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Insight on Reaction Pathways of Photocatalytic CO 2 Conversion
Yiou Wang, Enqi Chen, Junwang Tang
ACS Catalysis · 2022 · Review
Abstract
value-added products, taking into account the experimental evidence and theoretical calculation on the surface adsorption, proton and electron transfer, and products desorption. Finally, the remaining challenges in the field, including mechanistic understanding, reactor design, economic consideration, and potential solutions, are critically discussed by us.
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From PubMed Central, U.S. National Library of Medicine, as current on Oct 24, 2026. Paragraph numbers are ours, so an answer can point at one.
Introduction
The atmospheric CO2 content has inevitably increased from 275 ppm to over 400 ppm since the industrial evolution, far exceeding its natural fluctuation (180–300 ppm) over the past 800 000 years because of an emission rate of more than 2 ppm per annum., The reactions emitting CO2, such as the combustion of fossil fuels, could directly release heat and, in most cases, also produce water that is also a greenhouse gas in its vapor form. The IR-active CO2 molecules trap the thermal radiation from the Earth’s surface and the sunlight, raising the global temperature and subsequently liberating even more CO2 by shifting the CO2-carbonate dissolution equilibrium in the oceans. Once the natural carbon-cycle capacity is overwhelmed, an adverse process leads to dramatic climate change and other environmental issues, highlighting the urgent need for artificial approaches to maintain the carbon balance by capturing CO2 for the carbon-neutral economy.
The carbon on Earth simply moves between different reservoirs because of geological and geochemical processes as well as human activities, while the total carbon amount has remained constant (Scheme 1). The new technology for CO2 utilization should at least be carbon-neutral either via exergonic pathways or endergonic ones but driven by renewable energy sources. Inspired by the fact that the majority of carbon on the Earth’s surface is stored in the form of carbonates, scientists have developed thermodynamically favorable CO2-to-carbonate mineralization technologies. Recently, the concept of converting a carbon-containing fuel into carbonates and carbon-free hydrogen was reported. Meanwhile, inspired by natural photosynthesis, scientists have also made significant progress in uphill reactions to fix CO2 into high-value fuels with the input of energy from sunlight. Such sustainable solar fuels are attractive with a satisfactory density of energy stored in their chemical bonds (e.g., 20 MJ/kg for methanol), which are significantly higher than current batteries (∼0.1–0.7 MJ/kg) and able to be released on demand without additional carbon emission.− The storage of almost inexhaustible solar energy in CO2-reduction fuels will significantly contribute to balance the carbon-cycle and address the issues of carbon-neutral energy supply, leading to the concept of the photocatalytic process for CO2 reduction.
The earliest demonstration of photoassisted CO2 reduction in water dates back to the late 1970s when the Pt-SrTiO3 was used to convert gaseous water and CO2 to methane, as reported by Hemminger et al., and many semiconductors (TiO2, ZnO, CdS, GaP, and SiC) were also shown to reduce aqueous CO2 to formic acid, formaldehyde, methanol, and methane by Inoue et al., Since then, many efforts have been devoted not only to improve the efficiency of CO2 photoconversion or the related but also to tune the selectivity of a specific product., Moreover, the formation of C2+ products has attracted emerging attention because of their high value compared with their C1 counterparts., Despite the advancement made in the past decades, the performance of CO2 photoconversion is still unsatisfactory, far from the target 10% solar-to-fuel efficiency, because of a few intrinsic reasons.The difficulty in activation of inert CO2. Owing to the closed-shell electronic configuration, linear geometry, and D∞h symmetry, it requires −1.9 V potential (vs NHE at pH 7) to activate CO2 and to form an anion radical CO2–, which the majority of semiconductors could hardly provide except for a few reports (e.g., poly p-phenylene in trimethylamine).− A possible solution to lower the barrier to the reduction reaction is to adsorb CO2 on the surface of catalysts and then reduce CO2 together with protons, which usually requires the loading of active cocatalysts or the engineering of surficial defects such as oxygen vacancies.,,,The challenging multiple-electron kinetics. It is commonly believed that CO2 reduction is a process via multi-proton and multi-electron transfer, lowering the CO2 reduction potentials close to that of proton reduction, making it much more difficult than the two-electron proton reduction process to hydrogen. Except for some reports of molecular catalysts, it is challenging to validate whether the reactions proceed via a simultaneous multi-electron transport process or through a cascade of one-electron steps, where the first electron transfer seems to be the limiting step., Another question is whether the lifetime of the charge carriers matches that of the surface reactions of interest.Unfavorable thermodynamics of CO2 reduction by water. Opposite to the exothermal combustion of fuels, the production of solar fuels from CO2 and water is endothermal (e.g., Gibbs free energy of 818.3 kJ/mol for CH4 and 702.2 kJ/mol for CH3OH). Although using hydrogen instead of water could turn CO2 reduction into exothermic reactions hence having demonstrated much-enhanced activity, these thermal catalytic processes usually proceed under higher temperatures (>150 °C) even promoted by light, requiring an additional step and energy for water electrolysis to hydrogen. Thus, hydrogenation systems and those using sacrificial hole scavengers will not be included in this Perspective as they are debatably sustainable to some extent. As the water oxidation half-reaction is very sluggish because of the four-hole chemistry and the likely oxidation of the reduction intermediates before the multi-electron carbon products are generated, using water to reduce CO2 to valuable chemicals is exceptionally challenging. In short, to overcome the obstacles mentioned above for CO2 photoreduction, besides the commonly existing issues for photocatalysis such as light-harvesting, one has to carefully tailor the photocatalysts, cocatalysts and the reaction conditions based on the fundamental understandings.Selectivity toward preferable products. Various products could be obtained from CO2 conversion while tuning the selectivity remains the major challenge. It should be noted that not all of the products are value-added chemicals if the cost of CO2 capture is taken into consideration (Scheme 2). For example, the commonly observed CO (with low purity) and CH4 are economically unfavorable due to their relatively low market price. The most profitable C1 product is formic acid, which unfortunately has a low energy content. Methanol and C2+ products are more attractive because of their outstanding market price, market demand, and energy content. However, because of the lack of molecular-level understanding of reaction mechanisms, the selectivity control to preferable products is still challenging.
The difficulty in activation of inert CO2. Owing to the closed-shell electronic configuration, linear geometry, and D∞h symmetry, it requires −1.9 V potential (vs NHE at pH 7) to activate CO2 and to form an anion radical CO2–, which the majority of semiconductors could hardly provide except for a few reports (e.g., poly p-phenylene in trimethylamine).− A possible solution to lower the barrier to the reduction reaction is to adsorb CO2 on the surface of catalysts and then reduce CO2 together with protons, which usually requires the loading of active cocatalysts or the engineering of surficial defects such as oxygen vacancies.,,,
The challenging multiple-electron kinetics. It is commonly believed that CO2 reduction is a process via multi-proton and multi-electron transfer, lowering the CO2 reduction potentials close to that of proton reduction, making it much more difficult than the two-electron proton reduction process to hydrogen. Except for some reports of molecular catalysts, it is challenging to validate whether the reactions proceed via a simultaneous multi-electron transport process or through a cascade of one-electron steps, where the first electron transfer seems to be the limiting step., Another question is whether the lifetime of the charge carriers matches that of the surface reactions of interest.
Unfavorable thermodynamics of CO2 reduction by water. Opposite to the exothermal combustion of fuels, the production of solar fuels from CO2 and water is endothermal (e.g., Gibbs free energy of 818.3 kJ/mol for CH4 and 702.2 kJ/mol for CH3OH). Although using hydrogen instead of water could turn CO2 reduction into exothermic reactions hence having demonstrated much-enhanced activity, these thermal catalytic processes usually proceed under higher temperatures (>150 °C) even promoted by light, requiring an additional step and energy for water electrolysis to hydrogen. Thus, hydrogenation systems and those using sacrificial hole scavengers will not be included in this Perspective as they are debatably sustainable to some extent. As the water oxidation half-reaction is very sluggish because of the four-hole chemistry and the likely oxidation of the reduction intermediates before the multi-electron carbon products are generated, using water to reduce CO2 to valuable chemicals is exceptionally challenging. In short, to overcome the obstacles mentioned above for CO2 photoreduction, besides the commonly existing issues for photocatalysis such as light-harvesting, one has to carefully tailor the photocatalysts, cocatalysts and the reaction conditions based on the fundamental understandings.
Selectivity toward preferable products. Various products could be obtained from CO2 conversion while tuning the selectivity remains the major challenge. It should be noted that not all of the products are value-added chemicals if the cost of CO2 capture is taken into consideration (Scheme 2). For example, the commonly observed CO (with low purity) and CH4 are economically unfavorable due to their relatively low market price. The most profitable C1 product is formic acid, which unfortunately has a low energy content. Methanol and C2+ products are more attractive because of their outstanding market price, market demand, and energy content. However, because of the lack of molecular-level understanding of reaction mechanisms, the selectivity control to preferable products is still challenging.
Apart from the four key factors as mentioned above, the core of CO2 photoreduction lies in the selection of semiconductor photocatalysts. The progress of semiconductor photocatalyst development has been heavily summarized by many comprehensive reviews.,,− Also, the strategies to design novel photocatalysts for CO2 reduction resemble those for water splitting, which could be found in broad literatures (Scheme 3).− For example, Li et al. summarized the selectivity for photocatalytic reduction of CO2 over different cocatalysts. Briefly, Pd, Pt, or Au are more favorable for CH4 production; Ag for CO, CH4, or CH3OH; Cu for hydrocarbons; and Cu2O, RuO2, or NiOx for CH3OH production. Therefore, complementary to these reviews on photocatalysts’ development, here we aim to discuss the possible reaction pathways and mechanisms on the basis of our understandings in this Perspective, including how to design photocatalysts and how to obtain this fundamental information by spectroscopies, as well as the principles for various products. Furthermore, we propose challenges facing this field, such as the characterizations needed to validate and understand the experimental process and pathways to practical applications.
REACTION PATHWAYS AND POSSIBLE PRODUCTS
Scheme 4 lists the redox potential of various products from photocatalytic CO2 conversion and the band alignment of a few representative photocatalysts. To determine the selectivity and efficiency of the process, gas chromatography coupled with mass spectrometry (GCMS) is commonly used to quantify the products, while for nonvolatile ionic formate or oxalate products, ion-exchange chromatography is necessary. Understanding the exact reaction mechanism of CO2 photoreduction relies on evidence from experimental and theoretical methods. Infrared spectroscopy (IR) is helpful for surface chemistry studies, and electron paramagnetic resonance (EPR) is an essential tool to reveal the mechanism via the detection of paramagnetic unpaired electrons of the intermediates. The charge carrier dynamics could be analyzed by transient absorption measurements, together with modeling. Important information regarding adsorption and kinetics could also be provided by electrochemical measurements and theoretical computation.
In an earlier review, Habisreutinger et al. had summarized three possible mechanisms for the photocatalytic formation of five C1 (CO, HCOOH, CH2O, CH3OH, CH4) and some C2 products from CO2 on TiO2, namely the formaldehyde pathway, the carbene pathway, and the glyoxal pathway. These different possibilities start with the binding modes of CO2 on the surface of catalysts, including oxygen coordination, carbon coordination, and side/mixed coordination. On the basis of these, we proposed a comprehensive description of pathways (Scheme 5). The pathways are directed by whether the following reaction occurs via electron transfer, proton transfer (sometimes hydroxyl transfer) or concerted electron–proton transfer. An intermediate molecule in one pathway could be the final product of another pathway if it fast desorbs from the surface of the catalysts before further steps take place. Since the final products from the experiments are the most direct clues, we thus discuss the possible mechanistic details guided by respective products and the issues open to be elucidated.
As mentioned above, using water to reduce CO2 is the ideal and sustainable process, which includes two half-reactions, water oxidation (eq 1) and multi-electron reduction of CO2. The following details all these reduction processes, involving the production of C1 (e.g., formic acid, carbon monoxide, formaldehyde, carbon, methanol, and methane) and C2 products (e.g., oxalic acid, acetic acid, acetaldehyde, ethanol, ethylene, ethane) by photocatalysis.
Two-Electron Reduction Process
The two-electron reduction process produces CO and HCOOH on the basis of eqs 2–5, and HCOOH production happens together with water oxidation (eq 1).
Carbon monoxide plays a crucial role in the Fischer–Tropsch synthesis and carbonylation of alkenes, while formic acid is a necessary preservative and antibacterial agent in livestock feed. Regarding the numbers of electrons needed, CO and HCOOH are kinetically the most accessible products from CO2, while thermodynamically, both are uphill reactions. Meanwhile, it should be noted that the minimal potential for CO2 reduction decreases with the increase of the number of electrons involved in the products. For example, photocatalytic CO2 conversion to CO or HCOOH requires slightly more negative potential than that to CH4.
CO, as shown in Scheme 5, is a product, a byproduct or an intermediate in CO2 reduction. In detail, CO is an intermediate in the carbene pathway after anchoring the C atom of CO2 to the surface of the catalysts. One proton attacks the O atom in CO2 to form COOH radicals in the presence of the first electron, followed by an immediate cleavage of the C–OH bond, which releases CO and water if not proceeding further., The selectivity of this process could be controlled by the binding strength of CO on the surface of a catalyst. CO can be a poison if it binds too strongly to the metal, while CO desorbs as a final product before further reduction occurs if the binding is too weak. Studies have shown that the suitable binding energy of CO on the copper catalyst and the high coverage ensures the formation of more reduced products and inhibits the competitive hydrogen evolution. In the glyoxal pathway, CO is a byproduct when the C2 intermediates decarbonylize to form methanol or methane, which agrees well with the literature that CO is commonly detected together with methanol and methane products. The oxidation of organic products such as formaldehyde and methanol by photoholes also results in CO, which we observed. Such backward reactions convert the kinetically more challenging reduction products to a two-electron product CO, which can be mitigated by hindering the adsorption of the formaldehyde and methanol on the oxidation sites.,
It should be noted that the selective conversion of captured CO2 toward formic acid has been identified as one of the relatively profitable processes, although the market demand and the energy content are low (Scheme 2). Formate might be the most accessible product as all three binding modes can possibly lead to formate production (Scheme 5). Moreover, it only requires two electrons and one proton to form formate, and the breaking of the C–O bond does not occur during the formation of HCOOH. So far, the benchmark efficiency in photocatalytic CO2 reduction was achieved in a formate production system reaching a solar-to-formate conversion efficiency of 0.08 ± 0.01% on a Z-scheme system of SrTiO3:La,Rh/Au/BiVO4:Mo modified with molecular cocatalysts (Scheme 6).
HCOOH has been previously proposed as an intermediate in the formaldehyde pathway via the surface adsorption involving O, including bidentate and monodentate O coordination or the mixed C–O coordination. EPR studies by Shkrob et al. demonstrated that only when CO2– radical is doubly bound through its oxygens to the metal ions at the surface can this radical be further reduced to formate. Otherwise, the reduction is stalled. The bidentate binding of the CO2 via both O atoms results in the proton attaching to the C atom in CO2– to form the formate HCOO radical, which further accepts one electron and proton to form HCOOH, being a favored reaction in water with a high dielectric constant., Regarding the further reduction of formic acid, Koci et al. showed the profiles of produced CH4 and CH3OH disagreed with the formaldehyde pathway, as CH3OH is not observed as an intermediate of CH4. Hori et al. also suggested that formate is more likely the terminal product for electrochemical CO2 reduction on copper except for systems with very high concentrations, high cathodic bias, and highly acidic or basic electrolytes. Therefore, we did not wholly draw the proposed debatable formaldehyde pathway (gray dashed lines) in Scheme 5. Instead, we summarize a new formyl pathway from the literature discussed in detail below.
Four-Electron Reduction Process
The four-electron reduction process produces HCHO and C on the basis of eqs 6–9, while HCHO production requires water oxidation (eq 1).
Formaldehyde is helpful for disinfection and is a precursor to more complex compounds in industry. In the proposed formyl pathway (Scheme 5), if the catalyst has moderate adsorption strength, the C-anchored CO intermediate can accept one electron while a proton attacks the C atom, forming the formyl intermediate (CHO), as shown in Scheme 5, which could further be converted to CH2O with the other proton–electron pair. By calculation of Gibbs free energy differences and the energy barriers, Cheng et al. showed that adding the proton to C (forming CHO) is preferable to adding to O (forming COH) on Cu (100), which leads to the reaction toward the formyl pathway over the carbene pathway. Formaldehyde could then be formed after receiving another pair of electron and proton. If the formaldehyde is not desorbed, the path further leads to CHx species that can produce methane, as observed experimentally. Cheng et al. also calculated that although CH2O has been detected as a product, the energy barrier of CH2O formation is 0.47 eV higher than for CHOH and hence is kinetically unfavorable. In other words, reactions on Cu (100) should more likely have CHOH as an intermediate. CH2O is detectable as a product only if it is not strongly chemically bonded to the oxide surface. Nie et al. suggested that the COH intermediate more likely exists on Cu (111), since the CHO intermediate needs to overcome a significant energy barrier, blocking further reactions to produce CH3OH and CH4 by calculation study. Therefore, it is concluded that the exposed surface facets dominate the products and pathways.
However, Park et al. proposed an oxygen vacancy mediated mechanism to release formaldehyde on an rGO-grafted NiO-CeO2 sample (Scheme 7). The CeO2 surface and CO2•– radicals were monitored by in situ X-ray absorption near edge structure (XANES), in situ attenuated total reflectance infrared (ATR-IR) and in situ EPR, and then a detailed description of the multistep CO2 photoreduction process was illustrated. Briefly, CO2 capture occurs at the oxygen site adjacent to oxygen vacancy. One O atom from the CO2 molecule fills the vacancy site, and the C–O bond is broken. The formation of CHO, CHOH, and CH2OH occurs through a few electron and proton transfer processes, and then formaldehyde is produced. The formation of oxygen vacancies is due to solar light illumination, which could be validated by in situ XANES spectroscopy. Hence the catalytic process is sustainable, and this also indicates that a combination of these characterization techniques can reveal the mechanism in a straightforward way.
Carbon could also be formed as a four-electron product in the carbene pathway. When the proton attacks the O atom of the adsorbed CO followed by eliminating one OH– (or with another proton to eliminate one H2O), carbon radicals are generated (Scheme 5). Such a process has been verified by the signals of the C residue on the surface detected by EPR spectroscopy. DeWulf et al. also observed graphitic carbon species by X-ray photoelectron spectroscopy (XPS) and Auger electron spectroscopy (AES). Such surface carbon product or intermediate could further be reduced to CH, CH2, and CH3 over relatively low barriers.
Besides, three theoretical models have been proposed to investigate the CO2 reduction process via the formyl pathway, including implicit solvent models, explicit solvent models, and the H-shutting model. In the implicit solvent model, a continuous description of the ions is included, whereas the explicit solvent model offers an atomistic-level picture of solvation and cation effects. Furthermore, the H-shuttling model considers that water molecules shuttle the protons, and CHO radicals are formed via a direct transfer of H. However, on the Cu surface, explicit calculations concluded that all steps after the formation of CO radicals are proton–electron transfers. The inconsistencies in the explanation for CO2 reduction pathways come from both different study methods and the intrinsic complexity of the reaction mechanism. Clearly, more efforts are required to clarify this ambiguous pathway, and the combination of state-of-the-art operando spectroscopies can provide a strong potential to acquire the solution to this.
Six-Electron Reduction Process
The six-electron reduction process produces CH3OH on the basis of eqs 10 and 11, together with water oxidation (eq 1).
In the suggested “methanol economy” by Olah et al., methanol could be a crucial alternative to fossil fuels as it is a suitable energy-storage material, a fuel, and a feedstock to synthesize hydrocarbons and their products. In the context of the “hydrogen economy”, methanol is also regarded as a promising liquid medium to store hydrogen safely and efficiently before use. Methanol contains 40% more hydrogen mass density (kg H2 per m3) as well as over 80% more volumetric energy density than liquid H2. In contrast, the energy for compression and liquefaction of H2 accounts for 10–15% and 30–40% of the energy contained, respectively.− Methanol also has a suitable balance between market demand, market price, and energy content (Scheme 2). Therefore, photocatalytic CO2 conversion by water to methanol with a high selectivity has attracted substantial attention. The reduction potential (−0.38 V vs NHE at pH = 7) is slightly more positive than proton reduction (−0.41 V vs NHE at pH = 7); hence, a large group of photocatalysts reported for hydrogen production could be applied. However, the 6-electron process of methanol generation requires an exceptionally prolonged lifetime of charge carriers for accumulation. Moreover, the oxidation of methanol with holes (∼10 ns) on TiO2 is kinetically much more favored over water oxidation (up to ∼1 s), making the continuous production of methanol with high select ivity a significant challenge.
In the carbene pathway, the C radicals continue to accept three electron–proton pairs, forming the methyl CH3 radicals. Methanol could then be produced if the methyl CH3 radical recombines with a hydroxyl radical (•OH). In this case, methanol is not intermediate to CH4, and formaldehyde was not formed at all. Electrochemical studies also support that methanol could not be reduced to form methane., Instead, CH3OH is a competitive product to CH4, depending on a few factors such as the hydrophilicity of the surface and water amount., The kinetic model of such a mechanism agrees with the experiment results of methanol and methane production reported by Tan et al. and Koci et al. based on TiO2., CO is commonly observed in experiments with methanol as the major product since CO is an intermediate in this mechanism.
In another C-coordinated formyl pathway, the adsorbed CO was not dehydrated to C radicals but was attacked by electron–proton pairs. Interestingly, despite the variety of proposed paths how the electron and protons are bought to the CO radical intermediate, namely, CHO/COH or CHOH/CH2O, it seems that they eventually all lead to CH2OH and CH3O, as shown in Scheme 5, which possibly desorb as a CH3OH, although not all the intermediates are evidenced by experiments., Lum et al. carried out an electroreduction experiment of C16O2 in H218O on various Cu surfaces to identify the mechanism and found that CH3OH was not 18O rich, and it was only detected on Cu (111). This interesting experiment shows the face-dependent selectivity of CO2 reduction and, more importantly, indicates that the O in CH3OH comes from CO2 at the beginning instead of water. This result suggests that the formyl pathway or glyoxal pathway is more likely for methanol production than the carbene pathway, where OH radicals might come from water. Cheng et al. reported that at low pH, the intermediate CHOH underwent the dehydrating process, which led to the formation of CH3 radicals and then a higher selectivity to CH4 over CH3OH. In contrast, a high pH, more hydrophobic environment, weak hydrogen bonding solvent, or gaseous phase benefits the selectivity toward CH3OH. In fact, methanol is very often a competitive product to CH4 in all the proposed pathways in Scheme 5, including the glyoxal pathway. It should be noted that the production of methanol is very challenging, as the final step of releasing methanol in both the carbene pathway and formyl pathway require hydroxyl radicals, and the glyoxal pathway involves photoholes, both of which are highly oxidative. The upper routine to methanol in the formyl pathway (Scheme 5), where the intermediates are continuously bonded via carbon to avoid the oxidation of intermediates, prefers to produce methanol with high selectivity.
The stable production of methanol not only relies on the sufficient transport of electron–proton pairs but also depends on whether the produced methanol could be protected from the strongly oxidative nature of photoholes. The backward reaction of methanol oxidation could be determined by the CO yield in the products. A strategy to avoid such an issue is to suppress the adsorption of the methanol on these oxidation sites and to promote the kinetically sluggish oxidation of water against methanol. One can know whether the holes oxidize water or methanol by measuring stoichiometry between reduction and oxidation products during CO2 reduction. We have recently reported a unique hole-accepting carbon-dots cocatalyst (CD), where water instead of methanol selectively adsorbs (Scheme 8). Such CD prolongs the lifetime of charge carriers on pristine and oxygen-doped carbon nitride photocatalysts by 6–8 folds, resulting in the almost unity selectivity to methanol with stoichiometric oxygen production and internal quantum yields (IQYs) of 2–6% at 420 nm., A transient absorption spectroscopic investigation shows that extraction of holes by the CD is critical for the remarkable performance. Under visible light, methanol can be readily oxidized to CO by photoholes of carbon nitride (CN), while on the CD-decorated CN, no CO was detected, consistent with that methanol could not be readily adsorbed on the surface of CD where holes accumulate, and photooxidation of water occurs.
Eight-Electron Reduction Process
The eight-electron reduction process produces CH4 on the basis of eqs 12 and 13, together with water oxidation (eq 1).
Methane is not only fuel but also a precursor for syngas, hydrogen, and methanol via its reforming. The methane production requires the least negative reduction potential but the most significant amount of electrons in C1 products. As discussed above, the carbene pathway for methane formation is more plausible than the formaldehyde pathway (Scheme 5) via the acceptance of four electron–proton pairs on the C radicals (Scheme 5). In such a case, CO is an intermediate, and methanol is a competitive product. A low pH in an aqueous solution promotes the selectivity toward CH4, which could also be beneficial via the modification of surface hydrophilicity by deposition of, for example, Pt NPs. In the formyl pathway toward CH3OH, the CH3O intermediate is found using the explicit water model not to form CH4 because of the significant barrier for proton–electron transfer from CH3O to CH4 + O. The protonation of *CO to *CHO is the rate-determining step, which is followed by a series of proton–electron transfers to form *CHOH, *CH, *CH2, *CH3, and finally CH4.
Surface oxygen vacancies are commonly used strategies to modify a photocatalyst. Ji et al. proposed a mechanism for the perfect and defective surfaces by theoretical calculation (Scheme 9). They found that a fast-hydrogenation path can occur at both the surface Ti atoms and the oxygen vacancies, while the oxygen vacancies are more active than the surface Ti atoms for the reaction. The fast-hydrogenation path at the oxygen vacancies combines the hydrogenation and deoxygenation paths. This pathway agrees with the experimental results because CH3OH and CH4 often appear simultaneously and explain the possible formation of formic acid and formaldehyde.
As discussed above, the existence of more active intermediates, including formaldehyde and methanol in the presence of highly oxidative photoholes, contradicts the formaldehyde pathway for CH4 formation, in that one-electron reduction of these molecules in the reaction is energetically prohibitive. Shkrob et al. found that reaction barriers for further reduction could be significantly lowered by joining two carbon atoms and proposed to follow the glyoxal (CHO)2 pathway toward CH4 involving a number of C2 compounds (Scheme 10). In this pathway, the critical intermediate is the glyoxal (or ethanediol), produced from the dimerization of formyl radicals CHO radicals (Scheme 5). Because of its π-conjugation, glyoxal is still a much more efficient electron acceptor than formaldehyde, which can be step-by-step reduced to glycolaldehyde (HOCHCHO), acetaldehyde (CH2CHO), and acetaldehyde. These C2 molecules can be further oxidized to an unstable acetyl radical, which undergoes decarboxylation to a methyl radical. The recombination of the methyl radical with a hydrogen atom forms CH4. Formate, methanol, and formaldehyde are intermediates all formed in this pathway and serve as sacrificial hole scavengers. The glyoxal pathway will be further discussed later.
The representative examples of photocatalytic systems of CO2 reduction to C1 products have been summarized in Table 1. Considering the economic potential of the C1 products such as formate/formic acid and methanol, the efficient systems for these products are of particular interest. For example, the highest solar-to-fuel efficiency of 0.08 ± 0.01% (solar-to-formate) measured under the solar simulator was achieved on the molecular cocatalyst coated on a Z-scheme particulate sheet (phosphonated Co(II) bis(terpyridine) and RuO2 catalysts modified SrTiO3: La, Rh|Au| BiVO4: Mo). The benchmark system for CO2 photoreduction to formic acid was based on a gas-permeable metal–organic framework (MOF) with an apparent quantum efficiency (AQE) of 15.76% at 420 nm, at the porous gas–solid interfaces with a near-unity selectivity. Such a high quantum efficiency is also the highest among most systems for the C1 products, suggesting that the metal–organic complexes play a significant role in CO2 reduction. More examples of metal complex photocatalysts could be found in other reviews. The highest internal quantum efficiency at 420 nm toward methanol was measured on carbon dots/oxygen-doped carbon nitride. The key to maintaining a reasonable efficiency of methanol is to mitigate overoxidation of methanol product to CO.
Pathways to C2 Products
The direct photoconversion of CO2 to C2 products is more attractive because of their significantly higher market price and energy content per carbon compared with the C1 products (except for methanol in Scheme 2). The formation of the C–C bond by dimerization of C1 intermediates on the surface of catalysts is the key to further producing C2 products. For example, the pathways toward ethylene or ethane involve the coupling of carbene intermediates (CH2, CH3) in the carbene pathway while the dimerization of formyl (CHO) in the glyoxal pathway can result in a variety of C1 and C2 products (Scheme 5). These pathways mostly require multiple electrons and protons, which will be favorable on the surface with an increased density of charge carriers and protons. Also, the binding of intermediates on the surface of the catalysts must be sufficiently strong to reach the C2 products instead of desorbing them early as C1 products such as CO and CH2O. C1 products such as CO, CH4, and CH3OH can also be byproducts of these processes. All these processes again share the water oxidation half-reaction (eq 1). The following lists the chemical eqs (eqs 14–25) for C2 products with 2 to 14 electrons, respectively.
Two-Electron Reduction Process
The two-electron reduction process produces (COOH)2 on the basis of eqs 14 and 15.
Eight-Electron Reduction Process
The eight-electron reduction process produces CH3COOH on the basis of eqs 16 and 17.
Ten-Electron Reduction Process
The 10-electron reduction process produces CH3CHO on the basis of eqs 18 and 19.
Twelve-Electron Reduction Process
The 12-electron reduction process produces CH3CH2OH and C2H4 on the basis of eqs 20–23.
Fourteen-Electron Reduction Process
The 14-electron reduction process produces C2H6 on the basis of eqs 24 and 25.
Since the pathways to C2 products are believed to involve both multi-electron coupled proton transfer and the C–C coupling processes, the reactions are generally more challenging, and fewer reports have achieved high selectivities. Different from the reactions toward C1 products, which are mostly proton-coupled one-carbon two-electron processes, the pathway to C2 products proposed by Shkrob et al., namely the glyoxal pathway (Scheme 10), is a mainly one-electron two-carbon process through a glyoxal intermediate (e.g., on TiO2) as evidenced by EPR. The reason to postulate an alternative mechanism is that no evidence of one-electron reduction intermediate (e.g. formate, formaldehyde, or methanol) has been observed in EPR. As mentioned above, these intermediates are more likely to be oxidized than reduced. However, the glyoxal intermediate is a strong electron acceptor, which is more facile to be reduced than oxidized. Moreover, the glyoxal pathway can provide mechanisms for C1 products such as CO, CH4, methanol, formate and formaldehyde and explain the possible C2 products observed, including acetaldehyde and methylformate.
As shown in Schemes 5 and 10, different from the de–OH– step after receiving one proton in the carbene pathway, the crucial step in the glyoxal pathway is the dehydration step after getting three protons (or de-OH– step after accepting two protons), forming formyl radicals (HC*O). Then the formyl radicals dimerize to yield glyoxal, which is reduced to trans-ethan-1,2,-semidione (HO-C*H-CHO), glycolaldehyde (HO-CH2-CHO), and vinoxyl (*CH2-CHO) radicals. The vinoxyl radical could be further converted to acetaldehyde (CH3CHO) or decarbonylized to *CH2OH, which is the precursor for methanol (CH3OH). The acetaldehyde could be further oxidized to acetic acid or undergo decarbonylation to form methyl radicals (*CH3), which leads to the formation of methane (CH4). These decarbonylation processes release carbon monoxide (CO). In this case, CO is a byproduct commonly observed in CH4 and CH3OH production.
The most distinct difference between the glyoxal cycle and other pathways is that the former involves not only proton-coupled electron transfer but also oxidation steps. Such pathways are not possible in the absence of holes, for example, at the cathode in the electrocatalytic system. However, the existence of holes results in the production of CO rather than C2 products. Therefore, if one targets value-added C2 products, the oxidative conditions should be mitigated. Another interesting difference is that the glyoxal pathway has some recycling steps where some of the intermediates (e.g., CH3OH and CH2O) serve as hole scavengers, hence replenishing the pool of formyl and hydroxymethyl radicals. Compared with C1 products, glyoxal and methanol have the same required electrons with the number of 6, and the acetic acid and glycolaldehyde have the same electrons needed with the number of 8 as methane. The production of acetaldehyde and ethylene glycol need 10 electrons, while ethylene and ethanol need 12 electrons. It should be noted that the 10-electron product acetaldehyde is an intermediate for an 8-electron product CH4 and a 2-electron product CO, which are much cheaper. It is not economically favorable to oxidize acetaldehyde to CH4 and CO, considering the high numbers of demanded electrons and the low price of methane in the market. It is preferable to produce the C2 products with those electrons. How CO2 molecules bind on the surface of the catalysts usually determines the following steps for various possible products. In the pathways to C2 products, C–C, C–O and single C bindings probably exist at the initial stages when forming glyoxal intermediates, and the coordination might rearrange to O–O binding during the reaction. However, it seems that a few binding modes and the following steps all can lead to products including glycolaldehyde, acetaldehyde, ethylene glycol, ethylene, and ethanol.
Park et al. reported a CdS/(Cu-TNT: NaxH2–xTi3O7) for photoconversion of CO2 and water into C1–C3 hydrocarbons (e.g., CH4, C2H6, C3H8, C2H4, C3H6) under visible light without the detection of CO or H2 (Scheme 11). It could go through an F–T process consuming hydrogen and CO. They also proposed that the bidentate binding of O=C=O to specific reactive surface sites reduced the energy barrier for conduction band electron transfer to CO2. The formate radical eliminates an O2•– radical, forming a methyl radical. The methyl radical (CH3•), as observed by ESR, was trapped by the copper on the surface of TNTs and then self-reacts to produce ethane. This pathway indicates that the C–C coupling of methyl radicals on the surface of photocatalysts is crucial for the production of C2+ products such as ethane.
Regarding the C2H6 formation on the surface of Pt-graphene/defect-induced TiO2, where CO2 adsorption takes place upon abundant Ti3+/VO sites through the O atom of CO2. An alkaline surface is favorable for C2H6 formation by significantly improving the activation and dissociation. Electrons and holes accumulate on Ti3+ and graphene, respectively, with Pt accelerating electron extraction. Graphene scavenges water to supply sustained protons and benefits the stabilization of •CH3, thus promoting C2H6 formation, although CH4 is also a major product.
Hori et al. and Schouten et al. showed that Cu (111) leads to lower onset overpotentials for both CH4 formation and C2H4 formation, while the dimerization of CO leads to C2H4 as the product on Cu (100)., The dimerization of CO is followed by a few steps which are similar to the glyoxal pathway, except that the intermediate (CH2CHO) changes from C-coordination to O-coordination. CH2CHO• could further produce C2H4 or CH3CH2OH. It should be noted that these reports are based on studies on the electrochemical reduction of CO2, and the pathways to C2 products have not been observed in photocatalytic research.
There is also a possibility that C2 products can be produced via the carbene pathway (Scheme 5). In this pathway, another carbene radical might attack the formed CH4 or CH3OH to make C2H4 or C2H6. Other products, including C3 and C3+, could also be obtained if more carbene radicals are involved in such a mechanism but are hardly reported. Kuhl et al. have proposed an enol-like intermediates pathway. However, how the enol (e.g., C2H4O3, C3H6O2) is formed on the surface of catalysts remains unclear. Strategies that increase the density of charge carriers and protons, tune the surface adsorption/desorption, and modify the surface acidity and alkalinity are believed to promote the reaction toward C2+ products, including using a larger number of photon flux and higher energy, cocatalysts, SPR effects and surface defects.
Most of the C2 products are valuable products. As summarized in Table 2, the benchmark quantum efficiency for C2 products is 22.4% at 385 nm and 13.3% at 420 nm (CO2 to acetaldehyde with a 98.3% selectivity) achieved on locally crystallized carbon nitride. Liu et al. used DRIFT and theoretical calculation to prove that an amino-2-propanol-assisted hydrothermal treated carbon nitride had strong bonding with the *OCCHO group, which is favorable to a C–C coupling process and changes the reaction pathway to form CH3CHO instead of HCHO. The highest quantum efficiency for ethanol was 3.5% on AgBr–N-doped carbon nitride. While the activity and selectivity for ethylene and ethane are generally much smaller, which might result from the large numbers of electrons needed for these products (12–14 electrons).
CHALLENGES AND OUTLOOK
We have discussed the detailed potential pathways toward various products, including the well-established carbene pathway, glyoxal pathway and a formyl pathway. The reaction pathway and consequently the product selectivity of photocatalytic CO2 conversion highly depends on the surface chemistry of adsorption of CO2 and desorption of intermediates on the surface of photo/cocatalysts, which has been thoroughly summarized in other reviews (Scheme 12).,,,,, Other factors including crystal facets, surface poisoning phenomena, which are closely related with the bonding modes and strength as discussed above, could also influence the reactivity and selectivity.,,
The key facts of these pathways are summarized in Table 3 regarding different profiles of product distribution. For example, formate can be a promising product because it is both economically beneficial and kinetically easy to produce. However, CO exists in all the pathways. Based on the amount and production profile, the possible mechanism could be inferred. For example, if the amount of CO is minor compared with other main products, it is likely an intermediate or an oxidation product from, for example, methanol. If the amount of CO is comparable to methanol or methane, the reaction is most likely via the glyoxal pathway. Methanol and methane are always competitive products in these pathways, but methanol is more desired in the aspect of market price and transportation, providing its further oxidation could be mitigated. However, this is challenging because the final step of releasing methanol in a few pathways involves photoholes or hydroxyl radicals, which are highly oxidative. Methane requires multi-electrons (8 e–), but its price is even below the cost of capturing CO2. If the reaction goes through the glyoxal pathway, terminating the products at C2 before the decarbonlization is more meaningful, rather than the decomposition of the C2 to unprofitable CO and CH4. Another pathway to C2+ products via carbene coupling is promising as it has the potential to produce long-chain products.
Although substantial progress has been made in developing and understanding photocatalysts for solar fuel production from CO2 and water, we believe there are at least four significant challenges to overcome in this field apart from the discovery of catalysts/cocatalysts, which have been extensively reviewed by others.,,,,,,
Validation of the Reactions
The first challenge is the confirmation of the products in CO2 reduction reactions. In two studies, Yang et al. and Yui et al. observed 12C products (12CO and 12CH4, respectively) even if 13CO2 was used as the carbon source, indicating the carbon residues in the system could participate in the photoreactions hence should not be ignored. Therefore, the detection of all carbon-based products is not indeed proof of CO2 reduction before the validation by control experiments. Control experiments in the CO2 atmosphere and inert gas (e.g., Argon) might give some hints. While the direct evidence is the isotopic labeling experiments, which could be carried out in a GCMS, an IR system or NMR to distinguish the 13C labeled products. Hence it is crucial for all CO2 reduction reactions.
Meanwhile, the oxidation products (e.g. oxygen) should also be scrutinized and calculated with the detected carbon products to verify whether the stoichiometry of proposed reactions is achieved. Besides, the performance reported by different groups critically depends on many specific details of the experimental setup and reaction conditions, such as the light source, the pH, cocatalyst selection and loading, the sample concentration, and the reactor design. To minimize such influences, the quantum yield (QY) together with the product generation rate is all required.
Mechanism to Generate High-Value-Added Products
The second challenge is to understand the production mechanism of high-value chemicals, especially C2+, via multi-electron processes since interfacial reactions such as CO2 and multiproton reduction usually occur on a time scale of microseconds or longer. As observed for CNxHy, such trapping leads to a severe loss of driving force and microsecond charge transfer rate. To obtain a sufficient charge carrier lifetime without losing too much driving force for the interface redox reaction, nature uses a dual photocatalyst system instead of a single photocatalyst, allowing the realization of effective charge separation via a series of downhill charge transfers and overcome the inevitable back reaction. There were reports on the Z-scheme CO2 reduction systems, in which electrons and holes are generated on the spatially separated subsystems, thereby reducing the tendency of electron–hole recombination and allowing a longer lifetime and more significant accumulation of charge carriers to overcome the kinetic limitations. The accurate determination of the time scale of the charge carrier relaxation and the excited state as well as the respective reaction intermediates at the surface will provide us with the information needed to design effective materials for the selective production of the high-value products. This information can be obtained by in situ spectroscopies such as IR, EPR, XPE, XANES, and theoretical calculation.
Practical Devices
The third challenge is to develop practical devices for photocatalytic CO2 conversion. For simplicity and to focus on evaluating materials, a closed batch reactor is the most commonly used system in the literature despite its limitations. However, for potential large-scale use in the future, rationally designed reactors such as a flow system would be beneficial, in which the light distribution and mass flow need to be considered carefully. Only limited types of CO2 conversion devices have been reported so far. Wang et al. reported a wireless and stand-alone photocatalyst sheet device for scalable solar formate production from carbon dioxide and water with the solar-to-formate efficiency of ∼0.1% using a nature-mimicking Z-scheme architecture. Recently, a modular 5 kW pilot-scale solar-thermal system was demonstrated to synthesize methanol from H2O and CO2 captured directly from the ambient air operated under actual conditions. This large-scale reactor could be an exciting reference for practical CO2 conversion, although the device was only used in thermal catalysis so far. In the broad field of photocatalysis, a water-splitting device extended to the scale of 100 m2 was preliminarily validated very recently, reaching a solar to hydrogen efficiency (STH) of 0.76%, which to some extent demonstrated the safe, large-scale photocatalytic water splitting and gas collection and separation. However, the overall process was summed up as energy negative. A continuous flow reactor for scalable organosynthesis was also tested. Another group of practical reactors for CO2 photoreduction are the membrane reactors, which immobilize photocatalyst (nano)particles on the membrane substrates to replace a suspension. Although such systems might suffer from possible catalyst losses under long-term operation, they have the advantages such as no need to separate the catalyst from the solution and highly stable catalytic efficiency. The reported examples of such membrane reactors include C3N4 or TiO2 on Nafion membrane,, TiO2 on carbon paper, TiO2 and Cu–TiO2 on zeolitic imidazolate framework (ZIF-8), and so on, which are good examples for the potential use in a flow system. Reactors under concentrated solar power also have been developed to obtain the high density of electron–hole pairs in the photocatalyst, and the catalyst can also be heated to high temperatures., We have also recently developed a flow-reactor for oxidative coupling of methane to C2 products and a multilayer device for methanol reforming., All these devices for the equivalent photocatalytic reactions might accelerate the development of efficient and scalable devices for practical CO2 photoconversion, especially driven by the current global concern of the critical climate change.
Economic Considerations
The last challenge, closely connected to the third, is to take the cost of the reactant CO2 into account, which is a limiting factor for scaling up but is often ignored. Most reports used CO2 in significant excess without considering the cost of CO2 capture processes or the conversion efficiency of CO2. The approaches to directly capture CO2 from the air include aqueous alkali capture (cost US $97–134 tCO2–1 for 0.1 MPa CO2, US $116–168 tCO2–1 for 15.1 MPa CO2), supported amine capture (cost ∼ US $90 tCO2–1) and the disruptive solid absorption (cost ∼ US $15–50 tCO2–1).,, Besides, other criteria such as carbon intensity (CI, the amount of net carbon by weight emitted per unit of fuel energy consumed) and the full-cycle time should also be considered. An analysis by Nitopi et al. showed that products such as methane and CO (syngas) are not economically feasible because their market prices do not make up for the energy cost of CO2 capture, although these products are commonly reported in the literature. Instead, more preferable C1 products include methanol, formic acid, and CO (pure), while promising C2+ products are ethylene, ethanol, acetaldehyde, and propanol. The direct reduction of CO2 from the air is a very high cost and challenging process since CO2 only accounts for ∼400 ppm in the atmosphere, and the existence of oxygen also tends to react with photoelectrons to form O2– competitively. A preliminary example is the photocatalytic CO2 conversion directly from air with a ca. 98.35% selectivity to CH3OH and ca. 4.32% conversion efficiency of CO2 after 4 h reaction by selectively adsorbing CO2 rather than O2 on Rb0.33WO3 catalyst. Clearly, this is promising, while the economic benefit is too early to assess. However, the development of routes for high value-added products could be promoted by the driving force from the market.
Overall, the photocatalytic efficiency of CO2 to chemicals, in particular, the selectivity to the C2 chemicals, remains moderate so far, and its economic and environmental feasibility should be evaluated carefully to avoid extra carbon emission. An in-depth understanding of the reaction pathway will enable a precise design of the photocatalytic system, including the semiconductor, surface modification, defect engineering, cocatalyst loading, reaction conditions, and so on, toward preferable products. All these are at a very early stage at present, requiring multidisciplinary efforts and collaborations to overcome the barriers facing.
References 124
- 1.
Etheridge D. M.; Steele L. P.; Langenfelds R. L.; Francey R. J.; Barnola J.-M.; Morgan V. I. Natural and anthropogenic changes in atmospheric CO2 over the last 1000 years from air in Antarctic ice and firn. J. Geophys. Res.: Atmos. 1996, 101 (D2), 4115–4128..
Not in our library10.1029/95jd03410
- 2.
Smol J. P. Climate Change: A planet in flux. Nature 2012, 483 (7387), S12–S15..
Not in our library10.1038/483s12a
- 3.
Oktyabrskiy V. P. A new opinion of the greenhouse effect. St. Petersburg Polytechnical University Journal: Physics and Mathematics 2016, 2 (2), 124–126..
Not in our library10.1016/j.spjpm.2016.05.008
- 4.
Sabine C. L.; Heimann M.; Artaxo P.; Bakker D. C.; Chen C.-T. A.; Field C. B.; Gruber N.; Le Quéré C.; Prinn R. G.; Richey J. E. Current status and past trends of the global carbon cycle. The Global Carbon Cycle: Integrating Humans, Climate and the Natural World 2004, 62, 17–44.
Not in our library
- 5.
Olah G. A.; Prakash G. K. S.; Goeppert A. Anthropogenic Chemical Carbon Cycle for a Sustainable Future. J. Am. Chem. Soc. 2011, 133 (33), 12881–12898..
Not in our library10.1021/ja202642y
- 6.
Murphy J. L.; Measures C. I. Ocean Acidification: The Role of CO2. Oceanography 2014, 27 (1), 238–246..
Not in our library10.5670/oceanog.2014.01
- 7.
Xie H.; Yue H.; Zhu J.; Liang B.; Li C.; Wang Y.; Xie L.; Zhou X. Scientific and Engineering Progress in CO2 mineralization Using Industrial Waste and Natural Minerals. Engineering 2015, 1 (1), 150–157..
Not in our library10.15302/j-eng-2015017
- 8.
Wang Y.; Yao E.-P.; Wu L.; Feldmann J.; Stolarczyk J. K. A Multi-Layer Device for Light-Triggered Hydrogen Production from Alkaline Methanol. Angew. Chem., Int. Ed. 2021, 60 (51), 26694.
Not in our library10.1002/anie.202109979
- 9.
Randau S.; Weber D. A.; Kötz O.; Koerver R.; Braun P.; Weber A.; Ivers-Tiffée E.; Adermann T.; Kulisch J.; Zeier W. G.; Richter F. H.; Janek J. Benchmarking the performance of all-solid-state lithium batteries. Nat. Energy 2020, 5 (3), 259–270..
Not in our library10.1038/s41560-020-0565-1
- 10.
McKinlay C. J.; Turnock S. R.; Hudson D. A. Route to zero emission shipping: Hydrogen, ammonia or methanol?. Int. J. Hydrogen Energy 2021, 46 (55), 28282–28297..
Not in our library10.1016/j.ijhydene.2021.06.066
- 11.
Stolarczyk J. K.; Bhattacharyya S.; Polavarapu L.; Feldmann J. Challenges and Prospects in Solar Water Splitting and CO2 Reduction with Inorganic and Hybrid Nanostructures. ACS Catal. 2018, 8 (4), 3602–3635..
Not in our library10.1021/acscatal.8b00791
- 12.
Hemminger J. C.; Carr R.; Somorjai G. A. The photoassisted reaction of gaseous water and carbon dioxide adsorbed on the SrTiO3 (111) crystal face to form methane. Chem. Phys. Lett. 1978, 57 (1), 100–104..
Not in our library10.1016/0009-2614(78)80359-5
- 13.
Inoue T.; Fujishima A.; Konishi S.; Honda K. Photoelectrocatalytic reduction of carbon dioxide in aqueous suspensions of semiconductor powders. Nature 1979, 277 (5698), 637–638..
Not in our library10.1038/277637a0
- 14.
Walsh J. J.; Jiang C.; Tang J.; Cowan A. J. Photochemical CO2 reduction using structurally controlled g-C3N4. Phys. Chem. Chem. Phys. 2016, 18, 24825–24829..
Not in our library10.1039/c6cp04525a
- 15.
Kong D.; Han X.; Xie J.; Ruan Q.; Windle C. D.; Gadipelli S.; Shen K.; Bai Z.; Guo Z.; Tang J. Tunable Covalent Triazine-based Frameworks (CTF-0) for Visible Light-Driven Hydrogen and Oxygen Generation from Water Splitting. ACS Catal. 2019, 9, 7697–7707..
Not in our library10.1021/acscatal.9b02195
- 16.
Nitopi S.; Bertheussen E.; Scott S. B.; Liu X.; Engstfeld A. K.; Horch S.; Seger B.; Stephens I. E. L.; Chan K.; Hahn C.; Nørskov J. K.; Jaramillo T. F.; Chorkendorff I. Progress and Perspectives of Electrochemical CO2 Reduction on Copper in Aqueous Electrolyte. Chem. Rev. 2019, 119 (12), 7610–7672..
Not in our library10.1021/acs.chemrev.8b00705
- 17.
Albero J.; Peng Y.; García H. Photocatalytic CO2 Reduction to C2+ Products. ACS Catal. 2020, 10 (10), 5734–5749..
Not in our library10.1021/acscatal.0c00478
- 18.
Nordgren J.; Selander L.; Pettersson L.; Nordling C.; Siegbahn K.; Ågren H. Core state vibrational excitations and symmetry breaking in the CK and OK emission spectra of CO2. J. Chem. Phys. 1982, 76 (8), 3928–3932..
Not in our library10.1063/1.443509
- 19.
Freund H. J.; Roberts M. W. Surface chemistry of carbon dioxide. Surf. Sci. Rep. 1996, 25 (8), 225–273..
Not in our library10.1016/s0167-5729(96)00007-6
- 20.
Indrakanti V. P.; Kubicki J. D.; Schobert H. H. Photoinduced activation of CO2 on Ti-based heterogeneous catalysts: Current state, chemical physics-based insights and outlook. Energy Environ. Sci. 2009, 2 (7), 745–758..
Not in our library10.1039/b822176f
- 21.
Koppenol W. H.; Rush J. D. Reduction potential of the carbon dioxide/carbon dioxide radical anion: a comparison with other C1 radicals. J. Phys. Chem. 1987, 91 (16), 4429–4430..
Not in our library10.1021/j100300a045
- 22.
Matsuoka S.; Kohzuki T.; Pac C.; Ishida A.; Takamuku S.; Kusaba M.; Nakashima N.; Yanagida S. Photocatalysis of oligo(p-phenylenes): photochemical reduction of carbon dioxide with triethylamine. J. Phys. Chem. 1992, 96 (11), 4437–4442..
Not in our library10.1021/j100190a057
- 23.
Rasko J.; Solymosi F. Infrared Spectroscopic Study of the Photoinduced Activation of CO2 on TiO2 and Rh/TiO2 Catalysts. J. Phys. Chem. 1994, 98 (29), 7147–7152..
Not in our library10.1021/j100080a009
- 24.
Indrakanti V. P.; Schobert H. H.; Kubicki J. D. Quantum Mechanical Modeling of CO2 Interactions with Irradiated Stoichiometric and Oxygen-Deficient Anatase TiO2 Surfaces: Implications for the Photocatalytic Reduction of CO2. Energy Fuels 2009, 23 (10), 5247–5256..
Not in our library10.1021/ef9003957
- 25.
Kamat P. V. Manipulation of Charge Transfer Across Semiconductor Interface. A Criterion That Cannot Be Ignored in Photocatalyst Design. J. Phys. Chem. Lett. 2012, 3 (5), 663–672..
Not in our library10.1021/jz201629p
- 26.
Yamazaki Y.; Takeda H.; Ishitani O. Photocatalytic reduction of CO2 using metal complexes. J. Photochem. Photobiol., C 2015, 25, 106–137..
Not in our library10.1016/j.jphotochemrev.2015.09.001
- 27.
Chang X.; Wang T.; Gong J. CO2 photo-reduction: insights into CO2 activation and reaction on surfaces of photocatalysts. Energy Environ. Sci. 2016, 9 (7), 2177–2196..
Not in our library10.1039/c6ee00383d
- 28.
Tang J.; Durrant J. R.; Klug D. R. Mechanism of Photocatalytic Water Splitting in TiO2. Reaction of Water with Photoholes, Importance of Charge Carrier Dynamics, and Evidence for Four-Hole Chemistry. J. Am. Chem. Soc. 2008, 130 (42), 13885–13891..
Not in our library10.1021/ja8034637
- 29.
Fu J.; Jiang K.; Qiu X.; Yu J.; Liu M. Product selectivity of photocatalytic CO2 reduction reactions. Mater. Today 2020, 32, 222–243..
Not in our library10.1016/j.mattod.2019.06.009
- 30.
Henderson M. A. A surface science perspective on TiO2 photocatalysis. Surf. Sci. Rep. 2011, 66 (6), 185–297..
Not in our library10.1016/j.surfrep.2011.01.001
- 31.
Li X.; Yu J.; Jaroniec M.; Chen X. Cocatalysts for Selective Photoreduction of CO2 into Solar Fuels. Chem. Rev. 2019, 119 (6), 3962–4179..
Not in our library10.1021/acs.chemrev.8b00400
- 32.
Wang Q.; Domen K. Particulate Photocatalysts for Light-Driven Water Splitting: Mechanisms, Challenges, and Design Strategies. Chem. Rev. 2020, 120 (2), 919–985..
Not in our library10.1021/acs.chemrev.9b00201
- 33.
Kudo A.; Miseki Y. Heterogeneous photocatalyst materials for water splitting. Chem. Soc. Rev. 2009, 38 (1), 253–278..
Not in our library10.1039/b800489g
- 34.
Moniz S. J. A.; Shevlin S. A.; Martin D. J.; Guo Z.-X.; Tang J. Visible-light driven heterojunction photocatalysts for water splitting – a critical review. Energy Environ. Sci. 2015, 8 (3), 731–759..
Not in our library10.1039/c4ee03271c
- 35.
Hori Y.; Wakebe H.; Tsukamoto T.; Koga O. Electrocatalytic process of CO selectivity in electrochemical reduction of CO2 at metal electrodes in aqueous media. Electrochim. Acta 1994, 39 (11), 1833–1839..
Not in our library10.1016/0013-4686(94)85172-7
- 36.
Anpo M.; Yamashita H.; Ichihashi Y.; Ehara S. Photocatalytic reduction of CO2 with H2O on various titanium oxide catalysts. J. Electroanal. Chem. 1995, 396 (1), 21–26..
Not in our library10.1016/0022-0728(95)04141-a
- 37.
Tan S. S.; Zou L.; Hu E. Kinetic modelling for photosynthesis of hydrogen and methane through catalytic reduction of carbon dioxide with water vapour. Catal. Today 2008, 131 (1), 125–129..
Not in our library10.1016/j.cattod.2007.10.011
- 38.
Peterson A. A.; Abild-Pedersen F.; Studt F.; Rossmeisl J.; Nørskov J. K. How copper catalyzes the electroreduction of carbon dioxide into hydrocarbon fuels. Energy Environ. Sci. 2010, 3 (9), 1311–1315..
Not in our library10.1039/c0ee00071j
- 39.
Hori Y.; Murata A.; Yoshinami Y. Adsorption of CO, intermediately formed in electrochemical reduction of CO2, at a copper electrode. J. Chem. Soc., Faraday Trans. 1991, 87 (1), 125–128..
Not in our library10.1039/ft9918700125
- 40.
Shkrob I. A.; Marin T. W.; He H.; Zapol P. Photoredox Reactions and the Catalytic Cycle for Carbon Dioxide Fixation and Methanogenesis on Metal Oxides. J. Phys. Chem. C 2012, 116 (17), 9450–9460..
Not in our library10.1021/jp300122v
- 41.
Wang Y.; Liu X.; Han X.; Godin R.; Chen J.; Zhou W.; Jiang C.; Thompson J. F.; Mustafa K. B.; Shevlin S. A.; Durrant J. R.; Guo Z.; Tang J. Unique hole-accepting carbon-dots promoting selective carbon dioxide reduction nearly 100% to methanol by pure water. Nat. Commun. 2020, 11 (1), 2531.
Not in our library10.1038/s41467-020-16227-3
- 42.
Wang Y.; Godin R.; Durrant J. R.; Tang J. Efficient Hole Trapping in Carbon Dot/Oxygen-Modified Carbon Nitride Heterojunction Photocatalysts for Enhanced Methanol Production from CO2 under Neutral Conditions. Angew. Chem., Int. Ed. 2021, 60 (38), 20811.
Not in our library10.1002/anie.202105570
- 43.
Wang Q.; Warnan J.; Rodríguez-Jiménez S.; Leung J. J.; Kalathil S.; Andrei V.; Domen K.; Reisner E. Molecularly engineered photocatalyst sheet for scalable solar formate production from carbon dioxide and water. Nat. Energy 2020, 5 (9), 703–710..
Not in our library10.1038/s41560-020-0678-6
- 44.
Kortlever R.; Shen J.; Schouten K. J. P.; Calle-Vallejo F.; Koper M. T. M. Catalysts and Reaction Pathways for the Electrochemical Reduction of Carbon Dioxide. J. Phys. Chem. Lett. 2015, 6 (20), 4073–4082..
Not in our library10.1021/acs.jpclett.5b01559
- 45.
Shkrob I. A.; Dimitrijevic N. M.; Marin T. W.; He H.; Zapol P. Heteroatom-Transfer Coupled Photoreduction and Carbon Dioxide Fixation on Metal Oxides. J. Phys. Chem. C 2012, 116 (17), 9461–9471..
Not in our library10.1021/jp300123z
- 46.
Sasirekha N.; Basha S. J. S.; Shanthi K. Photocatalytic performance of Ru doped anatase mounted on silica for reduction of carbon dioxide. Appl. Catal., B 2006, 62 (1), 169–180..
Not in our library10.1016/j.apcatb.2005.07.009
- 47.
Subrahmanyam M.; Kaneco S.; Alonso-Vante N. A screening for the photo reduction of carbon dioxide supported on metal oxide catalysts for C1–C3 selectivity. Appl. Catal., B 1999, 23 (2), 169–174..
Not in our library10.1016/s0926-3373(99)00079-x
- 48.
Koci K.; Obalova L.; Solcova O. Kinetic study of photocatalytic reduction of CO2 over TiO2. Chem. Process Eng. 2010, 31, 395–407.
Not in our library
- 49.
Hori Y.; Murata A.; Takahashi R. Formation of hydrocarbons in the electrochemical reduction of carbon dioxide at a copper electrode in aqueous solution. J. Chem. Soc., Faraday Trans. 1 1989, 85 (8), 2309–2326..
Not in our library10.1039/f19898502309
- 50.
Cheng T.; Xiao H.; Goddard W. A. Free-Energy Barriers and Reaction Mechanisms for the Electrochemical Reduction of CO on the Cu(100) Surface, Including Multiple Layers of Explicit Solvent at pH 0. J. Phys. Chem. Lett. 2015, 6 (23), 4767–4773..
Not in our library10.1021/acs.jpclett.5b02247
- 51.
Nie X.; Esopi M. R.; Janik M. J.; Asthagiri A. Selectivity of CO2 Reduction on Copper Electrodes: The Role of the Kinetics of Elementary Steps. Angew. Chem., Int. Ed. 2013, 52 (9), 2459–2462..
Not in our library10.1002/anie.201208320
- 52.
Park H. R.; Pawar A. U.; Pal U.; Zhang T.; Kang Y. S. Enhanced solar photoreduction of CO2 to liquid fuel over rGO grafted NiO-CeO2 heterostructure nanocomposite. Nano Energy 2021, 79, 105483.
Not in our library10.1016/j.nanoen.2020.105483
- 53.
DeWulf D. W.; Jin T.; Bard A. J. Electrochemical and Surface Studies of Carbon Dioxide Reduction to Methane and Ethylene at Copper Electrodes in Aqueous Solutions. J. Electrochem. Soc. 1989, 136 (6), 1686–1691..
Not in our library10.1149/1.2096993
- 54.
- 55.
Schouten K. J. P.; Kwon Y.; van der Ham C. J. M.; Qin Z.; Koper M. T. M. A new mechanism for the selectivity to C1 and C2 species in the electrochemical reduction of carbon dioxide on copper electrodes. Chem. Sci. 2011, 2 (10), 1902–1909..
Not in our library10.1039/c1sc00277e
- 56.
Olah G. A. Beyond Oil and Gas: The Methanol Economy. Angew. Chem., Int. Ed. 2005, 44 (18), 2636–2639..
Not in our library10.1002/anie.200462121
- 57.
Lin L.; Zhou W.; Gao R.; Yao S.; Zhang X.; Xu W.; Zheng S.; Jiang Z.; Yu Q.; Li Y.-W.; Shi C.; Wen X.-D.; Ma D. Low-temperature hydrogen production from water and methanol using Pt/α-MoC catalysts. Nature 2017, 544, 80.
Not in our library10.1038/nature21672
- 58.
Barreto L.; Makihira A.; Riahi K. The hydrogen economy in the 21st century: a sustainable development scenario. Int. J. Hydrogen Energy 2003, 28 (3), 267–284..
Not in our library10.1016/s0360-3199(02)00074-5
- 59.
Crabtree G. W.; Dresselhaus M. S.; Buchanan M. V. The hydrogen economy. Phys. Today 2004, 57 (12), 39–44..
Not in our library10.1063/1.1878333
- 60.
Tountas A. A.; Ozin G. A.; Sain M. M. Solar methanol energy storage. Nat. Catal. 2021, 4 (11), 934–942..
Not in our library10.1038/s41929-021-00696-w
- 61.
Ikeue K.; Yamashita H.; Anpo M.; Takewaki T. Photocatalytic Reduction of CO2 with H2O on Ti−β Zeolite Photocatalysts: Effect of the Hydrophobic and Hydrophilic Properties. J. Phys. Chem. B 2001, 105 (35), 8350–8355..
Not in our library10.1021/jp010885g
- 62.
Yamashita H.; Fujii Y.; Ichihashi Y.; Zhang S. G.; Ikeue K.; Park D. R.; Koyano K.; Tatsumi T.; Anpo M. Selective formation of CH3OH in the photocatalytic reduction of CO2 with H2O on titanium oxides highly dispersed within zeolites and mesoporous molecular sieves. Catal. Today 1998, 45 (1), 221–227..
Not in our library10.1016/s0920-5861(98)00219-3
- 63.
Lum Y.; Cheng T.; Goddard W. A.; Ager J. W. Electrochemical CO Reduction Builds Solvent Water into Oxygenate Products. J. Am. Chem. Soc. 2018, 140 (30), 9337–9340..
Not in our library10.1021/jacs.8b03986
- 64.
Fasihi M.; Efimova O.; Breyer C. Techno-economic assessment of CO2 direct air capture plants. J. Cleaner Prod. 2019, 224, 957–980..
Not in our library10.1016/j.jclepro.2019.03.086
- 65.
Xie J.; Jin R.; Li A.; Bi Y.; Ruan Q.; Deng Y.; Zhang Y.; Yao S.; Sankar G.; Ma D.; Tang J. Highly selective oxidation of methane to methanol at ambient conditions by titanium dioxide-supported iron species. Nat. Catal. 2018, 1 (11), 889–896..
Not in our library10.1038/s41929-018-0170-x
- 66.
Ji Y.; Luo Y. New Mechanism for Photocatalytic Reduction of CO2 on the Anatase TiO2(101) Surface: The Essential Role of Oxygen Vacancy. J. Am. Chem. Soc. 2016, 138 (49), 15896–15902..
Not in our library10.1021/jacs.6b05695
- 67.
Hao Y.-C.; Chen L.-W.; Li J.; Guo Y.; Su X.; Shu M.; Zhang Q.; Gao W.-Y.; Li S.; Yu Z.-L.; Gu L.; Feng X.; Yin A.-X.; Si R.; Zhang Y.-W.; Wang B.; Yan C.-H. Metal-organic framework membranes with single-atomic centers for photocatalytic CO2 and O2 reduction. Nat. Commun. 2021, 12 (1), 2682.
Not in our library10.1038/s41467-021-22991-7
- 68.
Tahir M. Synergistic effect in MMT-dispersed Au/TiO2 monolithic nanocatalyst for plasmon-absorption and metallic interband transitions dynamic CO2 photo-reduction to CO. Appl. Catal., B 2017, 219, 329–343..
Not in our library10.1016/j.apcatb.2017.07.062
- 69.
Gao C.; Meng Q.; Zhao K.; Yin H.; Wang D.; Guo J.; Zhao S.; Chang L.; He M.; Li Q.; Zhao H.; Huang X.; Gao Y.; Tang Z. Co3O4 Hexagonal Platelets with Controllable Facets Enabling Highly Efficient Visible-Light Photocatalytic Reduction of CO2. Adv. Mater. 2016, 28 (30), 6485–6490..
Not in our library10.1002/adma.201601387
- 70.
Kuriki R.; Ishitani O.; Maeda K. Unique Solvent Effects on Visible-Light CO2 Reduction over Ruthenium(II)-Complex/Carbon Nitride Hybrid Photocatalysts. ACS Appl. Mater. Interfaces 2016, 8 (9), 6011–6018..
Not in our library10.1021/acsami.5b11836
- 71.
- 72.
Maeda K.; Kuriki R.; Zhang M.; Wang X.; Ishitani O. The effect of the pore-wall structure of carbon nitride on photocatalytic CO2 reduction under visible light. J. Mater. Chem. A 2014, 2 (36), 15146–15151..
Not in our library10.1039/c4ta03128h
- 73.
Guan G.; Kida T.; Harada T.; Isayama M.; Yoshida A. Photoreduction of carbon dioxide with water over K2Ti6O13 photocatalyst combined with Cu/ZnO catalyst under concentrated sunlight. Appl. Catal., A 2003, 249 (1), 11–18..
Not in our library10.1016/s0926-860x(03)00205-9
- 74.
Hou W.; Hung W. H.; Pavaskar P.; Goeppert A.; Aykol M.; Cronin S. B. Photocatalytic Conversion of CO2 to Hydrocarbon Fuels via Plasmon-Enhanced Absorption and Metallic Interband Transitions. ACS Catal. 2011, 1 (8), 929–936..
Not in our library10.1021/cs2001434
- 75.
Duan Y. Q.; Du T.; Wang X. W.; Cai F. S.; Yuan Z. H. Photoassisted CO2 Conversion to Carbon by Reduced NiFe2O4. Adv. Mater. Res. 2013, 726–731, 420–424..
Not in our library10.4028/www.scientific.net/amr.726-731.420
- 76.
Li A.; Wang T.; Li C.; Huang Z.; Luo Z.; Gong J. Adjusting the Reduction Potential of Electrons by Quantum Confinement for Selective Photoreduction of CO2 to Methanol. Angew. Chem., Int. Ed. 2019, 58 (12), 3804–3808..
Not in our library10.1002/anie.201812773
- 77.
Das R.; Sarkar S.; Kumar R.; D. Ramarao S.; Cherevotan A.; Jasil M.; Vinod C. P.; Singh A. K.; Peter S. C. Noble-Metal-Free Heterojunction Photocatalyst for Selective CO2 Reduction to Methane upon Induced Strain Relaxation. ACS Catal. 2022, 12 (1), 687–697..
Not in our library10.1021/acscatal.1c04587
- 78.
Albero J.; Garcia H.; Corma A. Temperature Dependence of Solar Light Assisted CO2 Reduction on Ni Based Photocatalyst. Top. Catal. 2016, 59 (8), 787–791..
Not in our library10.1007/s11244-016-0550-x
- 79.
Wang J.; Kim E.; Kumar D. P.; Rangappa A. P.; Kim Y.; Zhang Y.; Kim T. K. Highly Durable and Fully Dispersed Cobalt Diatomic Site Catalysts for CO2 Photoreduction to CH4. Angew. Chem., Int. Ed. 2022, 61 (6), e202113044.
Not in our library10.1002/anie.202113044
- 80.
Yu S.; Wilson A. J.; Heo J.; Jain P. K. Plasmonic Control of Multi-Electron Transfer and C–C Coupling in Visible-Light-Driven CO2 Reduction on Au Nanoparticles. Nano Lett. 2018, 18 (4), 2189–2194..
Not in our library10.1021/acs.nanolett.7b05410
- 81.
Luo W.; Nie X.; Janik M. J.; Asthagiri A. Facet Dependence of CO2 Reduction Paths on Cu Electrodes. ACS Catal. 2016, 6 (1), 219–229..
Not in our library10.1021/acscatal.5b01967
- 82.
Park H.; Ou H.-H.; Colussi A. J.; Hoffmann M. R. Artificial Photosynthesis of C1–C3 Hydrocarbons from Water and CO2 on Titanate Nanotubes Decorated with Nanoparticle Elemental Copper and CdS Quantum Dots. J. Phys. Chem. A 2015, 119 (19), 4658–4666..
Not in our library10.1021/jp511329d
- 83.
Sorcar S.; Thompson J.; Hwang Y.; Park Y. H.; Majima T.; Grimes C. A.; Durrant J. R.; In S.-I. High-rate solar-light photoconversion of CO2 to fuel: controllable transformation from C1 to C2 products. Energy Environ. Sci. 2018, 11 (11), 3183–3193..
Not in our library10.1039/c8ee00983j
- 84.
Paul J.; Hoffmann F. M. Co2 conversion and oxalate stability on alkali promoted metal surfaces: Sodium modified Al(100). Catal. Lett. 1988, 1 (12), 445–455..
Not in our library10.1007/bf00766205
- 85.
Schouten K. J. P.; Pérez Gallent E.; Koper M. T. M. The influence of pH on the reduction of CO and CO2 to hydrocarbons on copper electrodes. J. Electroanal. Chem. 2014, 716, 53–57..
Not in our library10.1016/j.jelechem.2013.08.033
- 86.
Hori Y.; Takahashi I.; Koga O.; Hoshi N. Electrochemical reduction of carbon dioxide at various series of copper single crystal electrodes. J. Mol. Catal. A: Chem. 2003, 199 (1), 39–47..
Not in our library10.1016/s1381-1169(03)00016-5
- 87.
Kuhl K. P.; Cave E. R.; Abram D. N.; Jaramillo T. F. New insights into the electrochemical reduction of carbon dioxide on metallic copper surfaces. Energy Environ. Sci. 2012, 5 (5), 7050–7059..
Not in our library10.1039/c2ee21234j
- 88.
Liu Q.; Cheng H.; Chen T.; Lo T. W. B.; Xiang Z.; Wang F. Regulating the *OCCHO intermediate pathway towards highly selective photocatalytic CO2 reduction to CH3CHO over locally crystallized carbon nitride. Energy Environ. Sci. 2022, 15 (1), 225–233..
Not in our library10.1039/d1ee02073k
- 89.
Zhu S.; Li X.; Jiao X.; Shao W.; Li L.; Zu X.; Hu J.; Zhu J.; Yan W.; Wang C.; Sun Y.; Xie Y. Selective CO2 Photoreduction into C2 Product Enabled by Charge-Polarized Metal Pair Sites. Nano Lett. 2021, 21 (5), 2324–2331..
Not in our library10.1021/acs.nanolett.1c00383
- 90.
Yu F.; Jing X.; Wang Y.; Sun M.; Duan C. Hierarchically Porous Metal–Organic Framework/MoS2 Interface for Selective Photocatalytic Conversion of CO2 with H2O into CH3COOH. Angew. Chem., Int. Ed. 2021, 60 (47), 24849–24853..
Not in our library10.1002/anie.202108892
- 91.
Molino A.; Mehariya S.; Di Sanzo G.; Larocca V.; Martino M.; Leone G. P.; Marino T.; Chianese S.; Balducchi R.; Musmarra D. Recent developments in supercritical fluid extraction of bioactive compounds from microalgae: Role of key parameters, technological achievements and challenges. J. CO2 Util. 2020, 36, 196–209..
Not in our library10.1016/j.jcou.2019.11.014
- 92.
Sun S.; Watanabe M.; Wu J.; An Q.; Ishihara T. Ultrathin WO3·0.33H2O Nanotubes for CO2 Photoreduction to Acetate with High Selectivity. J. Am. Chem. Soc. 2018, 140 (20), 6474–6482..
Not in our library10.1021/jacs.8b03316
- 93.
Niu P.; Yang Y.; Yu J. C.; Liu G.; Cheng H.-M. Switching the selectivity of the photoreduction reaction of carbon dioxide by controlling the band structure of a g-C3N4 photocatalyst. Chem. Commun. 2014, 50 (74), 10837–10840..
Not in our library10.1039/c4cc03060e
- 94.
- 95.
Qian X.; Yang W.; Gao S.; Xiao J.; Basu S.; Yoshimura A.; Shi Y.; Meunier V.; Li Q. Highly Selective, Defect-Induced Photocatalytic CO2 Reduction to Acetaldehyde by the Nb-Doped TiO2 Nanotube Array under Simulated Solar Illumination. ACS Appl. Mater. Interfaces 2020, 12 (50), 55982–55993..
Not in our library10.1021/acsami.0c17174
- 96.
Das R.; Das K.; Ray B.; Vinod C. P.; Peter S. C. Green transformation of CO2 to ethanol using water and sunlight by the combined effect of naturally abundant red phosphorus and Bi2MoO6. Energy Environ. Sci. 2022, 15, 1967.
Not in our library10.1039/d1ee02976b
- 97.
Li H.; Gan S.; Wang H.; Han D.; Niu L. Intercorrelated Superhybrid of AgBr Supported on Graphitic-C3N4-Decorated Nitrogen-Doped Graphene: High Engineering Photocatalytic Activities for Water Purification and CO2 Reduction. Adv. Mater. 2015, 27 (43), 6906–6913..
Not in our library10.1002/adma.201502755
- 98.
Dai W.; Xu H.; Yu J.; Hu X.; Luo X.; Tu X.; Yang L. Photocatalytic reduction of CO2 into methanol and ethanol over conducting polymers modified Bi2WO6 microspheres under visible light. Appl. Surf. Sci. 2015, 356, 173–180..
Not in our library10.1016/j.apsusc.2015.08.059
- 99.
Dai W.; Xiong W.; Yu J.; Zhang S.; Li B.; Yang L.; Wang T.; Luo X.; Zou J.; Luo S. Bi2MoO6 Quantum Dots In Situ Grown on Reduced Graphene Oxide Layers: A Novel Electron-Rich Interface for Efficient CO2 Reduction. ACS Appl. Mater. Interfaces 2020, 12 (23), 25861–25874..
Not in our library10.1021/acsami.0c04730
- 100.
Yu L.; Li G.; Zhang X.; Ba X.; Shi G.; Li Y.; Wong P. K.; Yu J. C.; Yu Y. Enhanced Activity and Stability of Carbon-Decorated Cuprous Oxide Mesoporous Nanorods for CO2 Reduction in Artificial Photosynthesis. ACS Catal. 2016, 6 (10), 6444–6454..
Not in our library10.1021/acscatal.6b01455
- 101.
Adachi K.; Ohta K.; Mizuno T. Photocatalytic reduction of carbon dioxide to hydrocarbon using copper-loaded titanium dioxide. Sol. Energy 1994, 53 (2), 187–190..
Not in our library10.1016/0038-092x(94)90480-4
- 102.
Gui M. M.; Wong W. M. P.; Chai S.-P.; Mohamed A. R. One-pot synthesis of Ag-MWCNT@TiO2 core–shell nanocomposites for photocatalytic reduction of CO2 with water under visible light irradiation. Chem. Eng. J. 2015, 278, 272–278..
Not in our library10.1016/j.cej.2014.09.022
- 103.
Kim W.; Seok T.; Choi W. Nafion layer-enhanced photosynthetic conversion of CO2 into hydrocarbons on TiO2 nanoparticles. Energy Environ. Sci. 2012, 5 (3), 6066–6070..
Not in our library10.1039/c2ee03338k
- 104.
Chen Q.; Chen X.; Fang M.; Chen J.; Li Y.; Xie Z.; Kuang Q.; Zheng L. Photo-induced Au–Pd alloying at TiO2 {101} facets enables robust CO2 photocatalytic reduction into hydrocarbon fuels. J. Mater. Chem. A 2019, 7 (3), 1334–1340..
Not in our library10.1039/c8ta09412h
- 105.
Garza A. J.; Bell A. T.; Head-Gordon M. Mechanism of CO2 Reduction at Copper Surfaces: Pathways to C2 Products. ACS Catal. 2018, 8 (2), 1490–1499..
Not in our library10.1021/acscatal.7b03477
- 106.
Sun M.; Zhao B.; Chen F.; Liu C.; Lu S.; Yu Y.; Zhang B. Thermally-assisted photocatalytic CO2 reduction to fuels. Chem. Eng. J. 2021, 408, 127280.
Not in our library10.1016/j.cej.2020.127280
- 107.
Kuehnel M. F.; Orchard K. L.; Dalle K. E.; Reisner E. Selective Photocatalytic CO2 Reduction in Water through Anchoring of a Molecular Ni Catalyst on CdS Nanocrystals. J. Am. Chem. Soc. 2017, 139 (21), 7217–7223..
Not in our library10.1021/jacs.7b00369
- 108.
Godin R.; Wang Y.; Zwijnenburg M. A.; Tang J.; Durrant J. R. Time-Resolved Spectroscopic Investigation of Charge Trapping in Carbon Nitrides Photocatalysts for Hydrogen Generation. J. Am. Chem. Soc. 2017, 139 (14), 5216–5224..
Not in our library10.1021/jacs.7b01547
- 109.
Wang Y.; Suzuki H.; Xie J.; Tomita O.; Martin D. J.; Higashi M.; Kong D.; Abe R.; Tang J. Mimicking Natural Photosynthesis: Solar to Renewable H2 Fuel Synthesis by Z-Scheme Water Splitting Systems. Chem. Rev. 2018, 118 (10), 5201–5241..
Not in our library10.1021/acs.chemrev.7b00286
- 110.
Guo L.; Chen Y.; Su J.; Liu M.; Liu Y. Obstacles of solar-powered photocatalytic water splitting for hydrogen production: A perspective from energy flow and mass flow. Energy 2019, 172, 1079–1086..
Not in our library10.1016/j.energy.2019.02.050
- 111.
Schäppi R.; Rutz D.; Dähler F.; Muroyama A.; Haueter P.; Lilliestam J.; Patt A.; Furler P.; Steinfeld A. Drop-in Fuels from Sunlight and Air. Nature 2022, 601, 63–68..
Not in our library10.1038/s41586-021-04174-y
- 112.
Nishiyama H.; Yamada T.; Nakabayashi M.; Maehara Y.; Yamaguchi M.; Kuromiya Y.; Nagatsuma Y.; Tokudome H.; Akiyama S.; Watanabe T.; Narushima R.; Okunaka S.; Shibata N.; Takata T.; Hisatomi T.; Domen K. Photocatalytic solar hydrogen production from water on a 100-m2 scale. Nature 2021, 598 (7880), 304–307..
Not in our library10.1038/s41586-021-03907-3
- 113.
Yang C.; Li R.; Zhang K. A. I.; Lin W.; Landfester K.; Wang X. Heterogeneous photoredox flow chemistry for the scalable organosynthesis of fine chemicals. Nat. Commun. 2020, 11 (1), 1239.
Not in our library10.1038/s41467-020-14983-w
- 114.
Baniamer M.; Aroujalian A.; Sharifnia S. Photocatalytic membrane reactor for simultaneous separation and photoreduction of CO2 to methanol. Int. J. Energy Res. 2021, 45 (2), 2353–2366..
Not in our library10.1002/er.5930
- 115.
Zhang W.; Ding L.; Luo J.; Jaffrin M. Y.; Tang B. Membrane fouling in photocatalytic membrane reactors (PMRs) for water and wastewater treatment: A critical review. Chem. Eng. J. 2016, 302, 446–458..
Not in our library10.1016/j.cej.2016.05.071
- 116.
Pomilla F. R.; Brunetti A.; Marcì G.; García-López E. I.; Fontananova E.; Palmisano L.; Barbieri G. CO2 to Liquid Fuels: Photocatalytic Conversion in a Continuous Membrane Reactor. ACS Sustainable Chem. Eng. 2018, 6 (7), 8743–8753..
Not in our library10.1021/acssuschemeng.8b01073
- 117.
Brunetti A.; Pomilla F. R.; Marcì G.; Garcia-Lopez E. I.; Fontananova E.; Palmisano L.; Barbieri G. CO2 reduction by C3N4-TiO2 Nafion photocatalytic membrane reactor as a promising environmental pathway to solar fuels. Appl. Catal., B 2019, 255, 117779.
Not in our library10.1016/j.apcatb.2019.117779
- 118.
Cheng X.; Chen R.; Zhu X.; Liao Q.; He X.; Li S.; Li L. Optofluidic membrane microreactor for photocatalytic reduction of CO2. Int. J. Hydrogen Energy 2016, 41 (4), 2457–2465..
Not in our library10.1016/j.ijhydene.2015.12.066
- 119.
Maina J. W.; Schütz J. A.; Grundy L.; Des Ligneris E.; Yi Z.; Kong L.; Pozo-Gonzalo C.; Ionescu M.; Dumée L. F. Inorganic Nanoparticles/Metal Organic Framework Hybrid Membrane Reactors for Efficient Photocatalytic Conversion of CO2. ACS Appl. Mater. Interfaces 2017, 9 (40), 35010–35017..
Not in our library10.1021/acsami.7b11150
- 120.
Guan G.; Kida T.; Yoshida A. Reduction of carbon dioxide with water under concentrated sunlight using photocatalyst combined with Fe-based catalyst. Appl. Catal., B 2003, 41 (4), 387–396..
Not in our library10.1016/s0926-3373(02)00174-1
- 121.
Li X.; Xie J.; Rao H.; Wang C.; Tang J. Platinum- and CuOx-Decorated TiO2 Photocatalyst for Oxidative Coupling of Methane to C2 Hydrocarbons in a Flow Reactor. Angew. Chem., Int. Ed. 2020, 59 (44), 19702–19707..
Not in our library10.1002/anie.202007557
- 122.
Keith D. W.; Holmes G.; St. Angelo D.; Heidel K. A Process for Capturing CO2 from the Atmosphere. Joule 2018, 2 (8), 1573–1594..
Not in our library10.1016/j.joule.2018.05.006
- 123.
Realmonte G.; Drouet L.; Gambhir A.; Glynn J.; Hawkes A.; Köberle A. C.; Tavoni M. An inter-model assessment of the role of direct air capture in deep mitigation pathways. Nat. Commun. 2019, 10 (1), 3277.
Not in our library10.1038/s41467-019-10842-5
- 124.
Wu X.; Li Y.; Zhang G.; Chen H.; Li J.; Wang K.; Pan Y.; Zhao Y.; Sun Y.; Xie Y. Photocatalytic CO2 Conversion of M0.33WO3 Directly from the Air with High Selectivity: Insight into Full Spectrum-Induced Reaction Mechanism. J. Am. Chem. Soc. 2019, 141 (13), 5267–5274..
Not in our library10.1021/jacs.8b12928
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