I (PSI). Since a series of pioneering works devoted by Fujishima and Honda on semiconductor photocatalysis in the 1970s (; ), substantial efforts have been made for the combination of the two individual processes within a single artificial architecture to mimic the natural photosynthesis (shown in Figure 1B) during the past decades (; Tu et al., 2014; White et al., 2015; ; ; Xu and Carter, 2019).
FIGURE 1
In a typical semiconductor photocatalytic process, the semiconductor photocatalyst is excited by the incident photons with energy greater than or equal to its bandgap energy (Eg), where electrons (e-) are excited to the conduction band (CB) to participate in the reduction reactions, remaining holes (h+) in the valence band (VB) for the oxidation reactions. Considering that CO2 molecule is very stable and the photocatalytic CO2 reduction is a series of uphill reactions (ΔG0>0, see in Table 1) (Wei L. et al., 2018), a large energy input is necessary to covert CO2 into solar fuels, corresponding to the photons in the ultraviolet or shortwave visible regions. In addition, the band structure of ideal semiconductors needs to meet the redox potentials of CO2 reduction and water oxidation reactions at the same time, as listed in Table 2 (; White et al., 2015). Generally, the CB edge position (ECB) should be more negative than the potential for reducing CO2, whereas the VB edge position (EVB) should be more positive than the potential for oxidizing H2O to O2. So far, the photocatalytic activity of numerous photocatalysts, etc. TiO2 (; ; Ola and Maroto-Valer, 2015), ZnO (; Nie et al., 2018; ), WO3 (; Shi et al., 2019; Wang H. et al., 2019), SnO2 (; You et al., 2020), Cu2O (; Shi et al., 2019), CdS (; ; Wei Z. H. et al., 2018; ; ), Bi2WO6 (; ), BiVO4 (Mao et al., 2012; Wei Z. H. et al., 2018), BiOBr (Ye et al., 2016; Wu et al., 2018), g-C3N4 (; Nie et al., 2018; Thi Thanh Truc et al., 2019; Wang et al., 2020a) and graphene (; Xiong et al., 2016; Shehzad et al., 2018a; Zhao H. et al., 2018; ), have been investigated intensively, in which few of them can realize the synergism of photocatalytic CO2 reduction and water oxidation. In particular, the low-cost TiO2 with suitable band structure and high resistibility to light corrosion is a very promising candidate, which has become the benchmark in this field (; ; Ola and Maroto-Valer, 2015). However, the wide band gap of TiO2 (3.2 eV for anatase) responses to UV light only, which accounts for only 3–5% of the incoming solar spectrum, thus restricting the conversion efficiency of solar energy. Besides, the fast recombination of photo-induced e-/h+ pairs within TiO2 results in the low charge separation efficiency, therefore reducing its photocatalytic performance further. Moreover, the low selectivity toward photoreduction products of CO2 based on aqueous TiO2 suspension photocatalytic system should also be improved.
TABLE 1
| Reactions | ΔG0 (kJ∙mol−1) | |
|---|---|---|
| 1 | 237 | |
| 2 | 257 | |
| 3 | 286 | |
| 4 | 522 | |
| 5 | 703 | |
| 6 | 818 |
The possible reactions during the photocatalytic CO2 reduction process.
TABLE 2
| Reactions | E0 (V) vs. NHE at pH 7 | |
|---|---|---|
| 1 | 1.23 | |
| 2 | −1.9 | |
| 3 | −0.53 | |
| 4 | −0.61 | |
| 5 | −0.48 | |
| 6 | −0.38 | |
| 7 | −0.24 | |
| 8 | −0.41 |
Electrochemical potentials of H2O oxidation and CO2 reduction into various products.
In the past few decades, various of strategies have been developed to enhance the photocatalytic performance of TiO2. Among them, the nanostructured TiO2 with single crystalline phase exhibited the decreased recombination rate of charge carriers, comparing to the polycrystalline samples that possess large amount of grain boundaries and defects acting as recombination centers (Tu et al., 2014; Xu et al., 2015). Moreover, crystal facet engineering has been adopted to tune the surface energy and active sites of TiO2, contributing to the adsorption and activation of CO2 (; Xiong et al., 2018; Tu et al., 2020). Obviously, the preference adsorption of CO2 molecules at the surface oxygen vacancy sites of TiO2 can reduce the reactive barrier of CO2 photoreduction reactions, in which one oxygen atom of CO2 is trapped by a bridging oxygen vacancy defect to induce affinity interactions (; ; Tan et al., 2017). Moreover, the localized electrons of oxygen vacancies can form adventitious energy levels, extending the photoresponsive range of semiconductor photocatalyst. Besides, surface oxygen vacancies with typical defect states can trap electrons or holes to inhibit their recombination (Wang et al., 2018). To sum up, the significance of surface oxygen vacancies on defected TiO2 has been ascertained in the enhancement of CO2 adsorption, activation, dissolution, and stabilization of reaction intermediates (Nguyen et al., 2020). In addition, metal/nonmetal ion doping is used to introduce additional energy level between the band gap of TiO2, resulting in the reduced band width and enhanced visible light adsorption (Tu et al., 2014; Ola and Maroto-Valer, 2015; Shehzad et al., 2018b; Patil et al., 2019). Dye sensitized TiO2 displays enhanced photoreduction efficiency of CO2 due to the injection of photosensitized electrons from the energy level of dye molecule to the CB of TiO2 with more negative potential, while the superior visible light responsibility of dye molecules can also improve the utilization of incident light (; Ola and Maroto-Valer, 2015; ; Woo et al., 2019). Although these strategies have proven to be effective, the charge separation efficiency, light energy utilization and product selectivity still need to be further improved to fulfill the demand of more efficient photoreduction of CO2, even for the practical application in the future.
As is known, construction of heterojunction between TiO2 and cocatalyst with matching electronic band structures can significantly promote the separation of photogenerated e- and h+, enlarge the spectra response range, while the physicochemical properties of some special cocatalyst can promote the photocatalytic CO2 reduction or water oxidation to a certain extent, thereby resulting in high photoreduction efficiency of CO2 over the heterostructured phocatalytic system with enhanced reduction products selectivity (; Wang et al., 2014; Wei L. et al., 2018; Nguyen et al., 2020).
In addition to photocatalysts, photoreactors as well as reaction modes also play vital roles in affecting the photoreduction efficiency of CO2. Generally, the two key parameters which determine the types of photoreactors utilized in CO2 photoreduction are the phases involved (i.e., gas-solid, liquid-solid) and the mode of operation (i.e., batch, semi-batch or continuous). In the solid-liquid cases, photocatalysts are usually dispersed in alkaline mediums (aqueous solution) which can realize higher CO2 solubility, resulting in the formation of CO32− and HCO3−. However, these species are difficult to be reduced in comparison with CO2 (). In order to overcome the above drawbacks, the solid-vapor mode has been widely applied where the generation rate of the products for CO2 photoreduction can be improved significantly (Xie et al., 2014; Xie et al., 2016; Xiong et al., 2017b). In addition, the exposure of photocatalysts in a CO2 atmosphere can reduce the generation of H2, thus enhancing the selectivity for CO2 reduction. Obviously, the solid-vapor mode is more suitable for CO2 photoreduction in the presence of H2O.
In this review, we will mainly focus on the recent advances of photocatatytic CO2 reduction processes with water oxidation using TiO2-based heterojunction as photocatalysts. Different categories of heterojunctions, including S-S heterojunction (Figure 2A), S-M heterojunction (Figure 2B), S-C heterojunction (Figure 2C), multicomponent heterojunction, phase heterojunction and facet heterojunction (Figure 2D) are reviewed individually. In addition, the unique functions of cocatalysts among different heterostructured photocatalytic systems (etc. photosensitizer, CO2 reduction promoter, water oxidation promoter and surface plasmon resonance (SPR) source) as well as the photoreduction mechanisms of CO2 are discussed in detail. In the end, we will look forward to the prospects, opportunities and challenges of photocatalytic CO2 reduction, predict the research directions of this field in the future, and put forward our opinions on the construction of efficient multifunctional integrated photocatalytic CO2 reduction systems. We believe that this review will provide some useful guidelines for the construction of heterostructured photocatalysts for photoreduction of CO2 with high performance in the future.
FIGURE 2
Photoreduction of CO2 to Solar Fuels on TiO2-Based Heterojunctions
From the perspective of semiconductor photocatalysis, the premise of high photocatalytic efficiency is the efficient separation and rapid transfer of photogenerated e-/h+ pairs, thereby prolonging their lifetimes and inhibiting their recombination. The strategy for the construction of heterojunction by coupling semiconductor (TiO2) with a secondary substance including other semiconductors (; Yang et al., 2017; She et al., 2018; Xu et al., 2018a; ; ; Thi Thanh Truc et al., 2019; Wu et al., 2019), metal nanoparticles (Xie et al., 2013; Neaţu et al., 2014; ; Xiong et al., 2015; ; Yu et al., 2016; ; Tahir et al., 2017; Xiong et al., 2017C; ; ; Tan et al., 2018; Tasbihi et al., 2018a; Wei Y. et al., 2018; Zhao Y. et al., 2018; ; Wang R. et al., 2019; Zeng et al., 2020; Ziarati et al., 2020; Wang et al., 2021) and carbon-based nanostructures (Xia et al., 2007; Tu et al., 2013; ; ; Xiong et al., 2016; ; Tan et al., 2017; Wang et al., 2017; ; Olowoyo et al., 2018; Shehzad et al., 2018a; Zhang J. et al., 2018; Zubair et al., 2018; ; Olowoyo et al., 2019; Wang R. et al., 2019; Rodríguez et al., 2020) has been generally applied. Since different phases (etc. anatase, brookite, or rutile) and exposed facets (etc. (001) or (101)) of TiO2 exhibit various of band structure and reactivity, TiO2-based phase heterojunction (Reñones et al., 2016; ; ; ; ; Xiong et al., 2020) or facet heterojunction (Yu et al., 2014; ; ; Xiong et al., 2016; Xiong et al., 2017a; ) are also fabricated for photocatalytic CO2 reduction, which exhibits enhanced photocatalytic efficiency in comparison with pristine TiO2. On the one hand, the heterostructure facilitates the separation of photoinduced charge carriers which then transfer across the heterointerface to restrain recombination. On the other hand, the additional active sites introduced by the cocatalysts favor for the adsorption and activation of CO2, thus enhancing the photoreduction efficiency of CO2. Besides, the promoted quantum efficiency and product selectivity can also be expected by the constructed heterojunctions, since light-excitation attributes, band structure, and separation efficiency of photogenerated charge carriers of heterojunctions play vital roles in the selectivity of CO2 photoreduction products. Moreover, various cocatalysts with different reactive active sites can also affect the product selectivity greatly, where the adsorption/activation of CO2 as well as the adsorption/desorption of the intermediates are tuned ().
In this section, the rational design, fabrication, photocatalytic performance and photoreduction mechanism of CO2 over the TiO2-based typical categories of heterojunctions (S-S, S-M, S-C, multicomponent, phase and facet heterojunction) will be reviewed and discussed in detail. In addition, the selectivity toward photoreduction products is another focus. The relative mechanism was concluded and analyzed in the certain case.
TiO2 Based Z-scheme S-S Heterojunction for CO2 Photoreduction
Coupling n-type TiO2 with a p-type semiconductor possessing matching energy band structure to form a p-n heterojunction is one of the most classic S-S heterojunction (Zeng et al., 2014; ; ; Zhang L. et al., 2018; ; Zhang et al., 2020). As shown in Figure 3, the contacting of the two semiconductors leads to the diffusion of e- and h+, then forms a space-charge region at the interface of the p-n heterojunction (Wang et al., 2014). As a result, a strong built-in electrical field is created which can drive the photoinduced e- and h+ to transfer in the opposite directions, therefore enhancing the separation efficiency of charge carriers. In addition to p-n heterojunction, TiO2-based non-p-n heterojunctions are also common (Yang et al., 2017; She et al., 2018; ; ; Thi Thanh Truc et al., 2019; Wu et al., 2019). Typically, two closely integrated semiconductors with staggered band configurations can form a type II-1 heterojunction (shown in Figure 4A) (Zhang and Jaroniec, 2018), in which the band bending facilitates the charge transfer at the heterointerface. Specifically, e- and h+ are separated individually in both semiconductor 1 (SC-1) and semiconductor 2 (SC-2) under the irradiation of incident light. The difference in energy level leads to the transfer of e- from the CB of SC-1 with more negative potential to the CB of SC-2. Meanwhile, h+ can transfer from the VB of SC-2 to the VB of SC-1 with more positive potential. Similar to the p-n heterojunction, the reverse migration of e- and h+ in the type II-1 heterojunction improves the separation efficiency of charge carriers, thus endowing the enhanced photocatalytic performance of the heterostructured system. However, the way of carrier transfer in the above heterojunctions will lead to a decrease in their redox ability, making it difficult to ensure the optimal photocatalytic activity.
FIGURE 3
FIGURE 4
Recently, study on the construction of all-solid-state Z-scheme heterojunction has gained great attention of researchers (; ; Takayama et al., 2017; Yang et al., 2017; She et al., 2018; ; Thi Thanh Truc et al., 2019; Wang et al., 2019; Raza et al., 2020; Wang et al., 2020). Comparing to the p-n and type II-1 heterojunctions, the carrier transfer mode in the Z-scheme heterojunction is more favorable for photocatalytic application. In general, the band bending at the interface of direct Z-scheme heterojunction (type II-2) is conducive to the recombination of photoinduced e- and h+ with weaker reduction and oxidation ability, so that e- in the more negative CB of SC-1 and h+ in the more positive VB of SC-2 can be remained (shown in Figure 4B). As a result, both high separation efficiency and optimal redox ability of photoinduced charge carriers can be realized, thus endowing the high photocatalytic performance of the Z-scheme system. In this section, recent advances for the construction of TiO2-based all-solid-state indirect and direct Z-scheme heterojunctions as well as their application for photocatalytic CO2 reduction with water oxidation will be reviewed and discussed in detail. Photocatalytic CO2 reduction performance of the typical TiO2-based all-solid-state Z-scheme heterojunctions are listed in Table 3.
TABLE 3
| Photocatalyst | Reductant | Light source | Generation rate of main products (μmol∙gcat−1∙h−1) | Quantum efficiency (%) | References |
|---|---|---|---|---|---|
| Indirect Z-scheme heterojunction | |||||
| CdS/rGO/TiO2 | H2O vapor | 300 W | CH4: 0.12 (μmol∙h−1) | - | |
| Xe lamp | |||||
| CuGaS2-RGO-TiO2 | Na2S aqueous solution | 300 W | CO: 0.15 | - | Takayama et al. (2017) |
| Xe lamp (λ > 330 nm) | H2: 28.8 (μmol∙h−1) | ||||
| Al−O Linked porous-g-C3N4/TiO2-nanotube (PCN/TNT) | Na2SO4 aqueous solution | 150 W Xe lamp | CH3COOH | - | Wu et al. (2019) |
| HCOOH | |||||
| CH3OH | |||||
| ZnFe2O4/Ag/TiO2 nanorods | H2O vapor | 200 W Hg lamp | CO: 1025 | - | Tahir (2020) |
| CH4: 132 | |||||
| CH3OH: 30.8 | |||||
| C2H6: 19.1 (μmol∙h−1) | |||||
| g-C3N4/Pt/3DOM-TiO2@C | H2O vapor | 300 W Xe lamp (λ ≥ 420 nm) | CO: 1.47 | 5.67 | Wang et al. (2020a) |
| CH4: 6.56 | |||||
| H2: 0.82 | |||||
| (Au/A-TiO2)@g-C3N4 | H2O vapor | 300 W Xe lamp (λ ≥ 420 nm) | CH4: 37.4 | 1.91 | Wang et al. (2020b) |
| CO: 21.7 | |||||
| Direct Z-scheme heterojunction | |||||
| Cu2O/TiO2 | H2O vapor | 1 kW high-pressure Hg (Xe) arc lamp (λ ≥ 305 nm) | CO: 2.11 | - | |
| ZnIn2S4/TiO2 | H2O vapor | 300 W Xe lamp | CH4: 1.135 | - | Yang et al. (2017) |
| TiO2/CuInS2 | H2O vapor | 350 W Xe lamp | CH4: 2.5 | - | Xu et al. (2018b) |
| TiO2/CdS | H2O vapor | 300 W Xe lamp | CH4: 11.9 | - | |
| μmol∙h−1∙m−2 | |||||
| Zn3In2S6/TiO2 | H2O vapor | 300 W Xe lamp | CH4: 6.19 | - | She et al. (2018) |
| CO: 23.35 | |||||
| Nb-TiO2/g-C3N4 | H2O vapor | Two 30 W white bulbs | CH4: 562 | - | Thi Thanh Truc et al. (2019) |
| CO: 420 | |||||
| HCOOH: 698 | |||||
| Copper (II)-porphyrin zirconium metal-organic framework (PCN-224(Cu))/TiO2 | Na2SO4 aqueous solution | 300 W Xe lamp | CO: 37.21 | - | Wang L. et al. (2019) |
| WO3-TiO2/Cu2ZnSnS4 | H2O vapor | 400 W Xe lamp (λ > 420 nm) | CH4: 1.69 | 0.52 | Raza et al. (2020) |
| CO: 15.37 | |||||
| Au-TiO2 | H2O vapor | AM1.5 G simulated sunlight | CH4: 302 | - | Zeng et al. (2020) |
| 50 W white cold LED light (λ > 400 nm) | HCHO: 420 | - | |||
| CO: 323 | |||||
| Single metal | |||||
| 3DOM Au/TiO2 | H2O vapor | 300 W Xe lamp | CH4: 2.89 | - | |
| Pt2+-Pt0/TiO2 | H2O vapor | 300 W Xe lamp | H2: 394.7 | 0.36 | Xiong et al. (2015) |
| CH4: 37.78 | |||||
| CO: 8.03 | |||||
| Ag/TiO2 | H2O vapor | 300 W Xe lamp | CH4: 1.40 | 0.16 (400 nm); 0.013 (520 nm) | Yu et al. (2016) |
| Ag/TiO2 nanorod arrays | H2O vapor | 300 W Xe lamp (λ > 420 nm) | CH4: 1.13 | - | |
| CO: 12 | |||||
| Pt/TiO2 | H2O vapor | Four 6 W lamps (λ ≤ 365 nm) | CH4 | - | Tasbihi et al. (2018a) |
| Pt/TiO2-COK-12 | CO | ||||
| Ag/TiO2 nanotube arrays (TNTAs) | H2O vapor | 300 W Xe lamp | CH4 | - | |
| Pt/TiO2-Al2O3 foam | H2O vapor | UV 8 W Hg lamp | H2: 22.5 | - | Tasbihi et al. (2018b) |
| CH4: 1.21 | |||||
| CO: 0.54 | |||||
| Au-TiO2 Nanotubes (TNTs) | H2O vapor | 300 W Xe lamp | CH4: 14.67% | - | |
| Au/TiO2 | H2O vapor | 300 W Xe lamp | CH4: 70.34 | - | Wang R. et al. (2019) |
| CO: 19.75 | |||||
| Au/TiO2 | H2O vapor | 300 W Xe lamp | CH4: 0.2 | - | Wang et al. (2021) |
| CO: 1.2 | |||||
| Metal alloy | |||||
| (Au, Cu)/TiO2 | H2O vapor | AM1.5 G simulated sunlight | H2: 286 | - | Neaţu et al. (2014) |
| CH4: 2200 ± 300 | |||||
| AgPd/TiO2 | Triethylamine (TEA) aqueous solution | 300 W Xe lamp | H2: 144.5 | - | Tan et al. (2018) |
| CH4: 79.0 | |||||
| PtRu/TiO2 | H2O vapor | 300 W Xe lamp | H2: 16.5 | 0.98 | Wei Y. et al. (2018) |
| CH4: 38.7 | |||||
| CO: 2.6 | |||||
| Hierarchical urchin-like yolk@shell TiO2-xHx (HUY@S-TOH)/AuPd | H2O (liquid) | 300 W Xe lamp | CH4: 47.0 | - | Ziarati et al. (2020) |
| Graphene and its derivatives | |||||
| Graphene-TiO2 | H2O vapor | 300 W Xe lamp | CH4: 8 | - | Tu et al. (2013) |
| C2H6: 16.8 | |||||
| RGO/Pt-TiO2 nanotubes (TNTs) | H2O vapor | 500 W tungsten-halog--en lamp | CH4: 10.96 (μmol∙m−2) | - | Sim et al. (2015) |
| TiO2/Nitrogen doped rGO (NrGO) | H2O vapor | 400 W Xe lamp | CO: 50 | 0.0072 | |
| GO/oxygen rich TiO2 (OTiO2) | H2O vapor | 300 W Xe lamp | CH4: 0.43 | 0.0103 | Tan et al. (2017) |
| rGO/TiO2 | H2O vapor | 500 W Hg lamp | CH4: 12.75 | - | Shehzad et al. (2018a) |
| CO: 11.93 | |||||
| ((Pt/TiO2)@rGO) | H2O vapor | 300 W Xe lamp | H2: 5.6 | 1.93 | Zhao Y. et al. (2018) |
| CH4: 41.3 | |||||
| CO: 0.4 | |||||
| Graphene quantum dots (GQDs)/TiO2 | H2O vapor | 100 W Xe solar simulator | CH4: 1.98 (ppm∙cm−2∙h−1) | - | Zubair et al. (2018) |
| rGO/TiO2 | Triethanolamine (TEOA) aqueous solution | 8 W UV-A lamp | CH3OH: 2330 | - | Olowoyo et al. (2019) |
| CNT | |||||
| MWCNT/TiO2 | H2O vapor | 15 W UV lamp | CH4: 11.74 | - | Xia et al. (2007) |
| HCOOH: 18.67 | |||||
| C2H5OH: 29.87 | |||||
| MWCNT/TiO2 | H2O (liquid) | 15 W energy saving light bulb | CH4: 0.17 | - | |
| Ag-MWCNT@TiO2 | H2O vapor | 15 W energy saving light bulb | CH4: 0.91 | - | |
| C2H6: 0.048 | |||||
| MWCNT/TiO2 | TEOA aqueous solution | 8 W UV-A lamp | H2: 2360.0 | - | Olowoyo et al. (2019) |
| CH3OH: 3246.1 | |||||
| HCOOH: 68.5 | |||||
| CNT/TiO2/Cu | H2O vapor | 300 W Xe lamp | CH4: 1.1 | - | Rodríguez et al. (2020) |
| CO: 8.1 | |||||
| Other carbon forms | |||||
| Carbon@TiO2 hollow spheres | H2O vapor | 300 W Xe lamp | CH4: 4.2 | - | Wang et al. (2017) |
| CH3OH: 9.1 | |||||
| N, S-containing carbon quantum dots (NCQDs)/TiO2 | H2O vapor | 300 W Xe lamp | CH4: 0.13 | - | |
| CO: 0.19 | |||||
| Carbon nanofibers@TiO2 | H2O vapor | 350 W Xe lamp | CH4: 13.52 | - | Zhang J. et al. (2018) |
| MgO-Pt-TiO2 | H2O vapor | 100 W Xe lamp | H2: 14 | - | Xie et al. (2014) |
| CH4: 1.2 | |||||
| CO: 1.8 | |||||
| Pt-rGO-TiO2 | H2O vapor | 15 W energy saving light bulb | CH4: 0.28 | - | Tan et al. (2015) |
| Pd-rGO-TiO2 | CH4: 0.20 | ||||
| Ag-rGO-TiO2 | CH4: 0.17 | ||||
| Au-rGO-TiO2 | CH4: 0.13 | ||||
| Pt-Cu2O/TiO2 | H2O vapor | 300 W Xe lamp | CH4: 1.42 | - | Xiong et al. (2017c) |
| CO: 0.05 | |||||
| WSe2-Graphene-TiO2 | Na2SO3 aqueous solution | 300 W Xe lamp | CH3OH: 6.33 | - | |
| Pt/MgAl layered double oxides (MgAl-LDO)/TiO2 | H2O (liquid) | 300 W Xe lamp | CH4: 1.42 | - | |
| CO: 2.3 | |||||
| TiO2-Graphene few-layered MoS2 | H2O vapor | 300 W Xe lamp | CO: 92.33 | - | |
| Au/Al2O3/TiO2 | H2O vapor | 450 W Xe lamp | CO: 11.8 | - | Zhao H. et al. (2018) |
| TiO2-MnOx-Pt | H2O vapor | 350 W Xe lamp | CH4: 34.67 | - | Meng et al. (2019) |
| CH3OH: 30.33 (μmol∙m−2∙h−1) | |||||
| Ag-MgO-TiO2 | H2O vapor | 300 W Xe lamp | CH4: 0.86 | 0.091 | Xu et al. (2018a) |
| CH3OH: 0.06 | |||||
| Au@TiO2 hollow spheres (THS)@CoO | H2O vapor | 300 W Xe lamp | CH4: 13.3 | - | Zhu et al. (2019) |
| Phase heterojunction | |||||
| Anatase-rutile TiO2 fibers | H2O vapor | Four 6 W | CO: 10.19 | 0.036 | Reñones et al. (2016) |
| UV lamps | CH4: 1.34 | ||||
| H2: 19.94 | |||||
| Anatase-rutile TiO2 nanoparticles with oxygen vacancy | H2O vapor | 300 W | CH4: 43.2 | - | Xiong et al. (2020) |
| Xe lamp | |||||
| Disordered Anatase/ordered rutile (Ad/Ro) TiO2 nanoparticles | H2O vapor | Solar simulator 1 Sun | CH4: 3.98 | 0.273 | |
| CO: 3.02 | |||||
| Pt-loaded anatase-rutile TiO2 nanoparticles | H2O vapor | 200 W Hg–Xe light | CH4 | - | |
| CO | |||||
| N-doped carbon coating paragenetic anatase/rutile heterojunction | TEOA and MeCN | 300 W | CO: 24.31 | - | |
| Xe lamp | |||||
| SrCO3-Modified brookite/anatase TiO2 heterojunction | H2O vapor | 300 W | CH4: 19.66 | - | |
| Xe lamp | CO: 2.64 | ||||
| Facet heterojunction | |||||
| {101}/{001} TiO2 | H2O vapor | 300 W | CH4: 1.35 | - | Yu et al. (2014) |
| Xe lamp | |||||
| Oxygen-deficient {101}/{001} TiO2 | H2O vapor | 100 W Hg lamp/450 W Xe lamp | CO: ∼10.91 (UV-vis) | 0.31 (UV-vis) | |
| CO: ∼5.36 (visible) | 0.134 (visible) | ||||
| Pt-loaded {101}/{001} TiO2 | 0.1 M KHCO3 solution | 250 W Hg lamp | CH4: 4.0 | - | |
| Pt-loaded {101}/{001} TiO2 | H2O vapor | 300 W | CH4: 4.6 | - | Xiong et al. (2017a) |
| Xe lamp | H2: 9.9 | ||||
| Graphene supported {101}/{001} TiO2 | H2O vapor | 300 W | CO: 70.8 | CO: 0.0557 CH4: 0.0864 | Xiong et al. (2016) |
| Xe lamp | CH4: 27.4 |
Photocatalytic CO2 reduction performance on typical TiO2-based S-S (Z-scheme), S-M, S-C, multicomponent, phase and facet heterojunctions.
Construction of indirect Z-scheme system between TiO2 and another semiconductor using noble metals such as Pt (Wang et al., 2020a), Au (Wang et al., 2020b) and Ag (Tahir, 2020) as electron mediators has gained increased attention due its enhanced separation efficiency of photogenerated e−/h+ pairs with the recombination of inefficient charge carriers, thereby improving the photoreduction efficiency of CO2. As reported by Tahir, ZnFe2O4/Ag/TiO2 nanocomposite was fabricated by physical mixing Ag/TiO2 nanorods and ZnFe2O4 nanospheres in methanol solution under continuous stirring (Tahir, 2020). Compared to the point contact between 0D TiO2 nanoarticles and 0D ZnFe2O4 nanospheres, the stronger interaction between 0D ZnFe2O4 nanospheres and 1D TiO2 nanorods is beneficial to the transfer of photogenerated electrons and holes at the interface. At the same time, the migration of these charge carriers along the 1D nanostructure is more efficient, which significantly inhibits their recombination. Moreover, the UV irradiation induced Z-scheme carrier transfer pathway ensures the high redox capability of the remaining carriers with the recombination of inefficient species within Ag nanoparticles, resulting in the superior CO generation rate of 1025 μmol gcat−1 h−1. Compared to ZnFe2O4, graphic-C3N4 (g-C3N4) is more preferred for the construction of TiO2-based Z-scheme heterojunction due to its fully visible light utilization, improved CO2 adsorption capacity (derived from its surface π bond) and proper band structure for CO2 photoreduction with H2O oxidation (Wu et al., 2019; Wang et al., 2020a). Moreover, it can also trap photogenerated electrons to enhance charge separation efficiency within the heterojunction. On this basis, g-C3N4 was coated on the surface of Au/TiO2 hybrid to form a Z-scheme photocatalyst (Figure 5A,B) for visible-light-driven (VLD) photocatalytic CO2 reduction (Wang et al., 2020a). In particular, the efficient separation of photogenerated e−/h+ pairs within anatase TiO2 is attributed to the formation of {001}/{101} facet heterojunction. Then, photogenerated electrons in the CB of TiO2 are directionally transferred through Au and recombine with photogenerated holes in the VB of g-C3N4, thereby boosting the photoreduction of CO2 by photogenerated electrons in the CB of g-C3N4 (shown in Figure 5C). Notably, the high selectivity toward CO2 photoreduction (>99%) was realized with few H2 generation, while the selectivity for CH4 generation (63.3%) was also enhanced compared to pure g-C3N4 (1.4%). The following work of this group (Wang et al., 2020a) devoted to further improving the selectivity for CH4 generation with high apparent quantum efficiency (AQE) under visible light irradiation, in which 3D ordered macroporous (3DOM) TiO2@C was coupled with g-C3N4 using Pt as electron mediator (3DOM-CNPTC) (shown in Figure 5D,E). The DFT calculation revealed the enrichment of photogenerated electorns by abundant N-sites on the interface between Pt and g-C3N4, which can reduce the adsorbed CO2 to CH4 directly in the presence of H2O, thereby improving the selectivity for CH4 generation (81.7%). In addition, the strong visible light adsorption by g-C3N4 and Pt as well as the multiple scattering of incident light within the 3DOM structure (Figure 5F) result in the high AQE of the Z-scheme heterojunction (5.67%), which is 140 folds than that of P25 (0.04%). Interestingly, the interaction between TiO2 and g-C3N4 could also be strengthened by Al-O links which was introduced into the Z-scheme through impregnation (Wu et al., 2019). Specifically, TiO2 nanotubes (TNTs) fabricated via anodization of Ti foils are dipped in AlCl3 solution followed by calcination to obtain Al-O-modified TNTs, which is then combined with porous g-C3N4 (PCN) via solid sublimation and transition of urea/NaHCO3 hybrid to from Al-O linked PCN/TNT composites. Results show that the low charge transfer efficiency at the interface between TiO2 and g-C3N4 caused by lattice mismatch of the two components can be significantly improved by introducing Al-O links to replace surface hydroxyl groups, thereby enhancing the separation efficiency of photogenerated charge carriers and benefiting for photoreduction of CO2 with increased yields of acetic acid, formic acid and methanol. According to Kuai’s research, rGO could also serve as electron mediator for the construction of Z-scheme heterojunction between TiO2 and CdS (). The remarkably prolonged photoluminasence (PL) decay time of CdS/rGO/TiO2 (2.4 ns) reveals the different electron migration mechanism compared to CdS/TiO2 (0.38 ns), which follows the carrier transfer mode in type II heterojunction. Obviously, the presence of rGO leads to the establishment of Z-scheme system, in which photogenerated electrons in the CB of TiO2 are extracted by rGO and then transferred to the VB of CdS to recombine with photogenerated holes there, resulting in the enrichment of photogenerated electrons and holes in the CB of CdS and the VB of TiO2, respectively. Although the photoreduction efficiency of CO2 is still low on CdS/rGO/TiO2, the attempt to construct Z-scheme heterojunction with low-cost carbon material instead of noble metal as electron mediator is successful, while the high selectivity for CH4 generation is also promising.
FIGURE 5
Recently, construction of direct Z-scheme system by coupling two different semiconductors with matching geometric and band structure has become research hotspot in the field of photocatalytic CO2 reduction, which is more facile to synthesis and more convenient for charge transfer at the interface. In particular, semiconductors with narrow band gap are more preferred in the TiO2-based direct Z-scheme heterojunction to improve the utilization of visible light. Typically, ZnInS2 nanosheets were decorated onto the surface of 1D TiO2 nanobelts via hydrothermal process (Yang et al., 2017). The authors claimed the Z-scheme electron transfer mechanism between ZnInS2 and TiO2 based on the experimental results of CH4 generation. Since the CB potential of TiO2 is lower than the redox potential of CO2/CH4, it is reasonable to believe that photogenerated electrons in the CB of ZnInS2 are retained due to the Z-scheme electron transfer mechanism and take in charge for photocatalytic CO2 reduction to produce CH4. However, stronger evidence is needed to prove this conjecture. In another work, a similar 3D hierarchical nanostructure was constructed by depositing CuInS2 nanoplates on TiO2 nanofibers (Xu et al., 2018b). DFT calculations revealed the higher Fermi level (EF) of CuInS2 than that of TiO2, which forces electrons transfer from CuInS2 to TiO2 after their contact and creates a build in internal electric filed at the interface. The recombination of photogenerated electrons in the CB of TiO2 and photogenerated holes in the VB of CuInS2 under the guidance of the internal electric filed leads to the accomplishment of high efficient Z-scheme charge transfer pathway. As a result, photogenerated electrons enriched in the CB of CuInS2 facilitate the photocatalytic reduction of CO2 to produce CH4 and CH3OH in the presence of protons provided by water oxidation. In situ irradiated X-ray photoelectron spectroscopy (ISI-XPS) was also applied to provide direct evidence of Z-scheme electron transfer mechanism (). The binding energy shifts of Ti 2p (by 0.3 eV) and Cd 3 days (by -0.2 eV) under light irradiation indicate the decreased electron density of TiO2 as well as the increased electron density of CdS, suggesting that photogenerated electrons migrates from TiO2 to CdS, which agrees well with Z-scheme mechanism. The ternary semiconductor of Zn3In2S6 was also used by She et al. for the construction of direct Z-scheme heterojunction with TiO2 (She et al., 2018). Higher CO and CH4 yields were realized on Zn3In2S6/TiO2 in comparison with ZnInS2/TiO2 and CuInS2/TiO2, which could be attributed to the higher crystallinity of the two constituents that favored for charge separation (shown in Figure 6). In addition, modification on TiO2 to narrow its band gap for the improved visible light adsorption is also an efficient strategy to further enhance the photocatalytic performance of the TiO2-based Z-scheme heterojunction. As reported by Truc et al., Eg of TiO2 (3.2 eV) was reduced to 2.91 eV after Nb doping (Thi Thanh Truc et al., 2019). The as-obtained Nb-TiO2 was grinded with melamine followed by calcination at 550 °C to form Nb-TiO2/g-C3N4 heterojunction with a clear boundary at the interface. The well matched lattice spacing of the TiO2 {101} (0.353 nm) and g-C3N4 {002} (0.320 nm) facets benefits to the electron transfer at the interface following Z-scheme mechanism, resulting in high efficiency for photocatalytic CO2 reduction. The advantages of low cost, full visible light spectrum responsibility (400–700 nm) and superior generation rate of CH4 (562 μmol gcat−1 h−1), CO (420 μmol gcat−1 h−1) and HCOOH (698 μmol gcat−1 h−1), make Nb-TiO2/g-C3N4 a promising VLD photocatalyst for practical application in the future to reduce the CO2 level in the atmosphere. Moreover, the high O2 yield of Nb-TiO2/g-C3N4 (1702 μmol gcat−1 h−1) indicates that the artificial Z-scheme system can mimic the nature photosynthesis by green plants well.
FIGURE 6
For a long time, stability is one of the main defects facing the photocatalysts that restricts their long-term performance. The photocatalytic activity decreased continuously in the process of illumination due to photocorrosion. Construction of Z-scheme heterojunction can also protect the narrow band gap semiconductor coupled with TiO2 from photo-oxidation. As reported by Aguirre et al., XPS spectra of Cu2O exhibited an increased Cu(II) content with the extension of illumination time, indicating that Cu(I) was partially oxidized by photogenerated holes (). On the contrary, Cu(I) in the Cu2O/TiO2 heterojunction showed no obvious change in valence state, revealing the protection of TiO2 toward Cu2O by injecting photogenerated electrons into the VB of Cu2O to recombine with photogenerated holes there, which also demonstrated the Z-scheme electron transfer mechanism between TiO2 and Cu2O. Interestingly, a stable direct Z-scheme heterojunction can also be formed between TiO2 and metal organic frameworks (MOFs) as PCN-224(Cu) (Wang L. et al., 2019). It is worth nothing that the high specific surface area as well as porous structure of MOFs benefits for CO2 adsorption, while the alternative ligands endow MOFs with adjustable band structure and spectra response range, thus providing a series of promising candidates for the design and construction of direct Z-scheme systems for efficient photocatalytic CO2 reduction. With deepening of the research on the Z-scheme photocatalytic system and the recognition of its photocatalytic performance, more and more different types of Z-scheme photocatalysts have been developed (Raza et al., 2020; Zeng et al., 2020), accelerating the process of photocatalytic CO2 reduction from basic research to practical application.
TiO2 Based S-M Heterojunction for CO2 Photoreduction
As reported by previous literatures, TiO2 modified by metal nanoparticles exhibits enhanced photocatalytic performance due to the promoted charge carrier separation efficiency, expanded light adsorption range as well as high selectivity toward reduction products. In general, Schottky barrier at the interface of semiconductor and metal prevents recombination of photogenerated e−/h+ pairs (; Wang et al., 2014; Ola and Maroto-Valer, 2015; ). Specifically, the higher work function of metal (Wm) than that of semiconductor (Ws) results in the higher Fermi level of semiconductor (EFs) than that of metal (EFm) (shown in Figure 7A). Contacting semiconductor with metal leads to charge transfer at the interface until the alignment of their Fermi levels. During the process, migration of electrons from semiconductor to metal results in band bending of the semiconductor and creates a space charge region at the interface (Schottky barrier), which could prevent backflow of photogenerated electrons to inhibit their recombination with photogenerated holes (shown in Figure 7B). The promoted charge separation efficiency benefits for photocatalytic CO2 reduction as well as the enhanced water oxidation efficiency. In addition, metals can enrich electrons to create high electron density regions on their surfaces, which are favoring for photoreducing CO2 to hydrocarbons in the presence of water due to their lower redox potential than CO. Besides, local surface plasmon resonance (LSPR) effect of certain metals can enhance visible light adsorption of the Schottky heterojunction and inject hot electrons into the CB of semiconductor, thereby facilitating the photoreduction of CO2 (shown in Figure 7C). In this section, strategies for coupling TiO2 with different metal nanoparticles as well as their different enhancement mechanisms of photocatalytic performance will be reviewed and discussed in detail. Photocatalytic CO2 reduction performance of the typical TiO2-based S-M heterojunctions are listed in Table 3.
FIGURE 7
As a classic noble metal cocatalyst, Pt has been widely used in the photocatalysis field for both water splitting and CO2 reduction. In particular, TiO2 loaded with Pt nanoparticles has been demonstrated to be efficient for photoreduction CO2 to CH4. As reported by Fresno et al., a series of Pt/TiO2 photocatalysts with different Pt loading amount were fabricated by treating P25 in the Pt precursor-contained aqueous solution via the deposition-precipitation procedure (Tasbihi et al., 2018a). The as-obtained sample (Figure 8A) displays ca. 100% selectivity toward CH4 generation at the optimum Pt content (>0.58 wt% of TiO2), which can be ascribed to the strong chemisorption of CO on Pt nanoparticles (proved by the FTIR spectra in ATR mode (shown in Figure 8B) along with in-situ NAP-XPS analysis) and the further reduction of CO to CH4 (shown in Figure 8C). However, the adsorption features of CO can not be observed on bare TiO2, which yields CO as the main product under the same condition. The correspondingly net selectivities and quantum yield indices (QYI) are shown in Figure 8D. In another work, Pt/TiO2 was synthesized by the hydrolysis of Titanium (IV) butoxide (TEOT) in the presence of H2PtCl6∙6H2O, resulting in the doping of Pt2+ into the lattice of TiO2 and loading of Pt nanoparicles (Pt0) on the surface of TiO2 (Xiong et al., 2015). The low recombination efficiency of photogenetated e−/h+ pairs due to the deposition of Pt0 as well as strong visible light adsorption attributed to Pt2+ doping significantly enhance photocatalytic performance of Pt2+-Pt0/TiO2 with higher quantum yield (1.42%) for CO2 conversion than that of bare TiO2 (0.36%). Moreover, plenty of electrons enriched by Pt0 and protons supplied by water oxidation benefit for the high selectivity toward CH4 formation (Ered/SCE = −0.48 V). Compared with the formation of CO (Ered/SCE = -0.77 V), this reaction is more feasible in thermodynamics. In summary, the kinetic feasibility (strong chemisorption of CO on Pt) and thermodynamic convenience contribute to photoreduction of CO2 to CH4. On this basis, Pt/TiO2 were deposited on porous supports with large surface area (etc. COK-12 (Tasbihi et al., 2018a) and Al2O3 foam (Tasbihi et al., 2018b)) to promote active sites exposure and achieve higher CH4 yield.
FIGURE 8
Coupling TiO2 with noble metals that can induce the LSPR effect has also been adapted by researchers for efficient photocatalytic CO2 reduction. As reported by Wang et al., 0D/2D Au/TiO2 was synthesized by in situ growth of Au nanoparticles on the surface of TiO2 nanosheets via chemically reduction (Wang R. et al., 2019). The hot electrons induced by the LSPR effect of Au under visible light irradiation (550 nm) could inject into the CB of TiO2 and reduce CO2 to CO. However, as the only electron source (TiO2 can not be excited by visible light), the limited hot electrons cannot further reduce CO to CH4. Interestingly, the Au/TiO2 hybrid yielded CH4 as the main product under 300 W Xe lamp irradiation that contained a certain amount of UV light. Specifically, recombination of photogenerated electrons and holes was suppressed owing to the Schottky barrier that facilitated transfer of e− from the CB of TiO2 to Au. Moreover, h+ remained in the VB of TiO2 could oxidize water to provided plenty of protons for CH4 generation. On this basis, facet engineering was introduced by Wang et al. for the rational design of interface between Au and exposed facet of TiO2 to realize higher charge separation efficiency (Wang et al., 2021). Results showed that the lower height of Schottky barrier on the Au/TiO2{101} interface resulted in more smooth migration of photogenerated electrons from the CB of TiO2 to Au compared to the Au/TiO2{001} interface, thereby exhibiting better performance for photocatalytic CO2 reduction. Notably, the architecture of TiO2 among Au/TiO2 heterojunction also plays an important role for efficient photoreduction of CO2 (; ). Jiao et al. () prepared 3D ordered macroporous (3DOM) TiO2 to support Au nanopaticles, which were uniformly dispersed in the inner wall of the 3DOM structure. The multiple scattering of incident light within the 3DOM structure enhanced light utilization efficiency of the heterojunction, while the ordered macroporous also improved the mass transfer efficiency of the reactants. In addition, the SPR effect of Au induced by visible light irradiation provided extra electrons for photocatalytic CO2 reduction, which was benefited for CH4 generation. In another work, electrochemical anodization was used to fabricate TiO2 nanotubes (TNTs) with light adsorption edge in the visible region, indicating its weak photocatalytic activity illuminated by visible light (). Coupling with Au by electronchemical deposition significantly improved visible light adsorption of TNTs and promoted charge separation efficiency due to the LSPR effect of Au nanoparticles. The excellent CH4 yield (14.67% of CO2 was converted to CH4) under visible light irradiation made Au-TNTs a very promising solar-driven photocatalyst to convert CO2 into hydrocarbon fuels. Similarly, plasmonic Ag were electronchemical deposited into the inner space of TiO2 nanotube arrays (Figure 9A) to investigate the enhancement of SPR effect on photocatalytic performance, while the morphology and structure of as-obtained Ag-TNTAs-E are shown in Figures 9B,C (). The direct evidences of the existence of Schottky barrier between Ag and TiO2 as well as migration of hot electrons induced by the SPR effect of Ag nanoparticles can be found in the synchronous-illumination X-ray photoelectron spectroscopy (SIXPS) spectra based on the shift of Ti 2p3/2 peak before and after illumination (Figures 9D,E). Moreover, the SPR effect of Ag nanoparticles was strengthened by the multiple scatted light in TNTAs (Figure 9F), while the derived near field effect accelerated charge transfer at the heterointerface to promote separation efficiency of photogenerated e−/h+ pairs, thereby endowing enhanced VLD activity of Ag-TNTAs for CO2 photoreduction. Although promoting photoreduction efficiency of CO2 and clarifying the involved mechanisms are the focus of current research, the improvement of photocatalyst synthesis methods also deserves attention. The silver mirror reaction was adopted by Yu et al. to deposited Ag on TiO2 nanoparticles (Yu et al., 2016). CH3OH generated in CO2-saturated 1 M NaHCO3 solution is the main product of photocatalytic CO2 reduction, which is more valuable than the primary products such as CO and CH4. In another work, Ag(I) adsorbed by TiO2 nanorod arrays were completely reduced by cold plasma within 30 s to form uniformly distributed Ag nanoparticles (). This fast and efficient strategy is very promising for the fabrication of metal nanoparticles decorated semiconductor photocatalysts on a large scale.
FIGURE 9
Bimetallic nanoalloys that combined advantages of the two metal components are efficient cocatalysts for photocatalytic CO2 reduction and have been introduced in the TiO2-based photocatalytic systems. As reported by Neaţu et al., Au and Cu species were deposited on TiO2 nanopartcles stepwisely followed by calcining in H2 atmosphere to form Au-Cu alloy (Neaţu et al., 2014). In this case, Au is served as visible light harvester due to its LSPR effect while Cu can covalently bind with CO reduced from CO2 and direct the generation of CH4. Therefore, high VLD photocatalytic activity with outstanding CH4 selectivity (97%) was achieved. Other bimetallic nanoalloys, such as Au-Ag (Tahir et al., 2017), Au-Pd (Ziarati et al., 2020), Ag-Pd (Tan et al., 2018) and Pt-Ru (Wei Y. et al., 2018) nanoparticles are also been used to enhance photocatalytic performance of TiO2 for selective reduction of CO2. Among them, the combination of bimetallic nanoalloys and modified TiO2 (etc. hydrogenated black TiO2 (TiO2-xHx) (Ziarati et al., 2020) and N-doped TiO2 (Tan et al., 2018)) exhibited considerably enhanced visible light utilization and charge separation efficiency, which could become the future development trend of TiO2-based S-M heterojunction for solar-driven CO2 photoreduction. Moreover, construction of S-M heterojunction with hierachical architecture is also in great demand (Ziarati et al., 2020).
TiO2 Based S-C Heterojunction for CO2 Photoreduction
Recently, coupling TiO2 with carbon-based nanomaterials including graphene and its derivatives (etc. graphene (GR) (Tu et al., 2013; Xiong et al., 2016;
Coupling TiO2 With Graphene and Its Derivatives
Construction of TiO2-carbon heterojunction using graphene or its derivatives as the guest/host component derives improved photocatalytic performance due to its excellent electrical properties and chemical stability. It is worth nothing that the path of graphite-GO-rGO has been generally adopted by researchers to obtain graphene, whereas various of strategies have been developed for the fabrication of TiO2-graphene nanocomposites. As reported by Tu et al., in situ simultaneous reduction-hydrolysis technique was developed for the fabrication of TiO2-graphene 2D sandwich-like hybrid nanosheets (Tu et al., 2013). During the process, GO was reduced to graphene (rGO) by ethylenediamine (En) while Ti (IV) was hydrolyzed to TiO2 nanoparticles and loaded on rGO through Ti-O-C bonds. The abundant surface Ti3+ sites generated from En reduction could trap photogenerated electrons efficiently, thereby decreasing the recombination efficiency of charge carriers. Moreover, the synergism of Ti3+ sites and garphene favors for the generation of C2H6, which is inspiring for C-C coupling during the photoreduction process of CO2. In another work, the suspension of GO and TiO2 in ethanol was ultrasonicated and refluxed to form Ti-O-C bonds, while GO was partially reduced to rGO during the process (Shehzad et al., 2018a). The tightly connected two phases improve charge separation at the heterointerface, while the enlarged light absorption coefficient is attributed to the reduced bandgap energy by the formation the Ti-O-C bonds. As a result, the rGO/TiO2 nanocomposites exhibited greater yields of CH4 (12.75 μmol gcat−1 h−1) and CO (11.93 μmol gcat−1 h−1) than anatase for 4 folds. Theoretical calculation was applied by Olowoyo et al. to investigate the enhanced photocatalytic performance of rGO/TiO2 in reducing CO2 (Olowoyo et al., 2019). Results reveal that the high electron density of rGO has significant influence on the TiO2 bands and endows visible light responsibility of the composite. Moreover, the different electron migration paths within rGO/TiO2 under different light sources were observed. Compared to the electron transfer from TiO2 to rGO under UVA, irradiation by visible light leads to the direct generation of electorns and holes in rGO or TiO2, respectively. Both of the two pathways are efficient for photogenerated charge separation and favor for methanol production. In addition, the large adsorption capacity of CO2 is another feature of TiO2/graphene that contribute to photocatalytic CO2 reduction (
Coupling TiO2 With CNT
Generally, charge transfer along the 1D CNT leads to high separation efficiency of photogenerated e−/h+ pairs and endows superior photocatalytic performance of TiO2/CNT heterojunction. Moreover, CNT can also serve as support to reduce the aggregation of TiO2 nanoparticles, thus resulting in the formation of highly dispersed heterointerface and large exposure of active sites. As reported by Xia et al., the multi-walled CNT (MWCNT)/TiO2 hybrid fabricated via sol-gel method yielded C2H5OH as the main photoreduction product of CO2 under UV light irradiation (Xia et al., 2007). In a further study, MWCNT/TiO2 with core-shell nanostructure was demonstrated to be visible light active (due to the excellent visible light adsorption ability of CNT) that can convert CO2 to CH4 (
Coupling TiO2 With CQDs
As a new class of 0D carbon-based nanomaterial, the excellent photoelectric properties of CQDs, such as wide spectral response range, photo-induced charge transfer ability, up-conversion function and anti-photocorrosion property, make it a promising cocatalyst to enhance photocatalytic performance of traditional semiconductor photocatalyst as TiO2 (
In addition to carbon-based nanomaterials analyzed above, other carbon forms can also combine with TiO2 to obtain heterojunction for photocatalytic CO2 reduction with high efficiency. For instance, Zhang et al. coated TiO2 on electrospun carbon nanofibers to promote active sites exposure as well as charge separation and transfer of the nanocomposites (Zhang J. et al., 2018). Besides, the heat produced by carbon nanofibers due to its photothermal conversion function accelerates the diffusion kinetics of reactants and products during photocatalytic process, thus further enhancing the photoreduction efficiency of CO2. The local photothermal effect induced by carbon species is also highlighted by Wang et al. among the hybrid carbon@TiO2 hollow spheres (Wang et al., 2017). Moreover, the multiple scattering of incident light within the hollow structure improves light utilization of the hybrid (shown in Figure 10) and contributes to improve the quantum efficiency of photocatalytic CO2 reduction. This result indicates that not only component, but also architecture of the heterojunction photocatalysts plays important role in improving photocatalytic performance.
FIGURE 10

(A) FESEM images of TNS, CSTS, T60, T120 and T180, and TEM images of T60, T120 and T180, and STEM image of T60 and the corresponding elemental mapping images of C, O and Ti; (B) Comparison of the photocatalytic CH4 or CH3OH evolution rate of carbon@TiO2 composite samples and P25 (under simulated solar light); and (C) Photoexcitation process of the carbon@TiO2 composite photocatalyst with hollow structure. Reproduced from Wang et al. (2017) with permission from the Royal Society of Chemistry.
TiO2 Based Multicomponent Heterojunction for CO2 Photoreductions
Construction of TiO2-based multicomponent heterojunction to introduce two different functional co-catalysts for efficient VLD photocatalytic CO2 reduction has been widely adopted, in which TiO2 combined with any two of another semiconductor (AS), metal nanoparticles (MNPs) and nanocarbon (C) to form ternary composites is currently the most studied system. Previous research revealed the highest selectivity of Pt for CH4 generation compared to other noble metal cocatalysts (Pt > Pd > Au > Rh > Ag) due to its excellent electron extraction ability that derives high electron density around it and facilitates CO2 photoreduction (Xie et al., 2014). However, the consequent increase in H2 production is unfavorable and should be suppressed to realize further enhanced photoreduction efficiency of CO2. Xie et al. coated MgO amorphous layers on Pt/TiO2 hybrid to improve chemisorption of CO2, which was then reduced to CH4 directly by photogenerated electrons enriched on adjacent Pt nanoparticles with high efficiency, thus benefiting for the selective formation of CH4. The similar function of Cu2O was demonstrated by Xiong et al. from the Pt-Cu2O/TiO2 nanocomposite (Xiong et al., 2017c). Notably, the charge separation efficiency of the ternary system decreased with the increasing amount of MgO, indicating that excess MgO may restrict electrons transfer from TiO2 to Pt. Therefore, TiO2/MNPs/AS ternary heterojunctions with rational designed architecture and efficient carrier migration path are necessary. According to Meng’s research, MnOx and Pt were selectively deposited on the {001} and {101} facet of TiO2 (Figure 11A,B,C), respectively (Meng et al., 2019). The series connection of S-M (Pt and TiO2{101}), facet (TiO2{101} and {001}) and p-n (TiO2{101} and MnOx) heterojunction accelerated migration of photogenerated electrons along the path of MnOx→TiO2{001}→TiO2{101}→Pt while photogenerated holes in the opposite direction (shown in Figure 11D,F). As a result, the separation efficiency of photogenerated charge carriers is greatly improved, so as to the enhanced photocatalytic performance with CH4 and CH3OH as the main products. In another work, Z-scheme heterojunction that is favoring for the recombination of inefficient charge carriers was constructed by coupling TiO2 and ZnFe2O4 using Ag as electron mediator (Tahir, 2020). Superior CO yield (1025 μmol gcat−1 h−1) accompanied with the generation of CH4 (132 μmol gcat−1 h−1) and CH3OH (31 μmol gcat−1 h−1) should be attributed to the enhanced charge separation efficiency under UV light irradiation. It is worth nothing that the magnetic properties of ZnFe2O4 should not be ignored which facilitate the recovery of photocatalyst from solid-liquid suspension, although the solid-gas mode is undertaken in this study. Moreover, Ag could also promote visible light adsorption of the ternary system due to its strong LSPR effect, which had been demonstrated by Xu et al. using MgO-Ag-TiO2 as photocatalyst (Xu and Carter, 2019). In order to further investigate the synergism of the LSPR effect and chemisorption of CO2 on the improvement of photoreduction efficiency of CO2, TiO2/MNPs/AS heterojunctions as Au/Al2O3/TiO2 (Zhao Y. et al., 2018) and Au@TiO2 hollow spheres (THS)@CoO (Zhu et al., 2019) were synthesized. On this basis, MgAl layered double oxides (MgAl-LDO) were developed to provide both Lewis basic sites (MgO) and Lewis acid sites (Al2O3) for CO2 chemisorption and H2O dissociation among the Pt/MgAl-LDO/TiO2 nanocomposite, respectively (
FIGURE 11

SEM images of as-prepared (A) TiO2 and (B) TiO2-MnOx-Pt (TMP); (C) Schematic diagram of selective photodeposition process of MnOx nanoflakes and Pt nanoparticles on anatase TiO2 {001} and {101} facets; Schematic diagram of proposed photocatalytic CO2 reduction mechanism of sample TMP. The relative band energy positions of TiO2, Pt, and MnOx(A) before contact and (B) after contact and under irradiation. Reproduced from Meng et al. (2019) with permission from the American Chemical Society.
In a typical TiO2/C/AS system, nanocarbon is served as electron channel to guide photogenerated electrons flow from TiO2 to the AS while photogenerated holes left in the VB of TiO2, thereby resulting in the spatial separation of photoinduced redox reactions with enhanced CO2 photoreduction efficiency. As reported by Jung et al., mesoporous TiO2 and a few layers of MoS2 were assembled with graphene aerogel via one-pot hydrothermal method to construct a 3D hierarchical structure (
TiO2 Based Phase and Facet Heterojunctions for CO2 Photoreduction
TiO2 Based Phase Heterojunction
Phase heterojunction composed of different crystal phases of the same semiconductor exhibits greater photocatalytic activity than the single-phased photocatalyst (
TiO2 Based Facet Heterojunction
The difference of geometrical and electronic structures between different crystal facets of the same semiconductor results in the distinctness of their photocatalytic activity. Facet engineering has been applied to control the exposed crystal facet of semiconductors, in order to increase the exposure of active sites and promote the adsorption and activation of substrates, so as to achieve enhanced photocatalytic performance. In terms of anatase TiO2, the {101} has the lowest surface energy (0.44 J m−2) among the low-index facets (including {001}, {010} and {101}) and dominant for CO2 adsorption basing on first-principles calculations (Yu et al., 2014). The photogenerated electrons transferred from the {101} of TiO2 to CO2 facilitates its activation and reduction. Moreover, the enriched photogenerated holes on the {001} of TiO2 can accelerate the oxidation reactions. Photocatalytic CO2 reduction over anatase TiO2 with coexposed {001} and {101} facets was reported by Yu et al. for the first time with the propose of “facet heterojunction” concept (Yu et al., 2014). The facet ratio of {001} and {101} can be tuned by adjusting the amount of HF during the fabrication process, as see in Figures 12A,B, while the correspondingly schematic illustration is displayed in Figure 12C. In particular, the formation of facet heterojunction between {001} and {101} contributes to the transfer and separation of photogenerated carriers, which is beneficial to the enrichment of e− and h+ on {101} and {001}, respectively (shown in Figure 12D). As a result, photocatalytic CO2 reduction occurs selectively on the {101} facet, while the optimized photocatalytic performance is realized when the facet ratio of {101} to {001} is 45–55, in which CO2 is reduced to CH4 with a generation rate of 1.35 μmol gcat−1 h−1 (Figure 12E). On this basis, oxygen vacancies were introduced to the {101} and {001} facets coexposed anatase TiO2 for the further enhancement of photocatalytic performance, where TiO2 fabricated via hydrothermal route in the presence of HF was reduced by NaBH4 to generate surface oxygen defects (
FIGURE 12

FESEM images of (A) HF4.5 and (B) HF9; Schematic illustration of (C) tuning the ratio of {101} to {001} facets of anatase TiO2 by adjusting the amount of HF, and (D) charge transfer at the interface of {101}-{001} facet heterojunction of anatase TiO2; (E) Comparison of the photocatalytic CH4-production activity of P25 and the TiO2 samples prepared by varying HF amount. Reproduced from Yu et al. (2014) with permission from the American Chemical Society.
Conclusions and Prospects
This review summarizes the recent advances in the rational design, fabrication and photocatalytic performance of TiO2-based heterojunctions for converting CO2 into solar fuels with water oxidation. Generally, photocatalytic CO2 reduction that mimic the nature photosynthesis of green plants exhibits great potential for the reduction of CO2 level in the atmosphere and storage of solar energy in hydrocarbon fuels, so as to alleviate the impact of energy crisis and climate change on the development of human society. However, some obstacles, such as low solar energy conversion efficiency, slow generation rate and poor selectivity toward reduction products of CO2, and common photocorrosion phenomenon facing the current photocatalytic systems, restricts the practical application of this very promising technology. In recent years, tremendous efforts have been devoted to fabricate TiO2-based heterojunctions, in order to realize enhanced photocatalytic performance for CO2 conversion, thus giving new life to this traditional and systematically studied photocatalyst. Although the composition, morphology, architecture and photocatalytic mechanism of TiO2-based heterojunctions are various, they have much in common that favors for photoreduction of CO2 as follows: 1) the efficient electron transfer at the heterointerface that promotes spatial separation of photogenerated e−/h+ pairs and prolongs their lifetime to participate in the photoinduced redox reactions; 2) the expanded light adsorption range and enhanced visible light responsibility, making it possible for solar-driven photocatalytic CO2 reduction; 3) the enlarged CO2 adsorption capacity due to the high specific surface area with highly exposed active sites that combine CO2 by chemical action, which could also activate the adsorbed CO2 molecules and facilitate hydrocarbon generation; 4) the increase in selectivity toward specific photoreduction products of CO2 is attributed to the contribution of the cocatalysts.
Although considerable progress has been made on TiO2-based heterojunction for photocatalytic CO2 reduction, it is still far from practical application. On the one hand, the formation of multi-carbon products has always been a bottleneck in this field. The study of CO2 photoreduction intermediates combined with in-situ analysis technology and theoretical calculations needs to be more in-depth in order to clarify the formation mechanisms of different hydrocarbons and guide for the rational design of photocatalysts for the generation of multi-carbon product with high selectivity. On the other hand, pre-defined design of the components and their spatial arrangement in the heterojunction for the optimized phtotcatalytic performance is still a great challenge. It is worth nothing that the difference in synthesis conditions limits the flexibility of component selection, which also complicates the synthesis procedure and reduces the yield of expected heterojunction photocatalyst. At the same time, the randomness arrangement of different components in many cases and the variability of the catalyst morphology and structure affect the photocatalytic performance significantly, which also makes it difficult to clarify the contribution of each component and the synergism mechanism. How to overcome the above limitations to select components of the heterojunction based on photocatalytic performance only, and achieve precise control at the structural unit level, thus realizing efficient synergy of each component for photocatalytic CO2 reduction is one of the main directions of future development in this field. To our knowledge, recent advances in DNA origami superlattice structure (Tian et al., 2016;Tian et al., 2020) may provide a possible solution and guide the design and construction of well-ordered heterojunction photocatalysts in the future. Specifically, the precisely control of the topological structure, arrangement sequence, and assembly quantity of each building block (polyhedral DNA frame) during the self-assembly process makes it possible for heterojunction photocatalysts with controllable structure and adjustable performance, which is expected to become the future research hotspot in the field of photocatalytic CO2 reduction. In addition, efficient solar harvesting systems are in great demand to replace artificial light sources with high energy consumption, since efficient photoreduction of CO2 is based on high light intensity. On the one hand, upconversion quantum dots can be introduced into the heterostructured photocatalyst, in which some of the long-waved visible light in the incident light can be converted into short-waved partial that can excite the photocatalyst to generate e− and h+ pairs. On the other hand, focusing lens system can be added to the photoreactor to enhance the concentration of sunlight, then the photocatalyst can operate under higher light intensity and exhibit optimized activity. Although the efficiency of photocatalytic CO2 reduction is far less than that of electrocatalysis, relying entirely on solar energy will become its irreplaceable advantage. Furthermore, the enrichment of CO2 in air will become an important consideration in the design of heterojunction photocatalysts, which meet the needs of practical applications. Fortunately, the research on CO2 storage and controlled release provides the possible solution while the visible light-triggered capture and release of CO2 from stable MOFs become the most promising candidate (Park et al., 2011;
In summary, the heterojunction photocatalysts with well-organized structure, optimized solar energy conversion efficiency, ideal turnover frequency of CO2, and high reduction product selectivity are still the direction of efforts in the future. We hope that this review can inspire new ideas to guide the design and synthesis of high-performance photocatalysts for photoreduction of CO2 into solar fuels, thus accelerating the industrialization process of this very promising technology and providing practical help to alleviate energy and environmental crises.
Statements
Author contributions
KL designed and wrote the review with input from CT, YT, SW, and QM for conceiving, writing, and editing the manuscript.
Funding
This study was supported by Shenzhen Science and Technology Innovation Program (Grand No. GJHZ20190819151807167), Post-doctoral Foundation Project of Shenzhen Polytechnic (Grand No. 6020330008K0), the Fundamental Research Funds for the Central Universities (Grand No. 020514380141), and China Postdoctoral Science Foundation (Grand No. 2020M671437).
Conflict of interest
The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
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Summary
Keywords
TIO2-based photocatalysts, heterostructures, CO2 photoreduction, water oxidation, high efficiency
Citation
Li K, Teng C, Wang S and Min Q (2021) Recent Advances in TiO2-Based Heterojunctions for Photocatalytic CO2 Reduction With Water Oxidation: A Review. Front. Chem. 9:637501. doi: 10.3389/fchem.2021.637501
Received
03 December 2020
Accepted
01 February 2021
Published
15 April 2021
Volume
9 - 2021
Edited by
Ping Yu, Institute of Chemistry, China
Reviewed by
Chang-Yong Nam, Brookhaven National Laboratory, United States
Yuqing Lin, Capital Normal University, China
Limin Zhang, East China Normal University, China
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© 2021 Li, Teng, Wang and Min.
This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.
*Correspondence: Chao Teng, tengchao@szpt.edu.cn; Qianhao Min, minqianhao@nju.edu.cn
This article was submitted to Green and Sustainable Chemistry, a section of the journal Frontiers in Chemistry
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