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. 2021 May 27;125(22):12038–12049. doi: 10.1021/acs.jpcc.1c03539

Effect of Pr in CO2 Methanation Ru/CeO2 Catalysts

Sergio López Rodríguez , Arantxa Davó-Quiñonero †,, Jerónimo Juan-Juan §, Esther Bailón-García , Dolores Lozano-Castelló , Agustín Bueno-López †,*
PMCID: PMC8494384  PMID: 34630817

Abstract

graphic file with name jp1c03539_0011.jpg

CO2 methanation has been studied with Pr-doped Ru/CeO2 catalysts, and a dual effect of Pr has been observed. For low Pr content (i.e., 3 wt %) a positive effect in oxygen mobility prevails, while for high Pr doping (i.e., 25 wt %) a negative effect in the Ru–CeO2 interaction is more relevant. Isotopic experiments evidenced that Pr hinders the dissociation of CO2, which takes place at the Ru–CeO2 interface. However, once the temperature is high enough (200 °C), Pr improves the oxygen mobility in the CeO2 support, and this enhances CO2 dissociation because the oxygen atoms left are delivered faster to the support sink and the dissociation sites at the interface are cleaned up faster. In situ Raman spectroscopy experiments confirmed that Pr improves the creation of oxygen vacancies on the ceria lattice but hinders their reoxidation by CO2, and both opposite effects reach an optimum balance for 3 wt % Pr doping. In addition, in situ diffuse reflectance infrared Fourier transform spectroscopy (DRIFTS) experiments showed that Pr doping, regardless of the amount, decreases the population of surface carbon species created on the catalysts surface upon CO2 chemisorption under methanation reaction conditions, affecting both productive reaction intermediates (formates and carbonyls) and unproductive carbonates.

1. Introduction

Cerium oxide materials have relevant utility in heterogeneous catalysts and have been the center of a significant battery of studies devoted to gaining insight into their high performance. The unique properties of ceria rely on its oxygen storage/release capacity (OSC) and strong synergistic metal–support interactions when a metal phase is dispersed on a ceria matrix.13 Not only promoting their catalytic activity but also understanding the effect on these active sites will lay the foundations of a rational design of heterogeneous catalysts.

CeO2 doping with other cations usually improves the catalytic features due to the creation of oxygen vacancies,414 but the beneficial effect is often obtained only when the content is optimized. It is well-known that doping ceria with Zr4+, Ti4+, Eu3+, La3+, or Tb3+ cations, among others, improves the catalytic activity in different reactions, such as volatile organic compound (VOC) oxidation, CO oxidation, soot combustion, and NOx reduction.57,14,15 Ceria–praseodymia catalysts have demonstrated superior redox properties and improved catalytic performance compared to other ceria-based mixed oxides in soot combustion and CO oxidation reactions, and these Ce–Pr formulations are currently under investigation in other catalytic applications.1620

CO2 conversion to methane by H2 is a practical strategy for clean energy utilization with the dual benefit of reducing CO2 emissions while meeting the increasing energy demand forecasted for the next few decades.21,22 Metals supported on ceria can activate CO2 molecules at lower temperatures compared to analogue catalysts with other supports. Ceria improves the efficiency of the reaction because oxygen vacancies serve as active sites for CO2 dissociation.2327 Up to now, the research on this reaction has shed light on the catalytic role of each active center by means of in situ spectroscopies and other advanced techniques.2834 It is known that CO2 methanation requires a bifunctional catalyst able to undertake both H2 and CO2 activation processes on one or two different type of sites. In heterogeneous catalysts based on inert supports (such as Al2O3 or SiO2), both events take place on reduced metal sites.3540 However, ceria-based CO2 methanation catalysts are proven to be more efficient because ceria contributes to CO2 chemisorption and dissociation in cooperation with the metal. That is, H2 dissociation takes place preferentially on reduced metal sites while the most efficient sites for CO2 dissociation are located at the metal–ceria interface.28,41

This study focuses on the investigation of the role of Pr in Ru/CeO2 catalyst for CO2 methanation by analyzing the effect of Pr loading. Pr is able to adopt +3 and +4 oxidation states, like Ce cations, and Pr cations can be introduced into the fluorite CeO2 lattice, forming a solid solution until ∼30% Pr (with regard to Ce + Pr), with segregated Pr6O11 being expected above this threshold.42

In this study, in situ Raman and in situ diffuse reflectance infrared Fourier transform spectroscopy (DRIFTS) experiments have been performed for the assessment of the role of oxygen vacancies and the identification of reaction intermediates under reaction conditions. Steady-state isotopic exchange (SSIE) experiments have been performed to study the oxygen exchange between CO2 and the catalysts by evaluating the activation of the CO2 molecules on the Pr-doped Ru/CeO2 catalysts.

2. Experimental Details

2.1. Catalyst Preparation

Ruthenium catalysts with Pr-doped CeO2 supports, referred to as Ru/Ce%PrOx onward, were prepared and used in this study. The “%” corresponds to the weight percent of Pr with regard to Ce + Pr, which ranges from 0 to 25%. A Ru/PrOx catalyst was also prepared.

The necessary amounts of Ce(NO3)3·6H2O (99%, Sigma-Aldrich) and Pr(NO3)3·6H2O (99.9%, Sigma-Aldrich) were physically mixed in a mortar and calcined at 600 °C during 6 h. Nitrates decompose to oxides during calcination and Ce3+ and Pr3+ cations were oxidized to a 4+ oxidation state, forming a CexPr1–xO2 solid solution. Ruthenium was loaded afterward by incipient wetness impregnation of the corresponding amount of ruthenium(III) acetylacetonate (97%, Sigma-Aldrich) to achieve 3 wt % Ru on the final catalysts. Finally, the impregnated samples were thermally treated at 350 °C during 3 h in N2 atmosphere, using a heating ramp of 5 °C/min.

2.2. Catalysts Characterization

The ruthenium content was determined by inductively coupled plasma–optical emission spectrometry (ICP-OES) in a PerkinElmer device (Optima model 4300 DV) after digestion of the catalysts in a HCl/HNO3 (3:1 volume) mixture assisted by microwaves.

The crystalline structure of each catalyst was analyzed by X-ray diffraction in a Rigaku Miniflex II diffractometer. The diffractograms were recorded in a range of 2θ from 10° to 90°, with a step of 0.025°. The wavelength used was λ = 0.155418 nm, corresponding to the Cu Kα radiation. The average crystal size of ceria was determined using the Scherrer equation. N2 physisorption isotherms were measured at −196 °C in an Autosorb-6 device (Quantachrome) after outgassing the catalysts during 4 h at 250 °C under vacuum conditions.

The reducibility of the catalysts was examined by H2 temperature-programmed reduction (H2-TPR) in a Micromeritics Pulse Chemisorb 2705 device. For such measurements, 25 mg of catalyst was loaded in a tubular quartz reactor coupled with a thermal conductivity detector (TCD) while flowing a mixture consisting of 40 mL/min of 5% H2/Ar. The temperature was increased at a 10 °C/min pace from room temperature up to 950 °C.

2.3. Catalytic Tests

Catalytic tests were performed in a fixed-bed tubular reactor (10 mm inner diameter) containing 100 mg of catalyst mixed with SiC particles (1.00–1.25 mm) to reach a bed volume of 1 cm3. The catalyst was pretreated in situ at 500 °C for 1 h under 100 mL/min of a 50% vol H2/He mixture. After cooling down to room temperature, the reaction mixture was fed to the reactor. The feed consisted of 100 mL/min of 10% CO2, 40% H2, and He balance at 1 atm. The GHSV was 9 000 h–1. The outlet gases were monitored under steady-state conditions at each temperature with a gas chromatograph (Agilent 8860 GC System) equipped with two packed columns (Porapak Q 80/100 for CO2 and Molecular Sieve 13× for O2 and CO separation) coupled to a TCD.

2.4. Isotopic Experiments

Steady-state isotopic experiments were performed with 13C18O2 (Aldrich; 99% 13C, 95% 18O) pulses in a fixed-bed cylindrical reactor with 4 mm inner diameter coupled to a Pfeiffer Vacuum mass spectrometer (model OmniStar) operating at 1 ms frequency. The catalytic bed (50 mg) was pretreated under 20 mL/min of 50% H2/He mixture at 500 °C for 1 h and then cooled down to room temperature under He atmosphere. The reaction mixture (10% CO2, 40% H2, and He balance) was then continuously fed to the reactor (20 mL/min), and different gas pulses were fed to this main stream. A six-way valve with a loop of 100 μL was used and was filled with 9 psi of the gas to be pulsed. This volume of gas was dragged by the main gas stream once the position of the valve was changed. One Ar pulse followed by a pulse of isotopic 13C18O2 was fed at 25, 100, 200, 250, and 300 °C.

2.5. In Situ Raman Spectroscopy Experiments

In situ Raman spectra were recorded in a LabRam Jobin Ivon Horiba instrument with a laser excitation source of He/Ne (632.8 nm). Experiments were performed in a high-temperature chamber fed with a gas flow of 60 mL/min. The catalysts were reduced with 50% H2/N2 for 1 h at 450 °C, and then the catalysts were cooled down to room temperature under N2 flow. The methanation gas mixture (10% CO2, 40% H2, and N2 balance) was fed to the cell, and spectra were recorded in steady state at 25, 100, 200, 300, and 400 °C. A monocrystalline Si reference (521 cm–1) was used to calibrate the position of the bands.

2.6. In Situ DRIFTS Experiments

In situ DRIFTS experiments were performed in a Jasco infrared spectrometer, model FT/IR-4000, using a reaction cell with temperature and gas flow control. The gas composition was monitored during the experiments with a Pfeiffer Vacuum mass spectrometer (model OmniStar). The catalytic bed consisted of 90 mg of catalyst, which was pretreated in 50% H2/He at 450 °C for 1 h and then cooled down to room temperature under He atmosphere. A background spectrum was recorded in these conditions, and then 100 mL/min of the methanation mixture (10% CO2, 40% H2, and He balance) was fed. Spectra were recorded from 4000 to 1000 cm–1 in steps of 1 cm–1 at 25, 100, 200, 300, and 350 °C once steady-state conditions were achieved at each temperature.

3. Results and Discussion

3.1. Catalytic Tests

Figure 1a shows the CO2 conversion to methane as a function of the temperature obtained in the catalytic experiments, and Figure 1b presents the conversion CO2 at a selected temperature (270 °C) as a function of the Pr loading of the catalysts. All catalysts displayed 100% selectivity to methane, which is a feature that can be attributed to ruthenium catalysts,4347 and the catalytic activity observed follows this trend:

3.1.

This trend indicates that Pr doping in low concentration is beneficial, with Ru/Ce3PrOx being moderately more active than Ru/CeO2 from 250 °C onward, while high Pr concentration has a negative effect. Taking these results into account, three catalysts (Ru/Ce3PrOx, Ru/Ce25PrOx, and Ru/CeO2) were selected to conduct an extended investigation of the effect of Pr in the catalytic behavior of Ru/CeO2 catalysts.

Figure 1.

Figure 1

CO2 methanation experiments performed in a fixed-bed reactor under steady-state conditions using Ru catalysts with different LnOx supports (Ln = Ce and/or Pr). Reduction pretreatment at 500 °C for 1 h in 50% H2/He. Reaction mixture: 10% CO2, 40% H2, and He balance. (a) CO2 conversion for different temperatures and (b) CO2 conversion at 270 °C for different Pr loadings.

3.2. ICP, X-ray Diffraction, and N2 Adsorption Characterization

The Ru loading was determined by ICP, and the values obtained are included in Table 1. The Ru content was below the nominal target value (3%) for all catalysts, probably because part of the metal was released during the thermal treatment due to the high volatility of some RuOx species.48 The thermal treatment performed to decompose the Ru precursor salt was carried out under inert atmosphere in order to minimize this effect, but the formation of RuOx volatile species with the oxygen available in the metal precursors cannot be ruled out. It is known that ceria interacts strongly with Ru species and diminishes the release of volatile RuOx oxides with regard to other supports, such as SiO2 or Al2O3.4049 This effect would explain the lower Ru content determined for the Ru/Ce25PrOx catalyst (2.1% of Ru) with regard to that measured for the catalyst without Pr (2.5% for Ru/CeO2) and with little Pr (2.6% for Ru/Ce3PrOx) because Pr doping partially hinders the RuOx–CeO2 interaction, as will be demonstrated later. The effect of Pr doping in the Ru content is relevant for 25% Pr doping but not for 3% Pr doping.

Table 1. Results of Catalysts Characterization by ICP-OES, X-ray Diffraction (XRD), and N2 Adsorption–Desorption.

  Ru content (wt %) lattice parameter of ceria (nm) crystallite size of ceria (nm) BET specific surface area (m2/g)
Ru/CeO2 2.5 0.540 13 90
Ru/Ce3PrOx 2.6 0.542 13 40
Ru/Ce25PrOx 2.1 0.543 16 70

The catalyst porosity was studied by N2 adsorption–desorption, and the isotherms at −196 °C are shown in Figure 2.

Figure 2.

Figure 2

N2 adsorption–desorption isotherms of the catalyst.

All isotherms show certain adsorption at low partial pressure due to the presence of narrow porosity followed by a hysteresis loop at higher partial pressures attributed to meso- and/or macropores. Pr doping changes the shape of the hysteresis loop, whose type indicates, for the Ru/CeO2 catalyst, the presence of mesopores, while the absence of a plateau in the isotherms of Ru/Ce3PrOx and Ru/Ce25PrOx evidences the formation of macropores. The Brunauer–Emmett–Teller (BET) specific surface areas, which are included in Table 1, range between 90 and 40 m2/g, and these values are consistent with those reported in the literature for similar materials. As shown in Table 1, the Pr-containing catalysts present a lower surface area compared to Ru/CeO2 due to the promoting effect of the Pr cations in CeO2 sintering. Usually, CeO2 doping with foreign cations favors sintering during calcination for moderate temperatures (∼500–700 °C) because dopants create defects on the ceria lattice that decrease the energy barrier that must be overcome for crystals to grow. On the contrary, dopants partially avoid sintering for high calcination temperatures where the energy barrier for sintering is already overcome.

The crystalline structure of the catalysts was characterized by XRD, and the diffractograms are compiled in Figure 3. As expected, all catalysts show diffractograms characteristic of the fluorite structure of ceria (JCPDS file 34-0394). Evidence of ruthenium species was not found in the diffractograms, which indicates that ruthenium species are highly dispersed on the ceria support.

Figure 3.

Figure 3

XRD patterns of the catalysts.

Identification of PrOx phases in CeO2-rich oxides is difficult by XRD because their diffraction patterns are analogous. Pr can adopt several PrOx stoichiometries with x ≤ 2, and their diffraction patterns are only slightly different from that of ceria (JCPDS file 24-1006 for PrO2 and 42-1121 for Pr6O11, for instance). In addition, Pr cations can be easily inserted into the CeO2 matrix. Evidence of segregated PrOx phases can be observed in some cases as shoulders in the CeO2 peaks, but these are not obvious in Figure 3, suggesting the formation of solid solutions with Pr cations inserted in the CeO2 framework and/or the presence of highly dispersed PrOx phases spread on the ceria surface.

The lattice parameter and crystallite size of the CeO2 phase were determined, and the calculated values are compiled in Table 1. The lattice parameter is consistent with that reported for pure ceria (ca. 0.540 nm) for all catalysts, and Pr doping does not significantly affect this value.18,37 This does not rule out the insertion of Pr cations into the ceria lattice because the sizes of Ce and Pr cations are similar and neither expansion nor contraction of the ceria lattice is expected upon Pr doping. The calculated crystallite sizes are also similar for the three catalysts (13–16 nm), evidencing that Pr doping has only a moderate effect on the size of the primary crystals.

3.3. H2 Temperature-Programmed Reduction

The reducibility of the catalysts was studied by H2-TPR, and the reduction profiles are shown in Figure 4. Three reduction peaks can be distinguished in all reduction curves, but the temperature of each event depends on the nature of the catalyst. The consumption of H2 on these peaks has been quantified, and the values are compiled in Table 2.

Figure 4.

Figure 4

H2-TPR profiles of the catalysts.

Table 2. H2 Consumed in H2-TPR Experimentsa.

catalyst lowest-temperature peak, mmol H2/mmol Ru intermediate-temperature peak, mmol H2/mmol Ln highest-temperature peak, mmol H2/mmol Ln
Ru/CeO2 1.04 0.07 0.08
Ru/Ce3PrOx 2.74 0.11 0.07
Ru/Ce25PrOx 1.46 0.30 0.02
a

Ln = Ce + Pr.

The lowest-temperature peaks at 67, 70, and 167 °C for Ru/CeO2, Ru/Ce3PrOx, and Ru/Ce25PrOx, respectively, are mainly attributed to RuOx reduction to Ru. According to the literature,43,45 ruthenium is expected to mainly form RuO2 in these types of materials, and the mol of H2 consumed in the lowest-temperature peak for the Ru/CeO2 catalyst is half of that required for the total reduction of RuO2 to Ru. On the contrary, the amount of H2 consumed in the lowest-temperature peak by the Ru/Ce3PrOx catalyst exceeds the amount required for 100% RuO2 reduction, suggesting that Ce4+ and/or Pr4+ cations are being reduced together with those of ruthenium at this low temperature. This result evidences the enhanced reducibility of the Ru/CeO2 catalyst upon 3% Pr doping. However, the opposite effect of Pr is observed for 25% doping because the lowest-temperature reduction peak of Ru/Ce25PrOx is delayed to 167 °C, and the consumption of H2 decreases significantly with regard to Ru/Ce3PrOx.

The intermediate- and highest-temperature peaks must be mainly assigned to the reduction of Ce4+ and Pr4+ cations together with the reduction of the remaining RuOx species, the former to surface reduction and the latter to bulk reduction. The presence of shoulders in these peaks evidences the overlapping of several events, which can be attributed to the slightly different reducibilities of the Ce4+ and Pr4+ cations and to the presence of different surface species on the catalysts, including hydroxyl groups, carbonates/bicarbonates, etc., that can be reduced or desorbed and methanated during the heating reduction.

Surface reduction of bare ceria usually starts around 400 °C, but the surface reduction peak is shifted to 250 °C in the Ru/CeO2 catalyst due to the catalytic effect of Ru in the reduction of ceria. Ruthenium species, once reduced to a metal state, are very efficient for H2 dissociation, accelerating the reduction of the support. Quantification of H2 consumed in this intermediate peak indicates that Pr doping enhances the reduction of the support; the higher the Pr loading, the higher is the achieved support surface reduction degree.

The improved reducibility of the support upon Pr doping is also observed in the highest-temperature peak. The temperature of this bulk reduction peak is shifted from 757 °C for Ru/CeO2 to 742 °C for Ru/Ce3PrOx as a consequence of the improved reducibility of the support in the latter catalyst, but it roughly keeps the same reduction degree (0.08–0.07 mmol H2/mmol Ln). On the contrary, the bulk reduction peak almost disappears for Ru/Ce25PrOx, while the area of the intermediate-temperature peak increases drastically. This behavior occurs because of the high oxygen mobility into the 25% Pr-doped CeO2 lattice because bulk oxygen is pumped out to the surface with a low energy barrier once the surface oxygen is depleted.

As a summary, these H2-TPR experiments allow the conclusion that Pr doping significantly improves the reducibility and oxygen mobility of the ceria support. In addition, RuOx reduction is improved for low Pr loading (3%), while it is impeded for high Pr loading (25%).

3.4. Steady-State Isotopic Exchange Experiments

To analyze the effect of Pr in the interaction of CO2 with the Ru/CeO2 catalysts, steady-state isotopic exchange (SSIE) experiments were carried out using isotopic CO2. Table 3 compiles the carbon species and mass spectroscopy signals involved in these changes to facilitate the interpretation of the experiments.

Table 3. Carbon Species and m/z Signals Involved in the Isotopic Experiments.

m/z species isotopic composition
15 CH4 12CH4
16 CH4 13CH4
44 CO2 12C16O16O
45 CO2 13C16O16O
46 CO2 12C16O18O
47 CO2 13C16O18O
48 CO2 12C18O18O
49 CO2 13C18O18O

Isotopic CO2 (13C18O18O; m/z 49) was pulsed at different temperatures to a methanation mixture with 10% CO2 (12C16O16O; m/z 44) + 40% H2 in He balance, which was continuously fed to the reactor. The oxygen and carbon species present in the catalysts before the isotopic pulses only include 16O and 12C atoms, and therefore, the release of species with 18O and 13C atoms provides information about the reaction pathway followed by the CO2 (13C18O18O) molecules pulsed. Pulse experiments performed without catalyst confirmed that no gas-phase reactions take place in the experiment conditions. Note also that CO species were not detected in the isotopic experiments, in accordance with the high selectivity of these catalysts toward CH4. H218O (m/z 20) was not detected in any isotopic experiments regardless of the catalyst and temperature, that is, all oxygen atoms in H2O emitted as a product of the methanation reaction are nonisotopic (16O).

Figure 5 shows, as a representative example, the main signals recorded upon a CO2 (13C18O18O; m/z 49) pulse at 250 °C for each catalyst. The m/z 49 signal is not detected in the conditions of Figure 5, which indicates that pulsed CO2 is stored on the catalysts or transformed to other species. The products of the methanation reaction (CH4 and H2O) are observed, as well as several CO2 species including 12C16O16O (m/z 44), 13C16O16O (m/z 45), 12C16O18O (m/z 46), and 13C16O18O (m/z 47). This evidences that CO2 molecules are involved in a dynamic equilibrium between the gas phase and the catalyst surface, which results in the activation of the CO2 molecules. This activation coupled with the oxygen exchange capacity yields different carbon species with m/z signals between 45 and 48. As such, the obtained reaction products (CH4 and H2O) are released in the form of isotopic (13CH4), nonisotopic (12CH4 and H216O), or a combination of them. Note that the isotopic methane peak is the result of the hydrogenation of carbon species coming from the CO2 (13C18O18O; m/z 49) pulse, and the release of nonisotopic methane (12CH4; m/z 15) indicates that the chemisorption of new species upon the CO2 (13C18O18O; m/z 49) pulse promotes the hydrogenation of carbon species previously present on the catalysts.

Figure 5.

Figure 5

Main signals detected upon CO2 (13C18O18O; m/z 49) pulses at 250 °C to the different catalysts under CO2 methanation conditions (10% 12C16O16O (m/z 44) + 40% H2 in He). (a) Ru/CeO2, (b) Ru/Pr3CeOx, and (c) Ru/Pr25CeOx. x-axis origin (0 s) corresponds to the time of the pulse.

Figure 5 allows for the conclusion that the qualitative behaviors of the three catalysts are similar, that is, the types of species evolved are the same for all catalysts. Nevertheless, quantitative differences can be distinguished that are attributed to Pr doping. The quantification of the areas under the different signals in the pulse experiments let us determine the mass balance of carbon in each pulse (Figure 6). It was considered for those calculations that the system is in steady state, and therefore, there is no net accumulation of carbon species on the catalyst surface after a single pulse.

Figure 6.

Figure 6

Mass balance of carbon species upon CO2 (13C18O18O; m/z 49) pulses at different temperatures under CO2 methanation gas flow. (a) Ru/CeO2, (b) Ru/Ce3PrOx, and (c) Ru/Ce25PrOx. Pretreatment of 50% H2/He at 450 °C, 1 h; methanation mixture 10% 12C16O2, 40% H2, and He balance.

As expected, reaction products (CH4 and H2O) were not detected at 30 °C for any catalyst, in accordance with the catalytic experiments shown in Figure 1, and the species released after the CO2 (13C18O18O; m/z 49) pulse at this temperature were CO2 molecules in a diverse isotopic combination. This means that the catalysts are able to chemisorb isotopic CO2 (13C18O18O; m/z 49) gas molecules, to break part of the C=O bonds even at room temperature, and to release other nonisotopic CO2 molecules with 12C and/or 16O atoms. Only the Ru/Ce25PrOx catalyst shows certain CO2 (13C18O18O; m/z 49) release at 30 °C, evidencing the poorest interaction with the gas-phase CO2 molecules.

The release of nonisotopic CO2 (12C16O16O; m/z 44) is relevant for all catalysts at 30 °C, and the percentage of 12C16O16O ranges between 22 and 34% of total carbon species, depending on the catalyst. These high percentages of evolved nonisotopic CO2 (m/z 44) indicate that the chemisorption of new carbon species upon the CO2 (13C18O18O; m/z 49) pulse leads to desorption of CO2 molecules previously chemisorbed on the catalysts. This process does not involve breaking C=O bonds necessarily.

The emission of 12C16O18O (m/z 46) is also relevant for all catalysts at 30 °C, and this species comes from the incorporation of one 18O atom of the CO2 pulsed (13C18O18O; m/z 49) to a previously chemisorbed 12C-containing surface species. On the contrary, the emission of 12C18O18O (m/z 48) is not relevant at 30 °C nor at higher temperatures for any catalyst, indicating that the two 18O atoms of a 13C18O18O molecule do not react with the same surface 12C-containing species.

The m/z 47 (13C16O18O) and m/z 45 (13C16O16O) signals indicate that the 13C atoms of the pulsed CO2 molecules are reoxidized with catalyst 16O once the 13C=18O bonds are broken, leading to the exchange of one or two oxygens, respectively. At room temperature, the double exchange prevails in the Ru/CeO2 catalyst (Figure 6a), and single exchange (Figure 6b and c) is more relevant in Pr-containing catalysts; the higher the Pr loading, the worse is the double exchange. This difference between Pr-free and Pr-containing catalysts suggests that the C=O bond-breaking rate is the slowest step of the process that involves: (i) CO2 adsorption, (ii) C=O bond breaking, (iii) reoxidation of surface carbon species with catalyst oxygen, and (iv) CO2 desorption. The slowest step (C=O bond breaking) is faster for Ru/CeO2 than for Ru/CeXPrOx catalysts, and for this reason the Pr-free catalyst has more time to exchange both oxygen atoms of the CO2 molecule than the Pr-containing catalysts before the CO2 molecule is desorbed. It is known that the most active sites for CO2 dissociation are oxygen vacancies located at the Ru–CeO2 interface,41,46 and the negative effect of Pr in the exchange of oxygen atoms between catalyst and CO2 is in accordance with the negative effect of Pr in the Ru–CeO2 interaction.

Minor differences in the distribution of the carbon species are noticed between 30 and 100 °C, but significant changes are observed at 200, 250, and 300 °C. The main change occurring at 200 °C is that the percentages of evolved nonisotopic CO2 (m/z 44) drop while the percentages of double oxygen exchanged CO2 (m/z 45; 13C16O16O) increase, that is, the exchange of oxygen atoms of the chemisorbed CO2 molecules is enhanced. This means that the slow step of the oxygen exchange process (C=O bond breaking) at 30 and 100 °C is significantly enhanced at 200 °C. As mentioned, the most active sites for CO2 chemisorption and dissociation are vacant sites located at the Ru–CeO2 interface,41 and an increase in the reduction degree of the catalyst surface would promote a higher concentration of oxygen vacancies, which would explain the enhanced CO2 dissociation at 200 °C.

At this temperature, the presence of Pr favors the double exchange of oxygen, and the drop in m/z 44 signal (12C16O16O) and increase of the m/z 45 one (13C16O16O) are the highest for Ru/Ce25PrOx and the lowest for Ru/CeO2. This could be related to the improved oxygen mobility into the ceria lattice upon Pr doping, as observed in H2-TPR. Once a 13C=18O bond of a 13C18O18O molecule is broken on a vacant site at the Ru–CeO2 interface, the created 18O species moves through the CeO2 support, leaving the vacant site available for further dissociative chemisorption of CO2. As such, the CeO2 support is a sink for 18O species, and the Pr doping improves the exchange of the oxygen atoms of the CO2 molecules by the oxygen of the catalyst due to the higher oxygen mobility.

For all catalysts, under the experimental conditions of the isotopic experiments, the release of CH4 species occurs in a significant percentage at 250 and 300 °C, and the formation of CH4 (m/z 15 for 12CH4 and m/z 16 for 13CH4) occurs together with the drop of the m/z 45 (13C16O16O) and m/z 46 (12C16O18O) signals. This means that, at 250 and 300 °C, the energy is high enough to hydrogenate the carbon intermediates once the 13C18O18O molecules are chemisorbed and the 13C=18O bonds are broken.

The percentages of CH4 species evolved (m/z 15 or m/z 16) and CO2 species depleted (m/z 45 and m/z 46) with regard to lower temperatures depend on the catalyst and on the temperature. As such, for Ru/CeO2 at both 250 and 300 °C, the main CO2 species consumed is 12C16O18O (m/z 46) and the main CH4 species evolved is 12CH4 (m/z 15). This is evidence that, for this catalyst, the species hydrogenated to CH4 are carbon intermediates present on the catalyst surface before the 13C18O18O pulse. The behavior of Ru/Ce3PrOx is quite similar to that of Ru/CeO2, and only a few 13CH4 (m/z 16) species were detected at 300 °C. On the contrary, for Ru/Ce25PrOx at 250 °C, the main CH4 species evolved is 13CH4 (m/z 16), and both the 13C16O16O (m/z 45) and 12C16O18O (m/z 46) signals drop. In this case, the hydrogenated carbon atoms come from the pulsed 13C18O18O molecules, which are hydrogenated once the 13C=18O bonds are broken. The distribution of carbon products changes at 300 °C, and the percentages of carbon species are the same for Ru/Ce3PrOx and Ru/Ce25PrOx at this temperature.

As a summary of the isotopic experiments, a dynamic equilibrium has been observed between gas-phase CO2 molecules and carbon species on the catalyst surface. At low temperature (30 and 100 °C), the adsorption–desorption of the CO2 molecules occurs both without breaking the C=O bonds and with breaking these bonds and exchanging oxygen atoms between the CO2 molecules and the catalysts. At 200 °C, the dissociation and exchange of oxygens is significantly favored with regard to the associative adsorption–desorption, and at 250 and 300 °C, surface intermediates created upon CO2 dissociation are hydrogenated to CH4.

Pr-doping on the CeO2 support has different effects in these processes. Pr hinders the Ru–CeO2 interaction and therefore hinders the dissociation of the CO2 molecules at low temperature, which takes place at the Ru–CeO2 interface. However, once the temperature is high enough (200 °C), Pr improves the oxygen mobility in CeO2, and this enhances the dissociation of the C=O bonds because the remaining oxygen atoms are delivered faster to the support sink, cleaning up the vacant sites.

3.5. In Situ Raman Spectroscopy Experiments

The important role of catalyst vacant sites in the CO2 methanation reaction pathway has been inferred from isotopic experiments because these sites are related with CO2 dissociation and with oxygen mobility in the ceria support. Raman spectroscopy is a powerful tool to identify vacant sites on ceria, and in situ experiments have been performed to monitor the behavior of such vacant sites under reaction conditions. Figure 7 shows, as a representative example, the Raman spectra recorded for the three catalysts at 25 °C under the methanation gas mixture (10% CO2, 40% H2, N2 balance) in steady state after reduction at 450 °C in 50% H2/N2 for 1 h.

Figure 7.

Figure 7

In situ Raman spectra recorded at 25 °C under methanation mixture (10% CO2, 40% H2, and N2 balance) after reduction at 450 °C with H2/N2 for 1 h.

All of the spectra show the same characteristic bands, but the area and intensity of these bands differ in each catalyst and temperature. The main band around 465 cm–1 is assigned to the F2g mode of the fluorite structure of ceria, and it is produced by oxygen anions breathing around the equilibrium position in the tetrahedral sites of the cubic unit cell. Another relevant band, denoted as D, appears around 565 cm–1, which is assigned to oxygen vacancies created upon removal of part of the ceria oxygens due to the partial reduction of Ce4+ and Pr4+ cations.5053 The bands at 523 and 640 cm–1 are assigned to monocrystalline RuOx, and they strongly overlap with the isolate surface oxygen vacancy bands from the CeO2 lattice and the shoulder of 2TO overtone that results in a flattened band.5456 To monitor changes in the oxygen vacancies population during the methanation reaction, all spectra have been deconvoluted, and the relative concentration of vacancies has been calculated for each spectrum as the ratio between the area of the vacant sites D band and the total area of the spectrum. The results of this quantification have been plotted in Figure 8 for the three catalysts during the reduction pretreatment and during further methanation experiments.

Figure 8.

Figure 8

Evolution of the oxygen vacancy sites on CeO2 during the reduction pretreatent (50% H2/N2) and further heating under methanation mixture (10% CO2, 40% H2, N2 balance) monitored by Raman spectroscopy.

As expected, the number of vacant sites increases during the reduction pretreatment with H2, and Pr favors the creation of vacancies; the higher the Pr loading, the higher is the amount of oxygen vacancies. Partial reoxidation of these oxygen vacancies takes place by CO2 once the methanation mixture is fed to the reactor, and the reoxidation rate and degree are different for each catalyst. For Ru/CeO2, reoxidation occurs in a relevant extent at 100 °C, while reoxidation of oxygen vacancies increases progressively from room temperature until 200 °C for Ru/Ce3PrOx and Ru/Ce25PrOx. This filling of oxygen vacancies observed by Raman spectroscopy between room temperature and 200 °C is consistent with the dynamic equilibrium between the gas phase and chemisorbed CO2 molecules deduced from isotopic experiments.

The amount of oxygen vacancies increases under methanation conditions above 200 °C (Figure 8), that is, the effect of H2 reduction is observed in the CO2 + H2 mixture. Figure 8 profiles evidence that, under methanation conditions (T ≥ 200 °C and CO2 + H2 gas mixture), each catalyst reaches a balance for each temperature between the H2 reduction and CO2 oxidation processes, and the amount of oxygen vacancies is the result of this balance. The highest concentration of oxygen vacancies is achieved by the Ru/Ce3PrOx catalyst under CO2 methanation conditions, and this is also the most active catalyst (Figure 1) above 250 °C. This correlation suggests that Ru/Ce3PrOx is able to keep the ceria support more reduced under methanation conditions than Ru/CeO2 and Ru/Ce25PrOx, and this has a positive effect on the catalytic activity because the chemisorption and dissociation of CO2 are very effective on reduced sites at the Ru–CeO2 interface.

These Raman spectroscopy experiments confirm the double role of Pr doping. On the one hand, Pr improves the reducibility of ceria, which is evidenced during the reduction pretreatment by creation of oxygen vacancies on the ceria support. On the other hand, Pr hinders the Ru–CeO2 interaction, which negatively affects the dissociation of CO2 and the reoxidation of oxygen vacancies, which is the most relevant event under the methanation gas mixture at temperatures below 200 °C. Once the temperature is high enough (T ≥ 200 °C), the two effects of Pr doping contribute in opposite ways to ceria reduction by H2 and reoxidation by CO2, reaching an optimum for the Ru/Ce3PrOx catalyst.

3.6. In Situ DRIFTS Experiments

Finally, the CO2 methanation reaction intermediates were studied by in situ DRIFTS measurements under the CO2 methanation reaction mixture at steady-state conditions, after reduction of the catalysts at 450 °C in H2/He for 1 h and cooling down to room temperature in He flow. A background spectrum was recorded at room temperature in He and subtracted from further spectra; therefore, bands shown in the spectra (Figure 9) only belong to surface species created (or depleted) under the CO2 methanation mixture. As shown in Figure 9, three relevant wavelength ranges were distinguished with characteristic bands assigned to C–O and C=O vibration modes (at 1800–1200 cm–1 range), ruthenium carbonyls (at 2200–1800 cm–1 range), and C–H vibration modes (at 2600–3200 cm–1 range), providing evidence of the formation of bidentate carbonates (at 1580 and 1280 cm–1), formates (2825–2950, 1615, and 1380 cm–1), and ruthenium carbonyls (1920 and 2017–2040 cm–1).

Figure 9.

Figure 9

In situ DRIFTS spectra recorded in steady-state conditions under 10% CO2, 40% H2, and He balance for (a) Ru/CeO2, (b) Ru/Ce3PrOx, and (c) Ru/Ce25PrOx. Pretreatment at 450 °C under 50% H2/He.

Pr affects the intensity of the signals of the different intermediates. The Ru/CeO2 catalyst shows bands compatible with the formation of bidentate carbonates, formates, and carbonyls, even at room temperature. These species are the same ones previously detected in similar conditions for Ru/CeO2 catalysts, and the changes introduced by praseodymium are related with the intensity of the signals, which are lower for the Ru/CeXPrOx catalysts with regard to Ru/CeO2.

The presence of carbonates, formates, and carbonyls on the catalysts surface at room temperature is consistent with the conclusions of the isotopic exchange experiments, where evidence about the dynamic equilibrium between gas-phase CO2 and surface carbon species was found, and is also in agreement with the reoxidation of the catalysts by CO2 deduced from Raman spectroscopy experiments. As a general trend, the intensity of the signals increases with temperature until a maximum value, and above this maximum the signals remain stable or decrease. For easier analysis of changes with temperature, Figure 10 shows the intensity of selected bands for each species identified in the spectra after baseline subtraction.

Figure 10.

Figure 10

Evolution of (a) carbonate, (b) ruthenium carbonyl, and (c) formate signals with temperature during in situ DRIFTS experiments under 10% CO2, 40% H2, and He balance (pretreatment in H2/He at 450 °C).

It is reasonable to assume, according to Figure 10, that carbonates are hardly hydrogenated to methane while formates and carbonyls are the most efficient reaction intermediates toward total hydrogenation. Ru/CeO2 support doping with Pr diminishes the formation of carbonates, as observed in Figure 10a, therefore keeping the catalyst surface with a lower coverage of carbon species with poor relevance for CH4 production. This effect is expected to have a positive contribution to the catalytic behavior and could be related with the improved ceria reduction by Pr doping, as deduced in H2-TPR characterization. It is known that carbonates are created on ceria after chemisorption of CO2 on surface oxygens, and the improved reducibility of the support will decrease the amount of these types of chemisorption sites under the methanation reaction conditions.

The surface concentrations of carbonyls (Figure 10b) and formates (Figure 10c) also decrease for Pr-containing catalysts with regard to Ru/CeO2; that is, Pr not only hinders the formation of unproductive carbonates but also hinders the formation of the productive reaction intermediates, and this is expected to have a negative effect on the catalytic activity. Once again, DRIFTS experiments show a double role of Pr affecting the formation of carbon surface species that are both productive and unproductive for methane formation.

It is important to compare the trend of the carbonyl (Figure 10b) and formate (Figure 10c) signals with temperature. The surface coverage of formates increases from room temperature until 200 °C for all catalysts and decreases above this temperature once the production of methane starts to be relevant. This is consistent with the participation of formates as reaction intermediates. On the contrary, carbonyl concentrations increase with temperature until reaching a quite stable value, and this could indicate that the slowest reaction step is the hydrogenation of carbonyls to methane.

In conclusion, the DRIFTS experiments show that Pr doping decreases the population of surface carbon species created on the catalysts upon CO2 chemisorption under methanation reaction conditions, affecting both productive reaction intermediates (formates and carbonyls) and unproductive carbonates.

4. Conclusions

The effect of Pr in Ru/CeO2 catalyst for CO2 methanation has been analyzed in this study, and the main conclusions can be summarized as follows:

Pr doping in low concentration is beneficial for CO2 methanation, and it has been observed that a 3%-doped Ru/CeO2 catalyst is moderately more active than bare Ru/CeO2 from 250 °C onward. On the contrary, high Pr concentration has a negative effect on the catalytic activity.

H2-TPR experiments showed that Pr doping has a double role in the reducibility of Ru/CeO2. Pr hinders the reduction of ruthenium species because it partially impedes the Ru-CeO2 interaction, but it improves the reducibility and oxygen mobility of the ceria support.

Pulse experiments with isotopic CO2 evidenced a dynamic equilibrium between gas-phase CO2 molecules and carbon species on the catalyst surface. At low temperature (30 and 100 °C), the adsorption–desorption of the CO2 molecules occurs both without breaking the C=O bonds and with breaking these bonds and exchanging oxygen atoms between the CO2 molecules and the catalysts. At 200 °C, the dissociation and exchange of oxygens is significantly favored with regard to the associative adsorption–desorption, and at 250 and 300 °C the surface intermediates created upon CO2 dissociation are hydrogenated to CH4. Pr doping on the CeO2 support has different effects in these processes. Pr hinders the Ru–CeO2 interaction and therefore hinders the dissociation of the CO2 molecules at low temperature, which takes place at the Ru–CeO2 interface. However, once the temperature is high enough (200 °C), Pr improves the oxygen mobility in CeO2, and this enhances the dissociation of the CO2 molecules because the remaining oxygen atoms are delivered faster to the support sink and the dissociation sites are cleaned up faster. In addition, once the methanation temperatures are achieved (T > 200 °C), hydrogenation of the previously chemisorbed surface carbon species is more favorable for Ru/CeO2, while Pr doping favors the hydrogenation of just chemisorbed CO2 molecules.

In situ Raman spectroscopy experiments confirmed the double role of Pr doping and showed that Pr improves the reduction of ceria by H2, with creation of more oxygen vacancies on the Pr-doped ceria supports than in bare ceria. Nevertheless, Pr hinders the Ru–CeO2 interaction, and this negatively affects the dissociation of CO2 and the reoxidation of oxygen vacancies, which is the most relevant event under the methanation gas mixture at temperatures below 200 °C. Once the temperature is high enough (T ≥ 200 °C), the two effects of Pr doping contribute in opposite ways to ceria reduction by H2 and reoxidation by CO2, reaching an optimum for 3% Pr doping.

Finally, in situ DRIFTS experiments evidenced that Pr doping decreases the population of surface carbon species created on the Ru/CeO2 catalysts surface upon CO2 chemisorption under methanation reaction conditions, affecting both productive reaction intermediates (formates and carbonyls) and unproductive carbonates.

Acknowledgments

This work was financially supported by Generalitat Valenciana (PROMETEO/2018/0765), MINECO (CTQ2015-67597-C2-2-R); MICINN (PID2019-105960RB-C22); Junta de Andalucía (Project P18-RTJ-2974); European Union’s Horizon 2020 research and innovation program (Marie Skłodowska-Curie Grant agreement no. 713567); and Science Foundation Ireland Research Centre (award 12/RC/2278_P2).

The authors declare no competing financial interest.

References

  1. Pereira-Hernández X. I.; De La Riva A.; Muravev V.; Kunwar D.; Xiong H.; Sudduth B.; Engelhard M.; Kovarik L.; Hensen E. J. M.; Wang Y.; et al. Tuning Pt-CeO2 interactions by high-temperature vapor-phase synthesis for improved reducibility of lattice oxygen. Nat. Commun. 2019, 10, 1358. 10.1038/s41467-019-09308-5. [DOI] [PMC free article] [PubMed] [Google Scholar]
  2. Trovarelli A. Catalytic Properties of Ceria and CeO2-Containing Materials. Catal. Rev.: Sci. Eng. 1996, 38, 439–520. 10.1080/01614949608006464. [DOI] [Google Scholar]
  3. Campbell C. T.; Peden C. H. F. Oxygen Vacancies and Catalysis on Ceria Surfaces. Science 2005, 309, 713–714. 10.1126/science.1113955. [DOI] [PubMed] [Google Scholar]
  4. Atribak I.; Bueno-López A.; García-García A. Role of yttrium loading in the physico-chemical properties and soot combustion activity of ceria and ceria–zirconia catalysts. J. Mol. Catal. A: Chem. 2009, 300, 103–110. 10.1016/j.molcata.2008.10.043. [DOI] [Google Scholar]
  5. Ke J.; Xiao J.-W.; Zhu W.; Liu H.; Si R.; Zhang Y.-W.; Yan C.-H. Dopant-Induced Modification of Active Site Structure and Surface Bonding Mode for High-Performance Nanocatalysts: CO Oxidation on Capping-free (110)-oriented CeO2:Ln (Ln = La–Lu) Nanowires. J. Am. Chem. Soc. 2013, 135, 15191–15200. 10.1021/ja407616p. [DOI] [PubMed] [Google Scholar]
  6. Xiao Z.; Ji S.; Li Y.; Hou F.; Zhang H.; Zhang X.; Wang L.; Li G. Tuning oxygen vacancies on mesoporous ceria nanorods by metal doping: Controllable magnetic property. Appl. Surf. Sci. 2018, 455, 1037–1044. 10.1016/j.apsusc.2018.05.216. [DOI] [Google Scholar]
  7. Di Monte R.; Kašpar J. Heterogeneous environmental catalysis – a gentle art: CeO2–ZrO2 mixed oxides as a case history. Catal. Today 2005, 100, 27–35. 10.1016/j.cattod.2004.11.005. [DOI] [Google Scholar]
  8. Wang Z.; Quan Z.; Lin J. Remarkable Changes in the Optical Properties of CeO2 Nanocrystals Induced by Lanthanide Ions Doping. Inorg. Chem. 2007, 46, 5237–5242. 10.1021/ic0701256. [DOI] [PubMed] [Google Scholar]
  9. Xiao Z.; Zhang X.; Hou F.; Wu C.; Wang L.; Li G. Tuning metal-support interaction and oxygen vacancies of ceria supported nickel catalysts by Tb doping for n-dodecane steam reforming. Appl. Surf. Sci. 2020, 503, 144319–144331. 10.1016/j.apsusc.2019.144319. [DOI] [Google Scholar]
  10. Ilieva L.; Pantaleo G.; Ivanov I.; Nedyalkova R.; Venezia A. M.; Andreeva D. NO reduction by CO over gold based on ceria; doped by rare earth metals. Catal. Today 2008, 139, 168–173. 10.1016/j.cattod.2008.06.033. [DOI] [Google Scholar]
  11. Terribile D.; Trovarelli A.; De Leitenburg C.; Primavera A.; Dolcetti G. Catalytic combustion of hydrocarbons with Mn and Cu-doped ceria–zirconia solid solutions. Catal. Today 1999, 47, 133–140. 10.1016/S0920-5861(98)00292-2. [DOI] [Google Scholar]
  12. Peden H. F.; Herman G. S.; Chambers S. A.; Gao Y.; Kim Y.-J.; Belton D. N. In Studies in Surface Science and Catalysis; Corma A.; Melo F.; Mendioroz S.; Fierro J. L. G., Eds.; Elsevier: Amsterdam, 2000; Vol. 130, pp 1367–1372. [Google Scholar]
  13. Jen H.-W.; Graham G. W.; Chun W.; McCabe R. W.; Cuif J.-P.; Deutsch S. E.; Touret O. Characterization of model automotive exhaust catalysts: Pd on ceria and ceria–zirconia supports. Catal. Today 1999, 50, 309–328. 10.1016/S0920-5861(98)00512-4. [DOI] [Google Scholar]
  14. Trovarelli A.; de Leitenburg C.; Dolcetti G. Design better cerium-based oxidation catalysts. CHEMTECH 1997, 27, 32–37. [Google Scholar]
  15. Letichevsky S.; Tellez C. A.; de Avillez R. R.; da Silva M. I. P.; Fraga M. A.; Appel L. G. Obtaining CeO2-ZrO2 mixed oxides by coprecipitation: Role of preparation conditions. Appl. Catal., B 2005, 58, 203–210. 10.1016/j.apcatb.2004.10.014. [DOI] [Google Scholar]
  16. De Rivas B.; Guillén-Hurtado N.; López-Fonseca R.; Coloma-Pascual F.; García-García A.; Gutiérrez-Ortiz J. I.; Bueno-López A. Activity; selectivity and stability of praseodymium-doped CeO2 for chlorinated VOCs catalytic combustion. Appl. Catal., B 2012, 121–122, 162–170. 10.1016/j.apcatb.2012.03.029. [DOI] [Google Scholar]
  17. Davó-Quiñonero A.; González-Mira J.; Lozano-Castelló D.; Bueno-López A. Templated Synthesis of Pr-Doped Ceria with Improved Micro and Mesoporosity Porosity; Redox Properties and Catalytic Activity. Catal. Lett. 2018, 148, 258–266. 10.1007/s10562-017-2215-1. [DOI] [Google Scholar]
  18. Guillén-Hurtado N.; Giménez-Mañogil J.; Martínez-Munuera J. C.; Bueno-López A.; García-García A. Study of Ce/Pr ratio in ceria-praseodymia catalysts for soot combustion under different atmospheres. Appl. Catal., A 2020, 590, 117339–117356. 10.1016/j.apcata.2019.117339. [DOI] [Google Scholar]
  19. Krishna K.; Bueno-López A.; Makkee M.; Moulijn J. A. Potential rare earth modified CeO2 catalysts for soot oxidation. I. Characterisation and catalytic activity with O2. Appl. Catal., B 2007, 75, 189–200. 10.1016/j.apcatb.2007.04.010. [DOI] [Google Scholar]
  20. Krishna K.; Bueno-López A.; Makkee M.; Moulijn J. A. Potential rare-earth modified CeO2 catalysts for soot oxidation part II: Characterisation and catalytic activity with NO + O2. Appl. Catal., B 2007, 75, 201–209. 10.1016/j.apcatb.2007.04.007. [DOI] [Google Scholar]
  21. Santer B. D.; Taylor K. E.; Wigley T. M. L.; Johns T. C.; Jones P. D.; Karoly D. J.; Mitchell J. F. B.; Oort A. H.; Penner J. E.; Ramaswamy V.; et al. A search for human influences on the thermal structure of the atmosphere. Nature 1996, 382, 39–46. 10.1038/382039a0. [DOI] [Google Scholar]
  22. Santer B. D.; Wehner M. F.; Wigley T. M. L.; Sausen R.; Meehl G. A.; Taylor K. E.; Ammann V.; Arblaster J.; Washington W. M.; Boyle J. S.; et al. Contributions of anthropogenic and natural forcing to recent tropopause height changes. Science 2003, 301, 479–483. 10.1126/science.1084123. [DOI] [PubMed] [Google Scholar]
  23. Liu B.; Li C.; Zhang C.; Yao X.; Chuang S. S. C.; Li Z. Oxygen Vacancy Promoting Dimethyl Carbonate Synthesis from CO2 and Methanol over Zr-Doped CeO2 Nanorods. ACS Catal. 2018, 8, 10446–10456. 10.1021/acscatal.8b00415. [DOI] [Google Scholar]
  24. Valenzuela R. X.; Bueno G.; Cortés Corberán V.; Xu Y.; Chen C. Selective oxidehydrogenation of ethane with CO2 over CeO2-based catalysts. Catal. Today 2000, 61, 43–48. 10.1016/S0920-5861(00)00366-7. [DOI] [Google Scholar]
  25. Vilé G.; Bridier B.; Wichert J.; Pérez-Ramírez J. Ceria in Hydrogenation Catalysis: High Selectivity in the Conversion of Alkynes to Olefins. Angew. Chem., Int. Ed. 2012, 51, 8620–8623. 10.1002/anie.201203675. [DOI] [PubMed] [Google Scholar]
  26. Wang F.; Wei M.; Evans D. G.; Duan X. CeO2-based heterogeneous catalysts toward catalytic conversion of CO2. J. Mater. Chem. A 2016, 4, 5773–5783. 10.1039/C5TA10737G. [DOI] [Google Scholar]
  27. Frontera P.; Macario A.; Ferraro M.; Antonucci P. L. Supported catalysts for CO2 methanation: A review. Catalysts 2017, 7, 59–87. 10.3390/catal7020059. [DOI] [Google Scholar]
  28. Wang F.; He S.; Chen H.; Wang B.; Zheng L.; Wei M.; Evans D. G.; Duan X. Active Site Dependent Reaction Mechanism over Ru/CeO2 Catalyst toward CO2 Methanation. J. Am. Chem. Soc. 2016, 138, 6298–6305. 10.1021/jacs.6b02762. [DOI] [PubMed] [Google Scholar]
  29. Aitbekova A.; Wu L.; Wrasman C. J.; Boubnov A.; Hoffman A. S.; Goodman E. D.; Bare S. R.; Cargnello M. Low-Temperature Restructuring of CeO2-Supported Ru Nanoparticles Determines Selectivity in CO2 Catalytic Reduction. J. Am. Chem. Soc. 2018, 140, 13736–13745. 10.1021/jacs.8b07615. [DOI] [PubMed] [Google Scholar]
  30. Karelovic A.; Ruiz P. Mechanistic study of low temperature CO2 methanation over Rh/TiO2 catalysts. J. Catal. 2013, 301, 141–153. 10.1016/j.jcat.2013.02.009. [DOI] [Google Scholar]
  31. Abdel-Mageed A. M.; Widmann D.; Olesen S. E.; Chorkendorff I.; Behm R. J. Selective CO Methanation on Highly Active Ru/TiO2 Catalysts: Identifying the Physical Origin of the Observed Activation/Deactivation and Loss in Selectivity. ACS Catal. 2018, 8, 5399–5414. 10.1021/acscatal.8b00384. [DOI] [Google Scholar]
  32. Zhao K.; Wang L.; Calizzi M.; Moioli E.; Zuttel A. In Situ Control of the Adsorption Species in CO2 Hydrogenation: Determination of Intermediates and Byproducts. J. Phys. Chem. C 2018, 122, 20888–20893. 10.1021/acs.jpcc.8b06508. [DOI] [Google Scholar]
  33. Proaño L.; Tello E.; Arellano-Trevino M. A.; Wang S.; Farrauto R. J.; Cobo M. In-situ DRIFTS study of two-step CO2 capture and catalytic methanation over Ru;”Na2O”/Al2O3 Dual Functional Material. Appl. Surf. Sci. 2019, 479, 25–30. 10.1016/j.apsusc.2019.01.281. [DOI] [Google Scholar]
  34. Navarro-Jaén S.; Szego A.; Bobadilla L. F.; Laguna O. H.; Romero-Sarria F.; Centeno M. A.; Odriozola J. A. Operando Spectroscopic Evidence of the Induced Effect of Residual Species in the Reaction Intermediates during CO2 Hydrogenation over Ruthenium Nanoparticles. ChemCatChem 2019, 11, 2063–2068. 10.1002/cctc.201900101. [DOI] [Google Scholar]
  35. Falbo L.; Visconti C. G.; Lietti L.; Szanyi J. The effect of CO on CO2 methanation over Ru/Al2O3 catalysts: a combined steady-state reactivity and transient DRIFT spectroscopy study. Appl. Catal., B 2019, 256, 117791–117803. 10.1016/j.apcatb.2019.117791. [DOI] [Google Scholar]
  36. Zhan Y.; Wang Y.; Gu D.; Chen C.; Jiang L.; Takehira K. Ni/Al2O3-ZrO2 catalyst for CO2 methanation: The role of -(Al; Zr)2O3 formation. Appl. Surf. Sci. 2018, 459, 74–79. 10.1016/j.apsusc.2018.07.206. [DOI] [Google Scholar]
  37. Alcalde-Santiago V.; Davó-Quiñonero A.; Lozano-Castelló D.; Quindimil A.; De-La-Torre U.; Pereda-Ayo B.; González-Marcos J. A.; González-Velasco J. R.; Bueno-López A. Ni/LnOx Catalysts (Ln = La; Ce or Pr) for CO2 Methanation. ChemCatChem 2018, 11, 810–819. 10.1002/cctc.201801585. [DOI] [Google Scholar]
  38. Lin J.; Ma C.; Luo J.; Kong X.; Xu Y.; Ma G.; Wang J.; Zhang C.; Li Z.; Ding M. Preparation of Ni based mesoporous Al2O3 catalyst with enhanced CO2 methanation performance. RSC Adv. 2019, 9, 8684–8694. 10.1039/C8RA10348H. [DOI] [PMC free article] [PubMed] [Google Scholar]
  39. Zhang Z.; Tian Y.; Zhang L.; Hu S.; Xiang J.; Wang Y.; Xu L.; Liu Q.; Zhang S.; Hu X. Impacts of nickel loading on properties; catalytic behaviors of Ni//-Al2O3 catalysts and the reaction intermediates formed in methanation of CO2. Int. J. Hydrogen Energy 2019, 44, 9291–9306. 10.1016/j.ijhydene.2019.02.129. [DOI] [Google Scholar]
  40. Shashidhara G. M.; Ravindram M. Methanation of CO2 over Ru-SiO2 catalyst. React. Kinet. Catal. Lett. 1992, 46, 365–372. 10.1007/BF02070959. [DOI] [Google Scholar]
  41. Guo Y.; Mei S.; Yuan K.; Wang De-J.; Liu H.-C.; Yan C. H.; Zhang Y.-W. Low-Temperature CO2 Methanation over CeO2-Supported Ru Single Atoms; Nanoclusters; and Nanoparticles Competitively Tuned by Strong Metal-Support Interactions and H-Spillover Effect. ACS Catal. 2018, 8, 6203–6215. 10.1021/acscatal.7b04469. [DOI] [Google Scholar]
  42. Luo M.-F.; Yan Z.-L.; Jin L.-Y.; He M. Raman spectroscopic study on the structure in the surface and the bulk shell of CexPr1-xO2-δ mixed oxides. J. Phys. Chem. B 2006, 110, 13068–13071. 10.1021/jp057274z. [DOI] [PubMed] [Google Scholar]
  43. Nguyen H. T. T.; Kumabe Y.; Ueda S.; Kan K.; Ohtani M.; Kobiro K. Highly durable Ru catalysts supported on CeO2 nanocomposites for CO2 methanation. Appl. Catal., A 2019, 577, 35–43. 10.1016/j.apcata.2019.03.011. [DOI] [Google Scholar]
  44. Navarro-Jaén S.; Navarro J. C.; Bobadilla L. F.; Centeno M. A.; Laguna O. H.; Odriozola J. A. Size-tailored Ru nanoparticles deposited over -Al2O3 for the CO2 methanation reaction. Appl. Surf. Sci. 2019, 483, 750–761. 10.1016/j.apsusc.2019.03.248. [DOI] [Google Scholar]
  45. Dreyer J. A. H.; Li P.; Zhang L.; Beh G. K.; Zhang R.; Sit P.H.-L.; Teoh W. Y. Influence of the oxide support reducibility on the CO2 methanation over Ru-based catalysts. Appl. Catal., B 2017, 219, 715–726. 10.1016/j.apcatb.2017.08.011. [DOI] [Google Scholar]
  46. Wang F.; Li C.; Zhang X.; Wei M.; Evans D. G.; Duan X. Catalytic behavior of supported Ru nanoparticles on the {100}; {110}; and {111} facet of CeO2. J. Catal. 2015, 329, 177–186. 10.1016/j.jcat.2015.05.014. [DOI] [Google Scholar]
  47. Porta A.; Falbo L.; Visconti C. G.; Lietti L.; Bassano C.; Deiana P. Synthesis of Ru-based catalysts for CO2 methanation and experimental assessment of intraporous transport limitations. Catal. Today 2020, 343, 38–47. 10.1016/j.cattod.2019.01.042. [DOI] [Google Scholar]
  48. Labhsetwar N.; Watanabe A.; Rayalu S.; Subrt J.; Mistuhashi T.; Devotta S.; Haneda H. Catalytic properties of strontium ruthenate perovskite prepared by hot isostatic pressure method. Stud. Surf. Sci. Catal. 2006, 162, 825–831. 10.1016/S0167-2991(06)80986-9. [DOI] [Google Scholar]
  49. Eckle S.; Anfang H. G.; Behm R. J. Reaction intermediates and side products in the methanation of CO and CO2 over supported Ru catalysts in H2-rich reformate gases. J. Phys. Chem. C 2011, 115, 1361–1367. 10.1021/jp108106t. [DOI] [Google Scholar]
  50. Guo M.; Lu J.; Wu Y.; Wang Y.; Luo M. UV and visible Raman studies of oxygen vacancies in rare-earth-doped ceria. Langmuir 2011, 27, 3872–3877. 10.1021/la200292f. [DOI] [PubMed] [Google Scholar]
  51. Chan H. Y. H.; Takoudis C. G.; Weaver M. J. High-pressure oxidation of ruthenium as probed by surface-enhanced Raman and X-ray photoelectron spectroscopies. J. Catal. 1997, 172, 336–345. 10.1006/jcat.1997.1841. [DOI] [Google Scholar]
  52. McBride J. R.; Hass K. C.; Poindexter B. D.; Weber W. H. Raman and x-ray studies of Ce1-xRExO2-y; where RE = La; Pr; Nd; Eu; Gd; and Tb. J. Appl. Phys. 1994, 76, 2435–2441. 10.1063/1.357593. [DOI] [Google Scholar]
  53. Dai Q.; Huang H.; Zhu Y.; Deng W.; Bai S.; Wang X.; Lu G. Catalysis oxidation of 1;2-dichloroethane and ethyl acetate over ceria nanocrystals with well-defined crystal planes. Appl. Catal., B 2012, 117–118, 360–368. 10.1016/j.apcatb.2012.02.001. [DOI] [Google Scholar]
  54. Davó-Quiñonero A.; Bailón-García E.; López-Rodríguez S.; Juan-Juan J.; Lozano-Castelló D.; García-Melchor M.; Herrera F. C.; Pellegrin E.; Escudero C.; Bueno-López A. Insights into the Oxygen Vacancy Filling Mechanism in CuO/CeO2 Catalysts: A Key Step Toward High Selectivity in Preferential CO Oxidation. ACS Catal. 2020, 10, 6532–6545. 10.1021/acscatal.0c00648. [DOI] [Google Scholar]
  55. Weber W. H.; Hass K. C.; McBride J. R. Raman study of CeO2: Second-order scattering; lattice dynamics; and particle-size effects. Phys. Rev. B: Condens. Matter Mater. Phys. 1993, 48, 178–185. 10.1103/PhysRevB.48.178. [DOI] [PubMed] [Google Scholar]
  56. Mar S. Y.; Chen C. S.; Huang Y. S.; Tiong K. K. Characterization of RuO2 thin films by Raman spectroscopy. Appl. Surf. Sci. 1995, 90, 497–504. 10.1016/0169-4332(95)00177-8. [DOI] [Google Scholar]

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