The ability of metal oxides to bind and activate CO
2 depends greatly on several factors, including their preparation methods, physiochemical properties, redox properties, and electronic and geometric structures
[36][43][47]. The preparation methods were found to impact the properties of CeO
2 nanostructures for the photocatalytic reduction of CO
2 [48]. A high surface area was obtained for catalysts synthesized through the sunlight-assisted combustion process, in addition to possessing a small particle size, high concentration of oxygen vacancies, and a narrow bandgap. Compared to that prepared from the conventional combustion process with a spongy-like structure, a porous network consisting of small and uniformed pores was also obtained for the sunlight-assisted process. The superior catalytic properties could be attributed to the novel properties endowed by solar irradiation during the synthesis process. As demonstrated with the CeO
x/Cu catalyst, the important roles of metal oxide ions were revealed on the catalytic cycle of H
2O and CO
2 activation. The Cu phase was reduced into Cu
0 that promoted Ce
4+ reduction into Ce
3+. H
2O and CO
2 activation occurred on the Ce
3+ sites. Without the presence of Cu, Ce
3+ would lead to oxidation into Ce
4+. However, in contact with Ce
4+, Cu
0 reacted to form Cu
+ and Ce
3+, sustaining ceria in the more active state. The cycle is closed when Cu
+ reduced to Cu
0 [49]. This synergistic effect afforded the catalyst with high reactivity in the RWGS reactions. The chemisorption of CO
2 molecules on CeO
2 at RT as studied using in situ DRIFTS indicated adsorption at both the Ce
3+ and Ce
4+ sites, although adsorption was also found at the oxygen sites that resulted in carbonates and bicarbonates species
[50]. In the same study, the CO
2 chemisorption on TiO
2 under similar reaction conditions and instrumentation was observed at both Ti
3+ and Ti
4+ sites, exhibiting O–C–O vibrations at 1667 and 1248 cm
−1 and 2339–2345 cm
−1, respectively
[50]. The CO
2 molecules adsorbed at Ti
3+ sites formed CO
2− species, which concentration increased with the amount of oxygen vacancies present. Like with CeO
2, CO
2 chemisorption at the oxygen sites formed carbonates and bicarbonates species. It was observed that the interaction between TiO
2 and CO
2 molecules is somewhat weak compared with that of CeO
2. Such weak interactions can be improved by doping TiO
2 with CeO
2. CeO
2 doping can improve the interaction of TiO
2 with CO
2 as a result of the introduction of Ce
3+, which strengthens the bonding of CO
2 with catalyst surfaces and enhances the production of bidentate carbon species that can readily be transformed to surface CO
2− in the presence of H
2O under solar irradiation. The formation of adsorbed species of CO
2 over CeO
2/TiO
2 could be attributed to the binding of CO
2 species to Ti/Ce atoms that have reductive capabilities under photo-irradiation. Furthermore, the Ce
3+ availability from CeO
2 facilitates photogenerated charge separation; thus, the CO
2 adsorption and enhanced charge separation can be tuned for increased activity of CeO
2/TiO
2 catalyst
[51]. The surface area of materials positively correlates with their adsorption capacity. It was found that the Bi
12O
17Cl
2 nanotubes had a higher adsorption capacity for CO
2 (~4.3 times) than bulk Bi
12O
17Cl
2 due to the higher BET specific surface area of the former. As a result, the effective adsorption of CO
2 on Bi
12O
17Cl
2 nanotubes over bulk Bi
12O
17Cl
2 favored the photocatalytic process
[52]. In addition, the high surface area correlated with strong adsorption. Weak chemisorption of CO
2 has been reported for CeO
2 nanostructures with low exposed surface area
[50]. Mesostructured photocatalyst displayed improved activity for CO
2 reduction into CH
4 due to the presence of high specific surface area and well-developed mesostructure that enhanced adsorption of CO
2 [53]. Highly mesoporous In(OH)
3 synthesized via the sol-gel hydrothermal treatment exhibited ~20-fold higher efficiency for CO
2 reduction in comparison with those lacking mesopores
[54]. It is reported that the methanol activity of the In
2O
3 catalyst could also be improved by increasing the (111) surface area
[55].
2.3.2. Characteristic Adsorption of Representative Metal Oxides
Ceria (CeO
2) has shown catalytic activity in the reduction of CO
2 to liquid fuels and chemicals. It has rich oxygen vacancies and high oxygen storage/release capacity. Several studies demonstrating the interaction of CO
2 with high-surface-area ceria catalysts have been reported. As noted in ref
[56], CO
2 dissociates into CO and an oxygen-containing surface species on the surface Ce
3+ ions, which are considered active sites for CO
2 activation due to the formation of carbonates or inorganic carboxylates. Graciani et al. reported a highly active CeO
x/Cu nanoparticles catalyst for methanol synthesis from CO
2 [57]. The catalyst activated CO
2 as CO
2δ− and exhibited a faster methanol production rate than Cu/ZnO, on which CO
2 was chemisorbed as CO
32−. A study on the CO
2 adsorption sites of CeO
2 (110) surface using DFT was carried out by Cheng et al.
[58]. Reduced and stoichiometric ceria (110) surfaces were compared. Results revealed that CO
2 adsorption on the reduced ceria (110) surface was thermodynamically favored than on the stoichiometric ceria (110) surface. Furthermore, the most stable adsorption configuration consisted of CO
2 adsorbed parallel to the reduced ceria (110) surface at the oxygen vacancy. Upon adsorption, the CO
2 molecule distorted out of the plane and formed carbonates with the remaining oxygen anion at the surface
[58]. It was suggested that the structural changes in the catalyst after CO
2 adsorption were due to charge transfer between the surface and adsorbate molecule. The formation of two different adsorbate species: a carbonate and a weakly bound and linear physisorbed species, were observed upon exposure of reduced CeO
2−x (110) substrates to CO
2 at low temperatures. There was no evidence for the formation of CO
2δ−. Furthermore, based on angle-dependent C K-edge NEXAFS spectra, the most preferred orientation of the adsorbate could not be observed. The physisorbed CO
2 species and carbonate species were completely desorbed at 250 and 500 K, respectively. The authors remarked that it is most unlikely that the activation of CO
2 on the reduced CeO
2−x (110) surface was via breaking the C=O bond to form CO and O. However, on fully oxidized CeO
2 (110), CO
2 adsorbed as a carbonate which was completely decomposed and desorbed as CO
2 at 400 K
[59]. CO
2 adsorbed on the CeO
2 (111) surface formed monodentate carbonate species found to be most stable on CeO
2 at low coverages
[60]. Increasing the CO
2 coverage destabilized the formed species, indicating a mixed adsorption mechanism with both carbonate and linearly adsorbed CO
2 species. Although CeO
2 has been studied for CO
2 reduction reactions, the insights into CO
2 adsorption, activation, and reaction on ceria surfaces are not yet fully understood.
Titania (TiO
2) possesses good photocatalytic properties for many chemical reactions, including CO
2 reduction. Since its first demonstration in the photoelectrochemical CO
2 reduction to formic acid and formaldehyde by Inoue et al.
[61], TiO
2-based materials have attracted great research interests in CO
2 photoreduction reactions. The adsorption properties of CO
2 on both the rutile and anatase phases of TiO
2 have been widely studied using various surface science techniques
[62][63][64][65]. Sorescu et al.
[66] investigated the adsorption and dissociation of CO
2 on an oxidized anatase (101) surface using dispersion-corrected DFT and found CO
2 to adsorbed at a fivefold coordinated Ti site in a tilted configuration. Based on in situ FTIR experiments, the CO
2 adsorption formed CO
32− and CO
2 bonded to Ti, with absorption bands at 1319, 1376, 1462, 1532, 1579, and 2361 cm
−1. The band at 2361 cm
−1 was assigned to adsorbed CO
2 with Ti–O–C–O adsorption configuration
[67]. The 1319 and 1579 cm
−1 bands were assigned to bidentate carbonate, while the band at 1461 cm
−1 was due to monodentate or free carbonate. Under the vacuum condition, the intensities of all of the bands were reduced at 35 °C. The bidentate carbonate was the predominant species for CO
2 on TiO
2.
The scanning tunneling microscopy (STM) enabled a study of the dissociation of CO
2 adsorbed at the oxygen vacancy of TiO
2 (110) at the single-molecule level
[68]. It was found that the electrons injected from the STM tip into the adsorbed CO
2 caused its dissociation into CO and O, and the released O was observed to heal the oxygen vacancy. According to experimental analysis, ~1.4 eV above the conduction band minimum of TiO
2 is needed for the electron induction process to dissociate CO
2. The formation of a transient negative ion by the injected electron is an important step in the CO
2 dissociation, and this can only be possible above the threshold voltage. TiO
2 modified with metal oxide nanoclusters possess enhanced activity to adsorb and convert CO
2 [69][70]. The Bi
2O
3-TiO
2 heterostructures obtained by modifying TiO
2 with Bi had low coordinated Bi sites in the nanoclusters and a valence band edge consisting mainly of Bi–O states due to the presence of the Bi lone pair. Upon interaction of CO
2 with the reduced heterostructures, CO or CO
2− were observed mainly through electron transfer to CO
2, and the Bi
2O
3–TiO
2 heterostructures became oxidized in the process with adsorbed CO
2 in carbonate form
[70]. In a related study, clean or hydroxylated extended rutile and anatase TiO
2 surfaces modified with Cr nanoclusters presented an upshift valence band edge related to the existence of Cr 3d–O 2p interactions, which promoted the CO
2 activation.
[69]. The activated CO
2 molecule reduced its O–C–O angle to 127–132° and increased the C–O bond length to 1.30 Å. It was concluded that the strong CO
2–Cr–O interaction induced the structural distortions.
Iron oxides (FeO
x) are an important component of catalysts for the conversion of CO
2 to hydrocarbons (liquid fuels). The adsorption and activation of CO
2 on FeO
x have been investigated by researchers
[71][72][73]. It is suggested that Fe
2+ and Fe
3+ cations are crucial for CO
2 adsorption. Using TPD, Pavelec et al.
[71] observed a weak interaction between CO
2 and Fe
3O
4 (001) surface. On this surface, CO
2 molecules existed in the physisorbed state as they desorbed at a low temperature (115 K). However, strong CO
2 adsorption was observed on the defects and surface Fe
3+ sites. Weak CO
2 adsorption has also been observed on Fe
3O
4 (111) as investigated by various experimental techniques
[74]. At different CO
2 dosages and temperatures (between 120 and 140 K), TPD experiments suggested CO
2 adsorb very weakly on a regular Fe
3O
4 (111) surface. However, CO
2 chemisorption was also observed but at relatively long CO
2 exposure times
[74][75] via binding to under-coordinated oxygen sites
[75]. The formation of chemisorbed species such as carboxylates and carbonates was facilitated by surface imperfections. Conclusively, FeO
x exhibit weak interaction with CO
2 molecules, and studies are recommended in this direction to adjust its CO
2 adsorption strength.
ZrO
2 has been demonstrated as catalyst support for the CO
2 hydrogenation reactions to a variety of products. In a study on CO
2 hydrogenation on Cu/ZrO
2 catalyst using the first-principles kinetic Monte Carlo simulations by Tang et al.
[76], the authors showed that CO
2 prefers to adsorb on the bare ZrO
2 nanoparticles surface rather than at the Cu/ZrO
2 interface. This led to the bending of the CO
2 molecule with a calculated adsorption energy of 0.69 eV. The stretching of the C–O bonds and charge transfer from the ZrO
2 surface to the antibonding 2π
μ orbital of CO
2 were also observed. On the bare ZrO
2 surface, bidentate bicarbonate (HCO
3) was formed upon CO
2 adsorption based on observable IR frequencies at ~1225, ~1620, and ~3615 cm
−1 [77].
3. Conclusion
CO2 is a kinetically stable molecule that requires high energy input for the C–O bond breaking. Its proper activation can reduce the high energy barrier substantially, easing conversion by various processes. The CO2 activation is an important step that precedes the conversion of CO2 to chemicals and fuels. It can be effected in the presence of a catalyst by altering the CO2 electronic and molecular properties. Upon accepting an extra electron from a substrate, the neutral CO2 molecule forms an anion with a full charge (CO2–) or partial charge (CO2δ–). Some metals and metal oxides are efficient catalysts for CO2 conversion reactions; thus, they should be good for CO2 activation. In general, metal nanoparticles serve as active sites for electron transfer, with certain factors such as change in morphology of metal particles, nanoparticle size, adsorption mode and configuration, and chemical ordering as the CO2 activation marker. The interaction of CO2 with some pure metals is rather weak but can be improved by incorporating promoters (e.g., alkali metals) with low electronegativity. Metal oxide nanoparticles are utilized as supports or as catalysts for CO2 conversion. Their surfaces comprise both metal (Mn+) and oxygen (O2–) ions, which can act as active sites for CO2 activation. They can activate CO2 by coordinating to one or two adjacent metal sites through the terminal oxygen atoms of the CO2 or by interaction of the carbon atom of CO2 with surface oxygen sites. A particularly interesting feature in metal oxides is the oxygen vacancies that facilitate CO2 adsorption and activation.
CO2 is a kinetically stable molecule that requires high energy input for the C–O bond breaking. Its proper activation can reduce the high energy barrier substantially, easing conversion by various processes. The CO2 activation is an important step that precedes the conversion of CO2 to chemicals and fuels. It can be effected in the presence of a catalyst by altering the CO2 electronic and molecular properties. Upon accepting an extra electron from a substrate, the neutral CO2 molecule forms an anion with a full charge (CO2–) or partial charge (CO2δ–). Some metals and metal oxides are efficient catalysts for CO2 conversion reactions; thus, they should be good for CO2 activation. In general, metal nanoparticles serve as active sites for electron transfer, with certain factors such as change in morphology of metal particles, nanoparticle size, adsorption mode and configuration, and chemical ordering as the CO2 activation marker. The interaction of CO2 with some pure metals is rather weak but can be improved by incorporating promoters (e.g., alkali metals) with low electronegativity. Metal oxide nanoparticles are utilized as supports or as catalysts for CO2 conversion. Their surfaces comprise both metal (Mn+) and oxygen (O2–) ions, which can act as active sites for CO2 activation. They can activate CO2 by coordinating to one or two adjacent metal sites through the terminal oxygen atoms of the CO2 or by interaction of the carbon atom of CO2 with surface oxygen sites. A particularly interesting feature in metal oxides is the oxygen vacancies that facilitate CO2 adsorption and activation.