Skip to main content
Wiley Open Access Collection logoLink to Wiley Open Access Collection
. 2025 Jun 11;21(32):2504707. doi: 10.1002/smll.202504707

The Dual‐Active‐Site Catalysts Containing Atomically Dispersed Pr3+ with Ni/CeO2 for CO2 Hydrogenation to Methane

Neha Choudhary 1, Navdeep Srivastava 2, Harshini V Annadata 3, Biplab Ghosh 3, Patrick Da Costa 1,
PMCID: PMC12366274  PMID: 40495724

Abstract

In this study, uniformly dispersed Pr3+ as an isolated atom over Ni/CeO2 catalyst (Ni‐Pr/CeO2) is designed to enhance catalytic activity for CO2 methanation, achieving an impressive 87% conversion with ≈100% CH4 selectivity at 300 °C temperature. In contrast, the traditional Ni/CeO2 and NiPr/CeO2‐imp catalysts exhibit poor conversion and selectivity, highlighting the proof of concept on the advantage of atomic‐scale dispersion. Structural analysis via PXRD, XAS, and XPS confirms the successful incorporation of Pr3+ into the CeO2 lattice by creating defects. XPS and XAS studies further reveal a significant increase in oxygen vacancies, a key factor in enhancing catalytic performance at lower reaction temperatures. STEM‐EDS analysis confirms the ultra‐dispersion of Pr3+ (≈7 wt.%) over CeO2, ensuring a highly active catalyst surface. H2‐TPR and CO2‐TPD results suggest that the Pr3+ doping enhances the catalytic activity by decreasing the reduction temperature and increasing basic sites. Additionally, long‐term stability tests demonstrate no significant loss in activity over 40 h, confirming the catalyst's robustness and recyclability. This work provides critical insights into the structure‐activity relationship of Pr3+‐modified Ni/CeO2 catalysts, emphasizing the role of oxygen vacancies in optimizing CO2 hydrogenation efficiency.

Keywords: CO2 methanation, interfacial sites, Ni catalyst, oxygen vacancy, single‐atom catalysts


Herein, the Ni‐Pr/CeO2 catalyst is reported for an efficient catalytic conversion of CO2 to methane with 87% conversion and 100% selectivity. STEM‐EDS analysis reveals the uniform dispersion of Pr3+ ions on CeO2 support. Doping of Pr3+ over CeO2 generates oxygen vacancies, which leads to excellent catalytic performance with long‐run activity with no significant loss in activity.

graphic file with name SMLL-21-2504707-g003.jpg

1. Introduction

In recent years, the emission of carbon dioxide (CO2) from traditional fossil fuels has impacted the global climate and ecosystem.[ 1 , 2 ] Hence, the conversion of CO2 into value‐added chemicals, including methanol, ethanol, methane, and long‐chain hydrocarbons, has drawn attention.[ 3 , 4 ] CO2 conversion into synthetic renewable energy alternatives using renewable H2 is a promising strategy to deal with the issue of CO2 emission.[ 5 , 6 ] In this regard, the thermal catalytic approach of CO2 to methane conversion over photo‐ and electro‐catalytic approach is more sustainable and practical for industrial application.[ 7 , 8 , 9 ] For selective CO2 methanation, a low‐temperature reaction is more favorable to avoid the CO formation over methane from CO2. The methanation process is exothermic, and at high temperature, the selectivity for methane as a product decreases due to thermodynamics.[ 10 , 11 , 12 ]

Since, at low‐reaction temperatures, high methane production is difficult due to kinetic limitations,[ 10 , 13 ] various noble metals and non‐noble metals have been explored and utilized for methane production.[ 14 , 15 ] Rh, Ru, Ag, Pd, and Pt‐based catalysts have shown excellent activity with good selectivity at low reaction temperatures.[ 16 , 17 , 18 ] However, their high cost limits their large‐scale application by making the overall process expensive. On the other hand, Ni‐based catalysts have drawn great attention owing to their low cost and good catalytic activity. Although, they usually suffer from poor catalytic performance at temperatures less than 300 °C.

To deal with this issue, various strategies have been opted by varying synthetic methods, amount of active metal or dopant, support materials (metal oxides, MOFs, carbon‐based material), and tuning shape or morphology, etc, to achieve high conversion and selectivity at low reaction temperature.[ 19 , 20 , 21 ] It was reported that Ni nanoparticles supported over metal oxides showed catalytic performance owing to their enhanced oxygen vacancies, improved basic sites, and, consequently, increased hydrogen spillover.[ 22 , 23 , 24 ] Ni nanoparticles (NPs) over ceria support demonstrated to be good catalysts due to the formation of interfacial sites, which maximize the synergistic effect between existing metals.[ 25 , 26 ]

To improve the catalytic activity at low reaction temperatures for tuning their electronic properties, the doping of active metal has been demonstrated. The doping of active metal with Ni over ceria could enhance the surface oxygen mobility by creating more Ce3+ ions on the surface, which as a result, supports the formate pathway during the reaction and promotes the selectivity toward methane as a product.[ 27 , 28 ] Xu et al. demonstrated that incorporating Cr3+ into CeO2 enhances the formation of surface oxygen vacancies, Ce3+ species, and hydroxyl groups, thereby facilitating the formate‐mediated pathway for methane production at low temperatures.[ 29 ] Moreover, Y‐doped CeO2 with Ni nanoparticles were prepared by Sun et al. and they observed that the oxygen vacancies were highly affected by the particle size of Ni and improved the metal‐support interaction.[ 30 ] Additionally, Ru single atoms were doped over ceria support and impregnated with Ni NPs where Zhang et al. observed that Ru1 SACs were able to convert CO2 to CO, and Ni NPs boosted the sequential conversion to methane product.[ 7 ] They concluded that the simultaneous presence of Ru1 and Ni sites significantly enhances the overall reaction performance.

Lanthanide doping over ceria with Ni NPs was also reported for enhanced catalytic performance. Liu et al. prepared a series of Sm‐doped CeO2 supports with varying Samarium loading to optimize the metal‐support interaction in Ni‐based catalysts. Their findings indicated that Ni/Sm0.25Ce0.75O2−δ, showed excellent catalytic performance, which exhibited the highest metallic Ni surface area and the largest active interface.[ 31 ] Eu3+ doping promoted Ni/CeO2 catalyst was also analyzed where they observed the more interfacial sites improved the catalytic performance by promoting bidentate carbonate formation and consequently leading to faster hydrogenation at low‐temperature.[ 10 ] Similarly, Ni/La‐CeO2 was prepared by Zhang et al., where the incorporation of La species into the CeO2 support, followed by calcination at 600 °C (CeO2‐La‐600), led to the formation of a La‐Ce‐O solid solution with a thin La2O2CO3 layer on the surface, resulting in an increased number of basic sites and oxygen vacancies.[ 32 ] This solid solution promoted the adsorption and dissociation of CO2, which led to enhanced catalytic performance. Moreover, mixed metal oxides of Sm3+, Pr3+, and Mg2+ cations over Ni/CeO2 catalyst were prepared by Siakavelas et al.[ 33 ] for comparing them for methanation, and it was observed that Ni/Pr‐Ce showed superior catalytic activity over other synthesized materials. It was observed that the doping of Pr3+ possesses more oxygen vacancies than Sm and Mg cations, and the presence of Pr2O3‐CeO2 also enhances the dispersion of Ni sites by restricting agglomeration.

On the basis of previous reports, we synthesized uniformly dispersed Pr doped over CeO2 and decorated with Ni nanoparticles (named Ni‐Pr/CeO2), where first atomically dispersed Pr/CeO2 was prepared using the co‐precipitation method and further covered with Ni nanoparticles for enhanced catalytic activity. The presence of both Ni and Pr promoted the catalytic performance owing to the synergistic effect between the metals. Also, when this material was compared with an undoped Ni/CeO2 catalyst then, the Ni‐Pr/CeO2 showed superior catalytic performance with excellent selectivity toward methane as a product. The catalyst is extensively characterized via various techniques like XPS, STEM‐HAADF, EXAFS, XANES, H2‐TPR, CO2‐TPD, and H2‐TPD. XPS analysis confirms the increase in oxygen vacancies after doping Pr3+, whereas STEM‐EDX confirms the uniform dispersion of Pr3+ ions over ceria support. The catalyst was tested for methane production where at 300 °C temperature, Ni‐Pr/CeO2 showed excellent catalytic conversion, i.e., 87% with 100% selectivity. These results confirm that the doping of Pr3+ over ceria with Ni nanoparticles plays an important role and provides more active sites. The effect of high oxygen mobility and basic sites was also analyzed in this study.

2. Results and Discussion

2.1. Structural Characterizations of Catalysts

In order to analyze the metal loadings of Ni and Pr over ceria, ICP‐OES was performed (Table S1, Supporting Information). As expected, the Pr and Ni loading in Ni‐Pr/CeO2 catalysts was found to be 8 and 7 wt.%, respectively.

X‐ray diffractograms of both fresh and reduced CeO2, Pr/CeO2, Ni‐Pr/CeO2, and Ni/CeO2, as reported in Figure 1 . All the catalysts showed typical peaks of fluorite structure of CeO2 with diffraction peaks at 28.89°, 33.13°, 47.51°, 56.31°, 59.1°, 69.47°, 76.73°, 78.98° and 88.44° corresponds to (111), (200), (220), (311), (222), (400), (331), (420) and (422) planes in agreement with JCPDS# 43–1002.[ 27 , 34 ] As indicated in Figure 1A, there was no prominent peak of Pr was observed in the case of fresh Pr/CeO2 and Ni‐Pr/CeO2, due to low Pr loading and similar crystal lattice of Pr and Ce.[ 35 , 36 ] Further, the weak diffraction peaks of NiO were observed in the case of fresh Ni/CeO2 and Ni‐Pr/CeO2 at 37.36°, 43.6° and 63.04° for (111), (200) and (220) planes confirmed with JCPDS# 44–1159.[ 30 , 37 ] When the major diffraction plane of CeO2 (111) was enlarged to compare, there was a shift in the case of Ni‐Pr/CeO2 was observed toward a lower 2θ value, which confirms the incorporation of Pr3+ ion in ceria lattice (Figure 1B).[ 36 , 38 ] This shift in d(111) spacing may be caused by the incorporation of Pr3+ cations (1.27 Å) in the place of Ce4+ (0.97 Å) ions in typical CeO2 fluorite structure, and as a result, lattice expansion leads to significant decrease in 2θ value.[ 33 , 39 , 40 ] This hypothesis of lattice expansion of CeO2 can be evidenced by the crystallite size calculations of fresh and reduced catalysts for the d(111) plane of ceria (Table S2, Supporting Information). The full‐width half maxima (FWHM) for undoped CeO2 and Ni/CeO2 were lower than the doped Ni‐Pr/CeO2 for CeO2 (111) plane, representing higher crystallite size for CeO2 than Ni‐Pr/CeO2 and Pr/CeO2 catalysts. For reduced Ni/CeO2 and Ni‐Pr/CeO2 catalysts, the diffraction peaks at 44.4° and 52.09° correspond to (111) and (020) planes for Ni(0) observed in agreement with JCPDS# 04–0850 as shown in Figure 1C.[ 10 , 41 ] Similar to the fresh catalyst, in the case of the reduced catalyst, Ni/CeO2 has a higher crystallite size than the Ni‐Pr/CeO2 catalyst, indicating that the doping of Pr3+ ions enhances the dispersion of Ni species over ceria by inhibiting the growth of ceria and NiO. Additionally, for comparison, the NiPr/CeO2‐imp catalyst was also analyzed, as depicted in Figure S1 (Supporting Information). The peaks of the fluorite structure of CeO2 were observed in the case of both fresh and reduced catalysts. Although the fresh NiPr/CeO2‐imp catalyst displayed peaks of NiO corresponding to JCPDS# 44–1159, the reduced catalyst showed the peaks of Ni(0) metallic as expected. There was no obvious peak of Pr observed in both fresh and reduced catalysts.

Figure 1.

Figure 1

PXRD of A) fresh catalysts, B) shifting of (111) plane of CeO2 after incorporation of NiO and Pr, and C) reduced catalysts.

N2 adsorption–desorption analysis was performed to estimate the surface area, pore size, and pore volume (Figure S2, Supporting Information). The results are in good agreement with PXRD results, where the incorporation of Pr3+ ions enhanced the surface area from 23 to 30 m2 g−1 in Ni‐Pr/CeO2 catalyst when compared with Ni/CeO2. On the other hand, the impregnation of Ni over Pr/CeO2 decreases the surface area from 37 to 30 m2 g−1 in NiPr/CeO2‐imp. The doping of Pr3+ ions generates defects on the surface of CeO2 and creates more surface vacancies, which leads to a higher surface area of Ni‐Pr/CeO2 than Ni/CeO2.[ 10 ] Additionally, this increase in surface area in the case of Ni‐Pr/CeO2 is in good agreement with the crystallite size as mentioned in Table S2 (Supporting Information) that as the crystallite size decreases, the surface area increases.[ 42 , 43 ] As shown in Figure S2A (Supporting Information), adsorption–desorption isotherms displayed type‐IV isotherm with H4 hysteresis loops, confirming the mesoporous structure of the catalysts.[ 44 , 45 ] This result of the presence of mesopore is further confirmed by BJH pore size distribution values in Figure S2B (Supporting Information), which ranges from 10–30 nm pore diameter. All catalysts have similar patterns in pore size distribution and BET desorption isotherms, maybe owing to having similar support material in the dominant amount.

To analyze the reduction of the catalysts, H2 TPR analysis was performed as shown in Figure 2A. Undoped CeO2 support showed three peaks in a broad temperature range from 350–580 °C, i.e., 357, 420, and 548 °C, indicating the removal of surface oxygen with a reduction of Ce4+ to Ce3+.[ 10 , 46 ] When Pr/CeO2 was analyzed where two major peaks were observed at higher temperatures, i.e., 488 and 551 °C, indicating the reduction of oxygen species from Pr‐Ce mixed oxide. In the case of Ni/CeO2, Ni‐Pr/CeO2, and NiPr/CeO2‐imp catalysts, the minor peaks between 230–300 °C represent the reduction of reactive surface oxygen on ceria support.[ 28 , 47 ] Further, the broad peak between 300–450 °C corresponds to the reduction of strongly bounded NiO clusters was observed.[ 48 ] It was reported that based on the size of NiO nanoparticles, the reduction temperature was highly influenced. Nevertheless, it was assumed that the removal of surface oxygen occurs in a similar temperature range (200–300 °C), which might be affecting the reduction peaks of NiO in the case of Pr3+ doped catalyst.[ 49 , 50 ] It was observed that the Pr‐doped catalyst displayed a major reduction peak from 300 to 450 °C temperature at a comparatively lower temperature than the undoped Ni/CeO2 catalyst. This data revealed that the doping of Pr3+ might enhance the metal support interaction between NiO and ceria support.[ 35 , 51 ] The split peak broadening in Ni‐Pr/CeO2 confirmed that the doping of Pr3+ increases the oxygen vacancies on ceria support.[ 10 , 28 ] In the case of impregnated NiPr/CeO2‐imp catalyst, the size of Ni nanoparticles is expected to be high, which leads to the weak interaction between NiO and ceria. Consequently, a major broad peak at 400 °C was observed.[ 28 , 52 ] Additionally, the reduction peak at higher temperatures (450–550 °C) in Ni‐Pr/CeO2 catalyst indicates the doping of Pr3+ into the lattice of CeO2 support owing to enhanced reducibility of CeO2 support, and this can be compared with Pr/CeO2 catalyst.[ 28 , 53 ] This result is also confirmed with H2 consumption calculation which indicates that the H2 consumption of the Ni‐Pr/CeO2 catalyst was higher than that of the Ni/CeO2 catalyst, i.e., 163 and 104 µmol g−1 respectively. In summary, the doping of Pr3+ improves the oxygen vacancy as well as the reducibility of the CeO2 support.

Figure 2.

Figure 2

A) H2‐TPR, B) CO2‐TPD, and C) H2‐TPD profile for all the catalysts.

To analyze the basic sites of the catalyst, CO2‐TPD was performed for all the catalysts, as reported in Figure 2B. The surface basicity plays an important role in determining the CO2 dissociation and hydrogen activity of the catalyst.[ 54 , 55 ] Based on the desorption curve, the temperature range was divided into three major regions, i.e., 55–150 °C, 150–300 °C, and 300–500 °C corresponds to I, II, and III types. The basic sites were calculated using the area under the curve values for each of the samples (Table 1 ). The total basic sites were obtained highest in Ni‐Pr/CeO2 than Ni/CeO2 and impregnated NiPr/CeO2‐imp catalysts. Basic sites between the 300–500 °C (type III) temperature range play an important role in CO2 adsorption–desorption and, consequently, influence the catalytic activity.[ 56 , 57 ] As mentioned in Table 1, type III basic sites are surprisingly high in the case of Ni‐Pr/CeO2 catalyst, indicating that the doping of Pr3+ enhances the basic sites, which is in good agreement with H2‐TPR results.

Table 1.

The distribution of basic sites is estimated from the CO2 TPD profile.

Catalyst Basic sites [µmol g−1]
I (55–150 °C) II (150–300 °C) III (300–500 °C) Total
Ni/CeO2 2.15 11.08 4.25 17.43
Ni‐Pr/CeO2 4.17 10.51 36.61 51.29
NiPr/CeO2‐imp 1.79 12.03 7.09 20.92

H2‐TPD analysis was also performed for all the catalysts to analyze the hydrogen desorption affinity of the catalyst (Figure 2C). All Ni‐based catalysts mainly showed three peaks, i.e., below 250 °C, 250–400 °C, and above 400 °C. The peak intensity in all three catalysts varies based on their interaction with metal support. In Pr/CeO2, the peak below 300 °C corresponds to desorbed hydrogen from Ni metal was absent and can be comparable with other Ni‐based catalysts. The intense peaks at low temperatures below 250 °C in Ni/CeO2 catalyst showed the desorption of hydrogen from active metal species, confirming the strong interaction between Ni and ceria support.[ 7 ] The peak at higher temperature in all three Ni‐based catalysts above 400 °C confirmed the strong interaction between Pr‐Ni with ceria support, which is absent in the case of Pr/CeO2. This also confirms that the synergistic effect of Ni and Pr improves the hydrogen desorption in catalysts. In both Ni‐Pr/CeO2 and NiPr/CeO2‐imp catalysts, a broad peak above 250–400 °C showed hydrogen desorption from ceria support. This could be hydrogen spillover due to the presence of Pr3+.[ 7 , 10 , 47 ] This result is in agreement with the H2‐TPR result, where Pr3+ doping over ceria support enhances the reducibility and H2 spillover over, creating oxygen vacancy.[ 28 , 58 ] Overall, doping of Pr3+ with the presence of Ni nanoparticles could improve the chemisorption of hydrogen over the catalyst surface.

Additionally, the morphological analysis was performed on reduced samples using High‐resolution Transmission electron microscope (HR‐TEM) analysis (Figure 3 ). In all the catalysts, lattice fringes of CeO2 support can clearly be seen in the inset image in Figure 3 for reduced Pr/CeO2, Ni/CeO2, and Ni‐Pr/CeO2 catalysts. However, it was difficult to analyze the particle size from the HR‐TEM images owing to the similar contrast of Ni and ceria.[ 7 , 59 , 60 ]

Figure 3.

Figure 3

HR‐TEM images of A) Ni/CeO2, B) Pr/CeO2, and C) Ni‐Pr/CeO2 catalysts at 200, 100, and 50 nm magnification.

Aberrated corrected scanning transmission electron microscopy (AC‐STEM) imaging and elemental analysis EDX analysis were performed to confirm the presence of Pr, Ni, Ce, and O elements (Figure 4 ; Figures S3–S5, Supporting Information). AC‐STEM in annular dark field (ADF) mode was performed for Pr/CeO2, where no cluster of Pr was observed, confirming the dispersion of Pr over ceria as shown in Figure S3 (Supporting Information) and due to microscopic limitations and similar atomic numbers of Pr and Ce, Pr atoms cannot be observed.[ 1 , 23 ] The HAADF images and EDX analysis with color mapping were performed at different magnifications at different regions of Pr/CeO2 catalysts to analyze the uniform dispersion of Pr over ceria. The results revealed that in each elemental map, the distribution of Pr over ceria was found to be uniform, i.e., ≈8 wt.%, which was in good agreement with ICP‐OES results (Table S1, Supporting Information). As shown in Figure 4, Ni‐Pr/CeO2 shows ≈7 wt.% of Pr with varied amounts of Ce, Ni, and O. The variation in the amount of Ni and Ce could be justified due to the presence of their oxides in the catalyst. It is also confirmed with EDX analysis that Ni NPs and Pr atoms are not overlapped and are well dispersed over ceria support. In all the elemental maps, the amount of Pr was found to be consistent, which was again confirmed with ICP‐OES results. In summary, it was observed that the Pr is uniformly dispersed over CeO2, which is consistent even after the impregnation of NiO NPs. For comparison, Ni/CeO2 and NiPr/CeO2‐imp catalysts were also analyzed using STEM‐EDX analysis. In both cases, the morphology of particles was quite distinct and not consistent (Figures S4 and S5, Supporting Information). Also, the amount of Ni and Pr was not consistent even at low magnification, i.e., 100 nm. In EDX analysis of Ni/CeO2 and NiPr/CeO2‐imp impregnated catalyst, it is revealed that both Ni and Pr wt.% were varied with different magnifications, which could be related to the presence of their oxides and in agglomerated form. This further confirms the importance of the precise synthesis of Ni‐Pr/CeO2 uniformly dispersed catalysts.

Figure 4.

Figure 4

STEM mapping of Nickel, Praseodymium, Cerium, and Oxygen elements of Ni‐Pr/CeO2 catalyst at different regions at higher magnifications with scale bars of A) 100 nm, B) 250 nm, C) 250 nm, and D) 500 nm.

The local coordination environment and oxidation states of Ni, Pr, and Ce were analyzed using Ni K‐edge, Ce L3‐edge, and Pr L3‐edge X‐ray Absorption Near‐Edge Structure (XANES) and Extended X‐ray Absorption Fine Structure (EXAFS) spectroscopy, as shown in Figures 5 and S6 (Supporting Information). The XANES spectra of Ni foil show the edge at ≈8333 eV, characteristic of metallic Ni (Figure 5A).[ 61 ] In contrast, both Ni/CeO2 and Ni‐Pr/CeO2 catalysts exhibit a higher energy edge shift and a more intense absorption peak than Ni foil but a less intense peak compared to NiO, indicating a predominant Ni2+ oxidation state.[ 10 , 62 ] However, the XANES spectrum of Ni‐Pr/CeO2, shifted to slightly higher energy than Ni foil and lower energy than Ni/CeO2 catalysts, suggesting cationic state Ni2+δ or mixed oxidation state (Ni2+ / Ni3+) due to the passivation or charge transfer of Ni metal to ceria support.[ 7 , 62 , 63 ] The Fourier transform EXAFS R‐space spectra (Figure 5B) reveal that Ni‐Ni coordination, characteristic of metallic Ni, is absent in both Ni/CeO2 and Ni‐Pr/CeO2 catalysts. Instead, a distinct Ni‐O peak, consistent with the NiO reference, is observed. The EXAFS fitting results (Table 2 ) confirm that both Ni‐Ni and Ni‐O coordination numbers in the catalysts match those of NiO nanoparticles, suggesting that Ni exists primarily as dispersed NiO‐like species, rather than forming a strong interaction with the ceria lattice.[ 64 ] The best fits to the EXAFS data, performed in R‐space using a NiO rocksalt structure model, confirm that the Ni‐O coordination number (CN) is 5.8 ± 0.2 for Ni/CeO2 and 5.9 ± 1.6 for Ni‐Pr/CeO2, comparable to the reference NiO standard (CN ≈6).[ 65 , 66 ] The ratio CN(Ni‐O)/CN(Ni‐Ni) in Ni/CeO2 (0.49) and Ni‐Pr/CeO2 (0.50) is also similar to NiO, confirming that the Ni‐O coordination originates from NiO nanoparticles rather than strong bonding with ceria support. This result revealed that Ni─O bonds are coming from only NiO nanoparticles of both the catalysts and confirmed the interaction of Ni with interfacial O atoms only, not from ceria support, suggesting that Ni exists primarily as dispersed NiO‐like species, rather than forming a strong interaction with the ceria support.[ 25 , 67 ] Upon Pr doping, a peak splitting in the Ni─O bond is observed, which may arise due to an increase in positive charge on Ni. This is further corroborated by the slightly higher Ni‐Ni coordination number (11.7 ± 3.1) in Ni‐Pr/CeO2 than Ni/CeO2 (11.7 ± 0.5).[ 10 ] The Pr L3‐edge XANES spectrum (Figure 5C) of Ni‐Pr/CeO2 was compared to a Pr2O3 reference. A peak at 5970 eV, assigned to Pr3+, was observed with a higher intensity than in Pr2O3, indicating an increased Pr3+ population.[ 53 , 68 ] Ce L3‐edge XANES spectra of Ni‐Pr/CeO2 and Ni/CeO2 catalysts exhibit peaks at 5732 and 5738 eV corresponding to Ce4+ oxidation state (Figure 5D).[ 69 , 70 ] The oxidation state of cerium in CeO2, as determined by XANES, remains a subject of debate within the scientific community due to varying interpretations of the 2p → 5d excitation.[ 71 , 72 ] The peak at 5732 and 5739 eV corresponds to 2p3/2→(4fL)5d and 2p3/2→(4f0)5d emissions, respectively, where L represents oxygen vacancy or hole in ceria lattice.[ 73 , 74 ] However, the hybridization between Ce 4f and O 2p orbitals facilitates electron density transfer from oxygen to cerium, resulting in a mixed oxidation state.[ 75 , 76 ] The white line intensity of the CeO2 standard is higher than Ni/CeO2 and Ni‐Pr/CeO2 catalysts (Figure 5D,E) indicating the reduction of Ce4+ to Ce3+ state.[ 74 ]

Figure 5.

Figure 5

A,B) Normalized XANES Ni K‐edge with Fourier transform spectra, C)Pr L3‐edge XANES, D,E) Ce L3‐edge XANES, and Fourier transform spectra.

Table 2.

Ni K‐edge fitting results.

Sample Path R (Å) CN σ 2 R‐factor
NiO Ni‐O 2.06 ± 0.01 6 (fixed) 0.006 0.010
Ni‐Ni 2.95 ± 0.02 12 (fixed) 0.007
Ni/CeO2 Ni‐O 2.06 ± 0.03 5.8 ± 0.2 0.006 0.008
Ni‐Ni 2.95 ± 0.02 11.7 ± 0.5 0.006
Ni‐Pr/CeO2 Ni‐O 2.06 ± 0.03 5.9 ± 1.6 0.005 0.014
Ni‐Ni 2.95 ± 0.02 11.7 ± 3.1 0.003

Where, R: interatomic distance; CN: coordination number; σ 2: Debye‐Waller factor and R‐factor: goodness of fit.

Further, the best fits of EXAFS data were performed in R‐space for CeO2, Ni/CeO2, and Ni‐Pr/CeO2, and the obtained parameters are shown in Table 3 . This result revealed the increment of Ce─O bond length in Ni‐Pr/CeO2 after doping of Pr3+ ion when compared with Ni/CeO2 and CeO2, indicating isolated Pr3+ ions over ceria support in Ni‐Pr/CeO2 catalyst.[ 1 , 53 , 77 , 78 ] Also, a decrease in Ce‐O coordination number from 6.8 ± 2.9 (Ni/CeO2) to 4.6 ± 2.0 (Ni‐Pr/CeO2), confirming increased oxygen defect formation upon Pr3+ incorporation.

Table 3.

Ce L3‐edge fitting results.

Sample Path R (Å) CN σ 2 R‐factor
CeO2 Ce‐O 2.30 ± 0.03 8 (fixed) 0.016 0.014
Ni/CeO2 Ce‐O 2.29 ± 0.04 6.8 ± 2.9 0.011 0.018
Ni‐Pr/CeO2 Ce‐O 2.33 ± 0.04 4.6 ± 2.0 0.005 0.012

To further distinguish overlapping scattering contributions, wavelet transform (WT) analysis of the k3‐weighted EXAFS spectra was performed as shown in Figure 6 . In NiO, Ni/CeO2, and Ni‐Pr/CeO2, two lobes corresponding to Ni‐Ni and Ni‐O shells were observed (Figure 6A–D). Compared to Ni foil, the Ni‐Ni feature is significantly weaker in Ni/CeO2, and Ni‐Pr/CeO2, indicating a high dispersion of Ni species rather than bulk Ni clusters. Meanwhile, the Ni‐O signal is more pronounced, suggesting that Ni is predominantly coordinated with oxygen within the catalysts. The Ce L3‐edge WT analysis further refined our understanding of the structural changes induced by Ni and Pr doping in CeO2, as shown in Figure 6E–G. The WT spectra of CeO2, Ni/CeO2, and Ni‐Pr/CeO2 revealed systematic shifts in the intensity and position of scattering features, corresponding to variations in Ce‐O and Ce‐Ce interactions.[ 77 ] In pure CeO2, the dominant Ce‐O scattering feature remained well‐defined, but with Ni incorporation (Ni/CeO2), a broadening and shift toward lower k‐space values indicated increased disorder and a higher fraction of Ce3+ species.[ 79 , 80 ] This trend became even more pronounced in Ni‐Pr/CeO2, where the Ce‐O contribution weakened, confirming an increase in oxygen vacancies. The distinct WT signature of Ni‐Pr/CeO2 reflected a more disrupted local environment, consistent with more defective and catalytically active ceria support.

Figure 6.

Figure 6

Morlet wavelet transforms of NiO A), Ni foil B), Ni/CeO2 C), and Ni‐Pr/CeO2 D) for Ni K‐edge and CeO2 E), Ni/CeO2 F) and Ni‐Pr/CeO2 G) for Ce L3‐edge.

X‐ray photoelectron spectroscopy (XPS) was performed on reduced Ni‐Pr/CeO2 and Ni/CeO2 catalysts for Ni 2p, Ce 3d, and O 1s spectra, as shown in Figure 7 . The deconvolution of all obtained spectra was done considering 284.8 eV as a reference. The Ni 2p spectra of Ni‐Pr/CeO2 displayed a peak for metallic Ni(0) at 853.16 eV and for Ni(+2) at 854.16 and 860.08 eV as shown in Figure 7A, whereas in Ni/CeO2, the peaks at 853.35 eV for metallic Ni(0) and 851.1, 855.02 and 860.1 eV corresponds to Ni2+.[ 7 , 81 , 82 ] The slight shift toward lower binding energy in the case of Ni‐Pr/CeO2 corresponds to a shift in electron density after doping of Pr3+ over ceria. This result also suggests that Pr doping enhances electron density at the Ni site in comparison to the undoped Ni site, which helps to enhance the dissociation of H2 and CO2 on the catalyst surface.[ 7 , 10 , 32 ] The ratio between Ni(0)/Ni(+2) was also analyzed, which revealed that in Ni‐Pr/CeO2, more metallic content present than Ni/CeO2 (Table 4 ). Nevertheless, the oxidation may occur due to fast surface oxidation of Ni in between recovery of the sample and analysis time.

Figure 7.

Figure 7

XPS spectra of A) Ni 2p, B) Ce 3d, and C) O 1s for Ni/CeO2 and Ni‐Pr/CeO2 catalysts.

Table 4.

Surface quantification for catalysts using XPS analysis.

Sample Ni0/Ni2+ Ce3+/Ce3++Ce4+ Ce3+/Ce4+ Oads/(Oads+Olatt)
Ni/CeO2 0.75 71.06 2.02 24.91
Ni‐Pr/CeO2 3.26 76.41 4.98 33.09

The Ce 3d spectra were also performed which showed peaks at 880.46, 884.16, 899.54, 903.14 eV for Ce3+ and at 897.05, 906.70 eV for Ce4+ in Ni‐Pr/CeO2 catalysts whereas at 880.27, 884.30, 899.49 and 902.56 eV for Ce3+ and at 897.21, 905.34 and 915.33 eV for Ce4+ cations (Figure 7B).[ 29 , 83 ] Furthermore, to analyze the H‐spillover effect, the Ce3+/Ce3++Ce4+ ratio was calculated using the integral area under the peaks, presented in Table 4. It was reported that for Ni‐Pr/CeO2 catalyst showed a higher value than Ni/CeO2, suggesting that Pr3+ doping enhances the interfacial sites as well as surface‐absorbed oxygen.[ 84 ] This may be caused by the H‐spillover effect where Ce3+ ions increase which is also confirmed with H2‐TPD results. Additionally, O 1s spectra indicate the major peak at ≈528.6 and ≈530.7 eV, corresponding to lattice oxygen (Olatt) and surface‐adsorbed oxygen (Oads) for both Ni/CeO2 and Ni‐Pr/CeO2 catalysts (Figure 7C).[ 85 , 86 ] The Oads/(Oads+Olatt) was calculated using the integral area to analyze the oxygen vacancies at the surface of the catalyst, as mentioned in Table 4.

The results revealed that doping of Pr3+ enhances the oxygen vacancies represented by a higher ratio for Oads/(Oads+Olatt). Overall, these findings suggest that the doping of Pr3+ promotes the formation of oxygen vacancies by forming Ce3+ ions in the Ni‐Pr/CeO2 catalyst. The higher Ce3+ fraction in Ni‐Pr/CeO2(76.41%) compared to Ni/CeO2 (71.06%) is consistent with EXAFS data, reinforcing the conclusion that Pr doping promotes defect formation in ceria, leading to increased oxygen vacancy concentrations.[ 27 , 36 , 53 ]

2.2. Catalytic Results

All characterized catalysts were further tested for CO2 conversion to methane at 25000 h−1 GHSV with varying temperatures from 250–450 °C as shown in Figure 8 . In Pr/CeO2, the conversion as well as selectivity was significantly low owing to the formation of more CO than CH4 as a product (Figure 8A,B). This result was consistent even at higher temperatures, i.e., 350–450 °C. The desorption of CO was maybe easy due to weaker binding with Pr sites in the Pr/CeO2 catalyst. It was reported that the higher amount of Pr over ceria affects both the conversion and selectivity of methane.[ 35 , 38 , 53 ] Furthermore, the atomically dispersed Ni‐Pr/CeO2 catalyst showed highest catalytic activity over undoped Ni/CeO2. The doping of Pr3+ over ceria enhances the catalytic activity drastically from 53 to 80%, even at 250 °C temperature. Even at 300 °C, the Ni‐Pr/CeO2 catalyst showed excellent 87% conversion with ≈100% selectivity toward methane product. When the catalytic temperature increased from 250–450 °C, the conversion increased 53%, 87%, 82%, 80%, and 77% at 250, 300, 350, 400 and 450 °C temperatures, respectively. This result revealed that the doping of Pr3+ plays an important role by enhancing the oxygen vacancies and hydrogen spillover at low reaction temperatures, as discussed above.[ 33 , 53 ] When the catalytic activity was compared with an impregnated NiPr/CeO2‐imp catalyst, only 37% conversion was obtained at 300 °C temperature with a decrease in selectivity. This result is in good agreement with other results presented in this study, where Pr/CeO2 showed activity toward CO formation, and Ni/CeO2 showed moderate activity. The trend of catalytic activity was as follows: Ni‐Pr/CeO2 > Ni/CeO2 > NiPr/CeO2 > Pr/CeO2.

Figure 8.

Figure 8

Methanation catalytic test results for all catalysts A) conversion and B) selectivity.

The catalytic performance of Ni‐Pr/CeO2 catalyst is superior over previously reported Pr, Ni, and CeO2‐based catalysts, as shown in Table S3 (Supporting Information). Tsiotsias et al. reported Pr‐based three catalysts (10 mol% Pr loading) using different synthesis methods at 350 °C, the maximum conversion was 77% with 99% selectivity for methane production at 25 000 ml g h−1 WHSV, whereas at 300 °C the conversion was only 46%, 33%, 71%, respectively for Ni/CSG, Ni/PC and Ni/MPC (Entrys 1–3).[ 39 ] Another study utilized the citrate sol‐gel method with Pr loadings ranging from 5–50 atomic % along with Ni and ceria, achieving only 45–21% conversion at 300 °C (Entrys 4–7).[ 38 ] The findings indicated that increasing the Pr content led to a decline in both conversion and selectivity. Siakavelas et al. prepared a catalyst using the microwave method, followed by the sol‐gel method, i.e., Ni/Pr‐Ce, which showed only 24% conversion with 25 000 mL g h−1 weight basis GHSV (Entry 8).[ 33 ] In another report, they utilized multimetallic catalytic system for methanation, i.e., Ni/La‐Pr‐CeO2 where 10% Ni, 5% La2O3 and 10% Pr2O3‐CeO2 was prepared using microwave sol‐gel method and then the wet‐impregnation method at 25 000 mL gcat h−1 which displayed 21% conversion at 300 °C whereas 55% conversion at 350 °C temperature with 100% selectivity (Entry 9).[ 87 ] Rodriguez et al. reported Ru‐based Pr‐CeO2 catalyst using the mechanochemical method followed by the incipient wetness method, which showed 81% conversion at very low GHSV, i.e., 9000 h−1 and 500 °C temperature (Entry 10).[ 35 ] Based on these reports, we can conclude that the synthesized atomically dispersed Ni‐Pr/CeO2 catalyst in this study showed excellent and superior catalytic activity even at lower reaction temperatures (250–300 °C) at 25 000 h−1 GHSV with 100% selectivity toward methane. These results also support that uniform dispersion of Pr3+ ion over ceria support along with Ni nanoparticles drastically enhanced the catalytic activity without compromising the selectivity toward methane production. Also, the synthesis processes of the above‐mentioned catalysts involved a multistep process with precious metals like Ru, Pd and high reduction temperature. Based on this, our results indicate superior catalytic performance with optimal reaction conditions and low reaction and reduction temperature with low Pr metal loading, i.e., 8 wt.% with 25 000 h−1 GHSV with excellent catalytic performance. To the best of our knowledge, the isolated atom Pr3+ over ceria support and NiO decorated catalyst is superior to other reported Pr, Ni, and ceria‐based catalysts for CO2 methanation catalysis at low reaction temperatures.

The space‐time yield (STY) for methane was also calculated at 300 °C temperature at 100 mL min−1 flow rate and 25 000 h−1 GHSV, as shown in Figure 9A. The obtained result showed superior STY for Ni‐Pr/CeO2 atomically dispersed catalyst than impregnated NiPr/CeO2 and Ni/CeO2 catalysts, i.e., 314 mmol gcat −1 h−1. The long‐run test was performed to analyze the robustness of the best catalyst Ni‐Pr/CeO2. In this regard, the catalyst was taken and reduced at 400 °C and then kept for 40 h at 275 °C under CO2:H2 = 1:4 ratio, as shown in Figure 9. The catalyst showed no significant change in catalytic activity and selectivity toward methane. This result showed high thermal stability and reusability of the catalyst, which could pave the path for bulk‐scale application.

Figure 9.

Figure 9

A) Space‐time yield (STY) of methane at 300 °C and B) long‐term CO2 conversion of Ni‐Pr/CeO2 catalyst at 275 °C (40 h).

After 40 h of catalytic runs, the HRTEM and PXRD analysis was analyzed. No significant changes in the catalytic system were observed. In summary, it can be mentioned that the Pr‐doped Ni/CeO2 catalyst showed superior catalytic activity over Ni/CeO2 and NiPr/CeO2‐imp catalysts. The reason behind such excellent catalytic performance was estimated as H‐spillover and high oxygen vacancy with a uniform dispersion of Pr over ceria support. Also, each Pr3+ ions act as an active site for the catalytic conversion of CO2 to methane.

2.3. Structure‐Performance Relationship

Based on comprehensive characterization, catalytic performance, and insights from previous literature, the structure‐performance relationship of the optimized Ni‐Pr/CeO2 catalyst for CO2 methanation was established. The atomically dispersed Ni‐Pr/CeO2 catalyst demonstrated significantly higher catalytic activity than Ni/CeO2 and NiPr/CeO2‐imp catalysts. This enhanced performance can be attributed to key factors such as improved reducibility, increased basicity, enhanced metal dispersion, stronger metal‐support interactions, the presence of oxygen vacancies, and optimized dopant concentration.

The isolated Pr3+ ions on the ceria support while simultaneously strengthening the interaction between NiO and CeO2 in the Ni‐Pr/CeO2 system. This observation aligns with H2‐TPR results, where Pr doping lowered the reduction temperature (Figure 2A), indicating improved reducibility. Besides, CO2‐TPD analysis revealed a higher concentration of basic sites within the 300–500 °C range, along with an overall increase in basicity compared to undoped Ni/CeO2 (Figure 2B). These basic sites play a crucial role in enhancing catalytic efficiency at lower reaction temperatures by accelerating the conversion of formate and carbonate intermediates into methane, as evidenced in this study.[ 84 ]

The uniform dispersion of Pr3+ on the ceria support was confirmed through STEM‐EDS analysis, revealing a concentration of approximately ≈7 wt.% (Figure 4), which aligns well with the ICP‐OES results (Table S1, Supporting Information). This atomically dispersed Pr3+ plays a crucial role in enhancing catalytic performance.

To further investigate the role of Ni species, the Pr/CeO2 catalyst was tested for methane formation. Its poor catalytic performance confirmed that the presence of Ni, along with Pr and Ce, is essential for achieving superior catalytic activity. A review of the literature indicates that Ni nanoparticles in the range of 10–25 nm, when supported on CeO2, exhibit highly effective CO2 methanation activity.[ 39 , 52 , 88 ] This finding aligns with the crystallite size obtained from PXRD analysis in this study (Table S2, Supporting Information).

Furthermore, the number of interfacial sites and the amount of metallic Ni were quantified through XPS and XAS analyses, revealing higher values in Ni‐Pr/CeO2 compared to Ni/CeO2 (Table 4). This confirms that Pr3+ doping enhances the interfacial sites while maintaining metallic Ni. The balance between interfacial sites Ni‐O‐Ce and metallic Ni needs to be maintained because Ni‐O‐Ce plays a key role in CO2 activation while Ni(0) activates the hydrogen for reaction.[ 89 , 90 , 91 ]

Additionally, H2 dissociation and spillover at metal‐support interfacial sites were confirmed by H2‐TPD, H2‐TPR, and XPS analyses, which demonstrated their role in promoting CO2 conversion and methane selectivity.[ 47 , 84 ] The lattice defects and oxygen mobility within the CeO2 structure significantly influence CO2 adsorption, further enhancing catalytic performance.[ 92 , 93 , 94 ] In the case of Ni‐Pr/CeO2, XPS analysis revealed that the Ce3+/Ce4+ ratio was more than twice as high as in Ni/CeO2 (Table 4). This defect formation in the ceria lattice is attributed to the size difference between Pr3+ (1.27 Å) and Ce4+ (0.97 Å), which leads to structural distortions in the ceria fluorite lattice as Pr3+ replaces Ce4+. PXRD analysis further supports this structural modification, as evidenced by shifts in the (111) plane peak of ceria (Figure 1B). These findings are consistent with WT results at the Ce L3‐edge, which indicate changes in Ce–O bonding upon Pr3+ doping in CeO2 (Figure 6). Ni K‐edge WT revealed that a high dispersion of Ni species rather than the formation of bulk Ni clusters as well as the Ni species is primarily coordinated with oxygen within the catalyst.

Ahn et al. previously reported that Pr3+ doping induces structural distortions in ceria and generates oxygen vacancies by replacing Ce4+ within the crystal lattice.[ 53 ] In this study, Pr3+ incorporation was found to create local lattice distortions near oxygen vacancies due to the size mismatch between Pr3+ and Ce4+, as well as differences in their bond lengths with oxygen. As a result, oxygen mobility within the lattice was enhanced. This observation is well supported by XPS and EXAFS analyses, which confirmed an increase in oxygen vacancies in Ni‐Pr/CeO2 catalysts.

In summary, atomically dispersed Pr3+ in the Ni/CeO2 catalyst improves oxygen vacancy concentration, promotes Ni dispersion, and enhances Ni–O–Ce interfacial sites. Based on previous reports, it can be concluded that Pr3+ doping accelerates the transformation of formate and carbonate intermediates, while Ni species facilitate hydrogen spillover and CO2 activation.[ 10 , 38 , 89 ] This study demonstrates that the substitution of CeO2 with a small amount of Pr is an effective strategy for developing highly active Ni‐based CO2 methanation catalysts.

3. Conclusion

Pr3+ doped CeO2 and decorated with NiO nanoparticles were prepared via the co‐precipitation method and utilized for excellent catalytic conversion of CO2 to methane. XAS, STEM‐EDS analysis confirmed the presence of atomically dispersed and isolated Pr3+ ions as isolated atoms over ceria support. The advantage of isolated ions was studied by comparing the activity with undoped Ni/CeO2 and impregnated Ni‐Pr/CeO2 catalysts where uniformly dispersed Ni‐Pr/CeO2 showed superior catalytic activity with 87% conversion and 100% selectivity at low reaction temperature. The results suggest that Pr3+ doping promotes interfacial sites, oxygen vacancies, and hydrogen spillover to enhance the reaction of methanation.

Conflict of Interest

The authors declare no conflict of interest.

Supporting information

Supporting Information

Acknowledgements

This work has benefited from French State aid managed by the Agence Nationale de la Recherche under the France 2030 plan, bearing the reference code ANR‐22‐PESP‐0010: Projet ciblé “POWERCO2” within the PEPR project SPLEEN. The authors thank “BL‐9, Indus‐2” for XAS studies at RRCAT, India, and MRC, MNIT‐Jaipur, India, for XPS analysis.

Choudhary N., Srivastava N., Annadata H. V., Ghosh B., Da Costa P., The Dual‐Active‐Site Catalysts Containing Atomically Dispersed Pr3+ with Ni/CeO2 for CO2 Hydrogenation to Methane. Small 2025, 21, 2504707. 10.1002/smll.202504707

Data Availability Statement

The data that support the findings of this study are available on request from the corresponding author. The data are not publicly available due to privacy or ethical restrictions.

References

  • 1. Choudhary N., Jiang S., Pham H., Kedarnath G., Datye A., Miller J. T., Tyagi A. K., Shaikh M. M., Appl. Catal. B Environ. 2024, 344, 123627. [Google Scholar]
  • 2. Fan M., Jimenez J. D., Shirodkar S. N., Wu J., Chen S., Song L., Royko M. M., Zhang J., Guo H., Cui J., Zuo K., Wang W., Zhang C., Yuan F., Vajtai R., Qian J., Yang J., Yakobson B. I., Tour J. M., Lauterbach J., Sun D., Ajayan P. M., ACS Catal. 2019, 9, 10077. [Google Scholar]
  • 3. Choudhary N., Nabeela K., Mate N., Mobin S. M., RSC Sustain. 2024, 2, 1179. [Google Scholar]
  • 4. Shi X., Huang Y., Bo Y., Duan D., Wang Z., Cao J., Zhu G., Ho W., Wang L., Huang T., Xiong Y., Angew. Chem. 2022, 134, 202203063. [DOI] [PubMed] [Google Scholar]
  • 5. Liu M., Zou R., Liu C., Appl. Catal. B Environ. Energy 2025, 360, 124549. [Google Scholar]
  • 6. Zhang M., Mao Y., Bao X., Wang P., Liu Y., Zheng Z., Cheng H., Dai Y., Wang Z., Huang B., ACS Catal. 2024, 14, 5275. [Google Scholar]
  • 7. Zhang T., Zheng P., Gu F., Xu W., Chen W., Zhu T., Han Y.‐F., Xu G., Zhong Z., Su F., Appl. Catal. B Environ. 2023, 323, 122190. [Google Scholar]
  • 8. Chen S., Zhang Z., Jiang W., Zhang S., Zhu J., Wang L., Ou H., Zaman S., Tan L., Zhu P., Zhang E., Jiang P., Su Y., Wang D., Li Y., J. Am. Chem. Soc. 2022, 144, 12807. [DOI] [PubMed] [Google Scholar]
  • 9. Wang J., Kim E., Kumar D. P., Rangappa A. P., Kim Y., Zhang Y., Kim T. K., Angew. Chem. 2022, 134, 202113044. [DOI] [PubMed] [Google Scholar]
  • 10. Zhang Z., Yu Z., Feng K., Yan B., Appl. Catal. B Environ. 2022, 317, 121800. [Google Scholar]
  • 11. Yarbaş T., Ayas N., Int. J. Hydrog. Energy 2024, 49, 1134. [Google Scholar]
  • 12. Jiang H., Wang L., Kaneko H., Gu R., Su G., Li L., Zhang J., Song H., Zhu F., Yamaguchi A., Xu J., Liu F., Miyauchi M., Ding W., Zhong M., Nat. Catal. 2023, 6, 519. [Google Scholar]
  • 13. Kumar Prabhakar J., Apte P. A., Deo G., Chem. Eng. J. 2023, 471, 144252. [Google Scholar]
  • 14. Kang H., Ma J., Perathoner S., Chu W., Centi G., Liu Y., Chem. Soc. Rev. 2023, 52, 3627. [DOI] [PubMed] [Google Scholar]
  • 15. Medina O. E., Amell A. A., López D., Santamaría A., Renew. Sustain. Energy Rev. 2025, 207, 114926. [Google Scholar]
  • 16. Vieira L. H., Rasteiro L. F., Santana C. S., Catuzo G. L., da Silva A. H. M., Assaf J. M., Assaf E. M., ChemCatChem 2023, 15, 202300493. [Google Scholar]
  • 17. Younas M., Kong L. L., Bashir M. J. K., Nadeem H., Shehzad A., Sethupathi S., Energy Fuels 2016, 30, 8815. [Google Scholar]
  • 18. Li J., Li K., Li Z., Wang C., Liang Y., Pang Y., Ma J., Wang F., Ning P., He H., Nat. Commun. 2024, 15, 3874. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 19. Gao P., Tang S., Han X., Hao Z., Chen J., Pan Y., Zhang Z., Zhang H., Zi X., Chen L., Li M., Ma X., Chem. Eng. J. 2024, 498, 155784. [Google Scholar]
  • 20. Qiu R., Wang W., Wang Z., Wang H., Catal. Sci. Technol. 2023, 13, 2566. [Google Scholar]
  • 21. Bhat S., Sepúlveda‐Pagán M., Borrero‐Negrón J., Meléndez‐Gil J. E., Nikolla E., Pagán‐Torres Y. J., Catal. Sci. Technol. 2024, 14, 3364. [Google Scholar]
  • 22. Jiang W., Loh H., Low B. Q. L., Zhu H., Low J., Heng J. Z. X., Tang K. Y., Li Z., Loh X. J., Ye E., Xiong Y., Appl. Catal. B Environ. 2023, 321, 122079. [Google Scholar]
  • 23. Dostagir N. H. M., Rattanawan R., Gao M., Ota J., Hasegawa J., Asakura K., Fukouka A., Shrotri A., ACS Catal. 2021, 11, 9450. [Google Scholar]
  • 24. Vrijburg W. L., van Helden J. W. A., Parastaev A., Groeneveld E., Pidko E. A., Hensen E. J. M., Catal. Sci. Technol. 2019, 9, 5001. [Google Scholar]
  • 25. Rui N., Zhang X., Zhang F., Liu Z., Cao X., Xie Z., Zou R., Senanayake S. D., Yang Y., Rodriguez J. A., Liu C.‐J., Appl. Catal. B Environ. 2021, 282, 119581. [Google Scholar]
  • 26. Tang R., Ullah N., Hui Y., Li X., Li Z., Mol. Catal. 2021, 508, 111602. [Google Scholar]
  • 27. Yang W., Chang K., Yang M., Yan X., Yang S., Liu Y., Wang G., Xia F., Wang H., Zhang Q., Chem. Eng. J. 2024, 499, 156493. [Google Scholar]
  • 28. Xiao Z., Li Y., Hou F., Wu C., Pan L., Zou J., Wang L., Zhang X., Liu G., Li G., Appl. Catal. B Environ. 2019, 258, 117940. [Google Scholar]
  • 29. Xu X., Liu L., Tong Y., Fang X., Xu J., Jiang D., Wang X., ACS Catal. 2021, 11, 5762. [Google Scholar]
  • 30. Sun C., Beaunier P., La Parola V., Liotta L. F., Costa P. D., ACS Appl. Nano Mater. 2020, 3, 12355. [Google Scholar]
  • 31. Liu F., Park Y. S., Diercks D., Kazempoor P., Duan C., ACS Appl. Mater. Interfaces 2022, 14, 13295. [DOI] [PubMed] [Google Scholar]
  • 32. Zhang T., Wang W., Gu F., Xu W., Zhang J., Li Z., Zhu T., Xu G., Zhong Z., Su F., Appl. Catal. B Environ. 2022, 312, 121385. [Google Scholar]
  • 33. Siakavelas G. I., Charisiou N. D., AlKhoori S., AlKhoori A. A., Sebastian V., Hinder S. J., Baker M. A., Yentekakis I. V., Polychronopoulou K., Goula M. A., Appl. Catal. B Environ. 2021, 282, 119562. [Google Scholar]
  • 34. Parsai P., Choudhary N., Sahu R., Mobin S. M., Chem. – Asian J. 2024, 10.1002/asia.202401395. [DOI] [PubMed] [Google Scholar]
  • 35. Rodríguez S. L., Davó‐Quiñonero A., Juan‐Juan J., Bailón‐García E., Lozano‐Castelló D., Bueno‐López A., J. Phys. Chem. C 2021, 125, 12038. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 36. Ballauri S., Sartoretti E., Hu M., D'Agostino C., Ge Z., Wu L., Novara C., Giorgis F., Piumetti M., Fino D., Russo N., Bensaid S., Appl. Catal. B Environ. 2023, 320, 121898. [Google Scholar]
  • 37. Chen K., Li W., Li X., Ogunbiyi A. T., Yuan L., ACS Appl. Nano Mater 2021, 4, 5404. [Google Scholar]
  • 38. Tsiotsias A. I., Charisiou N. D., AlKhoori A., Gaber S., Stolojan V., Sebastian V., van der Linden B., Bansode A., Hinder S. J., Baker M. A., Polychronopoulou K., Goula M. A., J. Energy Chem. 2022, 71, 547. [Google Scholar]
  • 39. Tsiotsias A. I., Charisiou N. D., Harkou E., Hafeez S., Manos G., Constantinou A., Hussien A. G. S., Dabbawala A. A., Sebastian V., Hinder S. J., Baker M. A., Polychronopoulou K., Goula M. A., Appl. Catal. B Environ. 2022, 318, 121836. [Google Scholar]
  • 40. Guillén‐Hurtado N., Giménez‐Mañogil J., Martínez‐Munuera J. C., Bueno‐López A., García‐García A., Appl. Catal. Gen. 2020, 590, 117339. [Google Scholar]
  • 41. Choudhary N., Kumar V., Mobin S. M., ChemistrySelect 2022, 7, 202202501. [Google Scholar]
  • 42. Martin L. P., Nagle D., Rosen M., Mater. Sci. Eng. A 1998, 246, 151. [Google Scholar]
  • 43. Lyu C., Zhou X., Lu X., Zhang Y., Li C., Zhou Q., Sun Z., Chen G., Geofluids 2021, 2021, 8898142. [Google Scholar]
  • 44. Gao G., Remón J., Jiang Z., Yao L., Hu C., Appl. Catal. B Environ. 2022, 309, 121260. [Google Scholar]
  • 45. Baldovino‐Medrano V. G., Niño‐Celis V., Isaacs Giraldo R., J. Chem. Eng. Data 2023, 68, 2512. [Google Scholar]
  • 46. Mierczynski P., Mierczynska A., Ciesielski R., Mosinska M., Nowosielska M., Czylkowska A., Maniukiewicz W., Szynkowska M. I., Vasilev K., Catalysts 2018, 8, 380. [Google Scholar]
  • 47. Guo Y., Mei S., Yuan K., Wang D.‐J., Liu H.‐C., Yan C.‐H., Zhang Y.‐W., ACS Catal. 2018, 8, 6203. [Google Scholar]
  • 48. Italiano C., Llorca J., Pino L., Ferraro M., Antonucci V., Vita A., Appl. Catal. B Environ. 2020, 264, 118494. [Google Scholar]
  • 49. Ni Z., Djitcheu X., Gao X., Wang J., Liu H., Zhang Q., Sci. Rep. 2022, 12, 5344. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 50. Xu L., Song H., Chou L., Int. J. Hydrog. Energy 2012, 37, 18001. [Google Scholar]
  • 51. Zhou G., Liu H., Cui K., Jia A., Hu G., Jiao Z., Liu Y., Zhang X., Appl. Surf. Sci. 2016, 383, 248. [Google Scholar]
  • 52. Du Y., Qin C., Xu Y., Xu D., Bai J., Ma G., Ding M., Chem. Eng. J. 2021, 418, 129402. [Google Scholar]
  • 53. Ahn K., Yoo D. S., Prasad D. H., Lee H.‐W., Chung Y.‐C., Lee J.‐H., Chem. Mater. 2012, 24, 4261. [Google Scholar]
  • 54. Ye R.‐P., Li Q., Gong W., Wang T., Razink J. J., Lin L., Qin Y.‐Y., Zhou Z., Adidharma H., Tang J., Russell A. G., Fan M., Yao Y.‐G., Appl. Catal. B Environ. 2020, 268, 118474. [Google Scholar]
  • 55. Li M., Amari H., van Veen A. C., Appl. Catal. B Environ. 2018, 239, 27. [Google Scholar]
  • 56. Li X., Li D., Tian H., Zeng L., Zhao Z.‐J., Gong J., Appl. Catal. B Environ. 2017, 202, 683. [Google Scholar]
  • 57. Muroyama H., Tsuda Y., Asakoshi T., Masitah H., Okanishi T., Matsui T., Eguchi K., J. Catal. 2016, 343, 178. [Google Scholar]
  • 58. Zhu M., Tian P., Cao X., Chen J., Pu T., Shi B., Xu J., Moon J., Wu Z., Han Y.‐F., Appl. Catal. B Environ. 2021, 282, 119561. [Google Scholar]
  • 59. Mi R., Li D., Hu Z., Yang R. T., ACS Catal. 2021, 11, 7876. [Google Scholar]
  • 60. Novak T. G., Herzog A. E., Buck M. R., Spears R. J., Sendgikoski K., DeBlock R. H., Brintlinger T. H., DeSario P. A., Rolison D. R., Sci. Adv. 2024, 10, adr9120. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 61. Lee S.‐Y., Oh H.‐J., Kim M., Cho H.‐S., Lee Y.‐K., Appl. Catal. B Environ. 2023, 324, 122269. [Google Scholar]
  • 62. Liu W., Li X., Hao Y., Xiong D., Shan H., Wang J., Xiao W., Yang H., Yang H., Kou L., Tian Z., Shao L., Zhang C., Adv. Funct. Mater. 2021, 31, 2008301. [Google Scholar]
  • 63. Fang G., Wang Q., Zhou J., Lei Y., Chen Z., Wang Z., Pan A., Liang S., ACS Nano 2019, 13, 5635. [DOI] [PubMed] [Google Scholar]
  • 64. Filez M., Redekop E. A., Poelman H., Galvita V. V., Marin G. B., Anal. Chem. 2015, 87, 3520. [DOI] [PubMed] [Google Scholar]
  • 65. Li J., Li Y., Routh P. K., Makagon E., Lubomirsky I., Frenkel A. I., J. Synchrotron Radiat. 2021, 28, 1511. [DOI] [PubMed] [Google Scholar]
  • 66. Prinz N., Schwensow L., Wendholt S., Jentys A., Bauer M., Kleist W., Zobel M., Nanoscale 2020, 12, 15800. [DOI] [PubMed] [Google Scholar]
  • 67. Ao X., Kong Y., Zhao S., Chen Z., Li Y., Liao X., Tian B., Angew. Chem., Int. Ed. 2025, 64, 202415036. [DOI] [PubMed] [Google Scholar]
  • 68. Asakura H., Shishido T., Fuchi S., Teramura K., Tanaka T., J. Phys. Chem. C 2014, 118, 20881. [Google Scholar]
  • 69. Kumar P. A., Jeong Y. E., Gautam S., Ha H. P., Lee K. J., Chae K. H., Chem. Eng. J. 2015, 275, 142. [Google Scholar]
  • 70. Li W., Yamada S., Hashimoto T., Okumura T., Hayakawa R., Nitta K., Sekizawa O., Suga H., Uruga T., Ichinohe Y., Sato T., Toyama Y., Noda H., Isobe T., Takatori S., Hiraki T., Tatsuno H., Kominato N., Ito M., Sakai Y., Omamiuda H., Yamaguchi A., Yomogida T., Miura H., Nagasawa M., Okada S., Takahashi Y., Anal. Chim. Acta. 2023, 1240, 340755. [DOI] [PubMed] [Google Scholar]
  • 71. Kvashnina K. O., Chem. – Eur. J. 2024, 30, 202400755. [Google Scholar]
  • 72. Plakhova T. V., Romanchuk A. Y., Konyukhova A. D., Seregina I. F., Baranchikov A. E., Svetogorov R. D., Terban M. W., Ivanov V. K., Kalmykov S. N., Environ. Sci. Nano 2024, 11, 3551. [Google Scholar]
  • 73. Estevenon P., Amidani L., Bauters S., Tamain C., Bodensteiner M., Meurer F., Hennig C., Vaughan G., Dumas T., Kvashnina K. O., Chem. Mater. 2023, 35, 1723. [Google Scholar]
  • 74. Sokol H. J., Ebrahim A. M., Caratzoulas S., Frenkel A. I., Valla J. A., J. Phys. Chem. C 2022, 126, 1496. [Google Scholar]
  • 75. Butorin S. M., Kvashnina K. O., Vegelius J. R., Meyer D., Shuh D. K., Proc. Natl. Acad. Sci. USA 2016, 113, 8093. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 76. Moreau L. M., Lapsheva E., Amaro‐Estrada J. I., Gau M. R., Carroll P. J., Manor B. C., Qiao Y., Yang Q., Lukens W. W., Sokaras D., Schelter E. J., Maron L., Booth C. H., Chem. Sci. 2022, 13, 1759. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 77. Yang S., Zhang W., Pan G., Chen J., Deng J., Chen K., Xie X., Han D., Dai M., Niu L., Angew. Chem., Int. Ed. 2023, 62, 202312076. [DOI] [PubMed] [Google Scholar]
  • 78. Yamazaki S., Matsui T., Ohashi T., Arita Y., Solid State Ion 2000, 136, 913. [Google Scholar]
  • 79. Guo J., Song R., Li Z., Pan D., Xie H., Ba Y., Xie M., Fan S., Yang X., Zhang H., Yu H., Zhang S., Du J., He L., Wang L., Adv. Energy Sustain. Res. 2022, 3, 2200106. [Google Scholar]
  • 80. Safonova O. V., Guda A., Rusalev Y., Kopelent R., Smolentsev G., Teoh W. Y., van Bokhoven J. A., Nachtegaal M., ACS Catal. 2020, 10, 4692. [Google Scholar]
  • 81. Chen S., Costley‐Wood L., Lezcano‐Gonzalez I., Campbell E., Weng Z., Asunción Molina M., Wu Y., Beale A. M., Appl. Catal. B Environ. Energy 2025, 366, 125029. [Google Scholar]
  • 82. Hissariya R., Sharma R., Mishra S. K., J. Phys. Chem. Solids 2023, 181, 111549. [Google Scholar]
  • 83. Li W., Lv J., Liu D., Cai W., Chen X., Huang Q., Wang L., Wang B., Chem. Mater. 2023, 35, 3892. [Google Scholar]
  • 84. Hongmanorom P., Ashok J., Chirawatkul P., Kawi S., Appl. Catal. B Environ. 2021, 297, 120454. [Google Scholar]
  • 85. Khatun R., Siddiqui N., Singh Pal R., Bhandari S., Suvra Khan T., Singh S., Kumar Poddar M., Samanta C., Bal R., Catal. Sci. Technol. 2023, 13, 6431. [Google Scholar]
  • 86. Khatun R., Singh Pal R., Bhati K., Chandra Kothari A., Singh S., Siddiqui N., Rana S., Bal R., RSC Sustain. 2025, 3, 844. [Google Scholar]
  • 87. Siakavelas G. I., Charisiou N. D., AlKhoori A., AlKhoori S., Sebastian V., Hinder S. J., Baker M. A., Yentekakis I. V., Polychronopoulou K., Goula M. A., J. CO2 Util. 2021, 51, 101618. [Google Scholar]
  • 88. Liu K., Xu X., Xu J., Fang X., Liu L., Wang X., J. CO2 Util. 2020, 38, 113. [Google Scholar]
  • 89. Cárdenas‐Arenas A., Quindimil A., Davó‐Quiñonero A., Bailón‐García E., Lozano‐Castelló D., De‐La‐Torre U., Pereda‐Ayo B., González‐Marcos J. A., González‐Velasco J. R., Bueno‐López A., Appl. Catal. B Environ. 2020, 265, 118538. [Google Scholar]
  • 90. Cárdenas‐Arenas A., Quindimil A., Davó‐Quiñonero A., Bailón‐García E., Lozano‐Castelló D., De‐La‐Torre U., Pereda‐Ayo B., González‐Marcos J. A., González‐Velasco J. R., Bueno‐López A., Appl. Mater. Today 2020, 19, 100591. [Google Scholar]
  • 91. Xu Y., Chen R., Lin H., Lv Q., Liu B., Wu L., Tan L., Dai Y., Zong X., Tang Y., J. Catal. 2024, 435, 115545. [Google Scholar]
  • 92. Sun Y., Wu T., Bao Z., Moon J., Huang Z., Chen Z., Chen H., Li M., Yang Z., Chi M., Toops T. J., Wu Z., Jiang D., Liu J., Dai S., ACS Cent. Sci. 2022, 8, 1081. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 93. Wang L., Yang Q., Huo M., Lu D., Gao Y., Chen Y., Xu H., Adv. Mater. 2021, 33, 2100150. [DOI] [PubMed] [Google Scholar]
  • 94. Kenyotha K., Kidkhunthod P., Poo‐arporn Y., Chanapattharapol K. C., J. Phys. Chem. Solids 2024, 190, 112009. [Google Scholar]

Associated Data

This section collects any data citations, data availability statements, or supplementary materials included in this article.

Supplementary Materials

Supporting Information

Data Availability Statement

The data that support the findings of this study are available on request from the corresponding author. The data are not publicly available due to privacy or ethical restrictions.


Articles from Small (Weinheim an Der Bergstrasse, Germany) are provided here courtesy of Wiley

RESOURCES