Abstract

In2O3 is a promising electrocatalyst for CO2 electroreduction (CO2ER) to formate. In2O3 nanoparticles doped with Pd, Ni, Co, Zr, and Ce promoters using flame-spray pyrolysis were characterized and evaluated in a gas diffusion electrode for the CO2ER. Doping results in slight shifts of the In binding energy as probed by XPS, which correlates with a change of the Faradaic efficiency to formate (FEformate) in the order Ce-doped In2O3 > Zr-doped In2O3 > In2O3 > Pd-doped In2O3 > Ni-doped In2O3 > Co-doped In2O3. However, the differences in CO2ER performance are caused mainly by the different extent of In2O3 reduction. Co-doped In2O3 is prone to complete reduction to a stable Co–In alloy with a low FEformate due to a high hydrogen evolution activity. The stabilizing effect of Ce on In2O3 is further demonstrated by an X-ray absorption spectroscopy study of a set of Ce-doped In2O3 samples (10, 50, 90 at%), highlighting that reduction of In2O3 is suppressed with increasing Ce content. Optimum performance in terms of FEformate is obtained at a Ce content of 10 at%, which is attributed to the stabilization of In2O3 under negative bias up to −2 V. At higher Ce content, less active CeO2 is formed. The highest FEformate of 86% observed for In2O3 doped with 10 at% Ce, at a current density of 150 mA/cm2, compares favorably with a FEformate of 78% for In2O3.
Keywords: CO2 electroreduction, formate, In2O3, dopants, cerium promotion
Introduction
CO2 is considered a circular carbon source for the chemical industry and transport sector. Converting CO2 to chemicals and fuels using renewable energy sources could replace fossil resources in these sectors, thereby closing the carbon cycle. Electrochemical CO2 reduction offers a direct pathway to utilize renewable electricity to convert CO2 into base chemicals, which can be further converted to other chemicals and fuels.1 Typical products of the CO2 electroreduction reaction are CO, ethylene, ethanol, and formic acid.2 Among these, formic acid and formate have the potential to serve as feedstock for chemicals and as a liquid hydrogen carrier relevant to energy storage in chemical bonds.3,4 Electrochemical CO2 reduction to formate can achieve high Faradaic efficiency at industrially relevant current densities, making it one of the most promising electrochemical processes for commercialization.1,5 Typical electrocatalysts for CO2 reduction comprise the metals Sn, In, and Bi.2,5,6 Such catalysts reach Faradaic efficiencies close to 100% at current densities >100 mA/cm2.5
The reaction mechanism of CO2 electroreduction (CO2ER) to formic acid involves an oxygen-bound formate intermediate on the catalytic surface.7 The carbonyl pathway that leads to undesired CO byproduct competes with this formate pathway. A high oxophilicity of a metal catalyst, therefore, stabilizes the formate intermediate, which is thought to increase the selectivity of the formate pathway over the carbonyl one.8 On the other hand, metal oxides are widely believed to be the most active for CO2ER to formate. Still, their stability against reduction to the metal under the reducing CO2ER conditions is heavily debated.9−13 Several theoretical studies showed that defects in metal oxides, such as oxygen vacancies, can act as CO2 adsorption sites.14,15 Alternatively, it is proposed that surface hydroxyls can react with CO2 to form a carbonate intermediate before15,16 or instead of the formate intermediate.17 A major benefit of metal oxides over metallic catalysts is the higher kinetic barrier of the former for the main competing hydrogen evolution reaction (HER).18,19 Experimental studies to understand the role of oxide surfaces indicate that oxygen vacancies and hydroxyls are involved in reducing CO2 to formate. Nevertheless, these studies are primarily conducted at low current densities in H-cell configurations employed in conventional electrochemical studies, which are, for instance, more conducive to coupling with surface-sensitive characterization techniques such as infrared spectroscopy.16,17,20−22 Industrial applications require high current densities, implying operation at more negative potentials. Convincing experimental evidence for the importance of oxides as the main catalyst during the CO2ER at industrially relevant conditions is lacking. Broekmann and co-workers utilized operando Raman, X-ray absorption spectroscopy (XAS), and X-ray diffraction (XRD) to study the impact of experimental conditions at which Sn- and Bi-oxide phases remain stable utilizing a gas diffusion electrode (GDE) configuration.11,13,23 They observed a strong correlation between the presence of Sn-oxide and Bi-oxy-carbonate phases and high Faradaic efficiency (FE) toward formate. Such a study has not been undertaken yet for In-based CO2ER catalysts. Wang et al. showed by operando XAS that a mixed In–Sn-oxide shell was maintained on an In–Sn alloy electrocatalyst during CO2ER at a potential up to −1.2 V vs RHE in an H-cell configuration.24
Here, we report on In2O3-based catalysts for CO2 electroreduction to formate. In2O3 nanoparticles doped with Pd, Ni, Co, Ce, and Zr were obtained using flame synthesis. It has been demonstrated that flame spray pyrolysis (FSP) is suitable to incorporate other elements in In2O3 nanoparticles.25 Doping of the In2O3 with these transition metals can modify the catalytic properties of the In2O3 surface and its stability against metal reduction, thereby impacting the CO2ER to formate in terms of FE and stability. Pd and Co were chosen because of their activity toward reduction of CO2 to formate at low potential.26,27 Ce and Zr were selected, as their oxides form strong interactions with In2O3,28 which can stabilize their dispersion and impact oxygen vacancy formation as reported to be beneficial for thermal CO2 hydrogenation.25,29 During our investigations, we found that Zr and especially Ce doping positively impacted the FE to formate. This led us to investigate in more detail mixed oxides of Ce and In prepared by FSP by varying the Ce content from 0% to 90%. The catalytic performance of the metal oxides is evaluated using gas diffusion electrodes at industrially relevant current densities in the range of 100–200 mA/cm2. The samples are investigated by electron microscopy, XRD, XAS, and X-ray photoelectron spectroscopy (XPS) to elucidate the promoters’ influence on the catalytic activity and stability of In2O3 as a catalyst for the CO2ER. This work is also available as part of a PhD thesis.30
Methods
Catalyst Preparation
In2O3 Nanoparticles
Nanoparticles (NPs) of In2O3 were prepared by flame spray pyrolysis (FSP) using a Tethis NPS10 setup. A 0.15 M In(NO)3 solution was prepared by dissolving an appropriate amount In(NO)3·5H2O (99%, Alfa Aesar) in an equivolumetric mixture of ethanol (99.9%, Biosolve) and 2-ethylhexanoic acid (99%, Sigma-Aldrich). This synthesis was modified by introducing dopants during the FSP preparation, namely 5 wt % Co(NO3)2·6H2O (98%, Sigma-Aldrich), 5 wt % Ni(NO3)2·6H2O (98.5%, Sigma-Aldrich), 5 wt % Pd(OCOCH3)2 (98%, Sigma-Aldrich), 5 wt % Zr(acac)2 (99.9%, Sigma-Aldrich), and 10–90 at% Ce(acac)2 (acac = acetylacetonate, 99.9%, Sigma-Aldrich). For comparison with XPS analysis, the weight-based concentration of the dopant is converted to the atomic concentration with respect to total metal content as listed in Table 1 and Table 2. The solution was then injected into the nozzle of the FSP setup using an injection rate of 5 mL/min. The flame was fed with a flow of 3.0 L/min O2 and 1.5 L/min CH4, to which a dispersion flow of 5.0 L/min O2 was added. The solid particles were collected from a quartz filter placed downstream of the flame region. The (doped) In2O3 solids were sieved over a 250 μm steel sieve. The Ce–In-oxide catalysts are denoted by their atomic Ce content, i.e., Ce(50)-In2O3 having a Ce content of roughly 50 at% with respect to total of In and Ce content.
Table 1. Physicochemical Properties of (Doped) In2O3 Nanoparticles Synthesized by FSP.
| Loading
dopant |
Particle size |
XPS analysis |
|||||
|---|---|---|---|---|---|---|---|
| Catalyst | Nominal (wt%)a | Nominal (at%)a | Surface (at%)b | dTEM (nm) | dXRD (nm) | In2O3 (at%) | In(OH)3/defects (at%) |
| In2O3 | – | – | – | 6.2 ± 1.4 | 9.2 | 87 | 13 |
| Zr–In2O3 | 4.9 | 7.5 | 5.7 | 6.3 ± 1.5 | 8.3 | 85 | 15 |
| Ce–In2O3 | 9.6 | 9.7 | 11 | 6.0 ± 1.6 | 8.2 | 94 | 6 |
| Pd–In2O3 | 5.3 | 6.8 | 7.7 | 5.8 ± 1.7 | 9.0 | 92 | 8 |
| Ni–In2O3 | 5.0 | 11.0 | 16 | 7.3 ± 1.5 | 9.1 | 82 | 18 |
| Co–In2O3 | 5.0 | 11.1 | 11 | 6.7 ± 1.6 | 9.3 | 64 | 36 |
ICP elemental analysis.
XPS surface analysis.
Table 2. Physicochemical Properties of Mixed Ce–In-Oxide Nanoparticles Synthesized by FSP.
| Ce loading |
Particle size |
XPS analysis |
||||||
|---|---|---|---|---|---|---|---|---|
| Catalyst | Nominal (at%)1 | Surface (at%)2 | dTEM (nm) | dXRD In2O3 (nm) | dXRD CeO2 (nm) | In2O3 (at%) | In(OH)3/defect (at%) | Ce4+/Ce3+ ratio |
| In2O3 | – | – | 6.8 ± 2.0 | 8.6 | – | 80 | 20 | – |
| Ce(10)-In2O3 | 11.0 | 8.0 | 6.2 ± 1.5 | 7.8 | – | 92 | 8 | 3.2 |
| Ce(50)-In2O3 | 51.5 | 38 | 6.6 ± 1.7 | – | 4.6 | 89 | 11 | 4.2 |
| Ce(90)-In2O3 | 92.6 | 83 | 6.0 ± 2.0 | – | 7.1 | 55 | 45 | 5.3 |
Gas Diffusion Electrode (GDE) Preparation
A suspension of the catalyst was prepared by weighing appropriate amounts of (doped) In2O3, Vulcan XC-72R activated carbon (AC) as support and PTFE nanoparticles (Sigma-Aldrich, 1 μm) and dispersing these solids by sonication in 3 mL isopropanol (99.9%, Sigma-Aldrich) and 1 mL ultrapure water. Nafion ionomer solution (D-520, dispersion, 5% w/w in water and isopropanol, Alfa Aesar) was added to reach a mixture containing 20 wt % Nafion with respect to solid particles. The solution was sonicated for ∼30 min. The ink was sprayed on a commercial gas diffusion layer (GDL, ELAT LT1400W, FuelCellStore) with a spray gun. The total loading of the catalyst on the GDE, as determined by weighing the GDL before and after catalyst deposition, amounted to 0.30 ± 0.06 mg/cm2 for the (doped) In2O3 nanoparticles and 0.47 ± 0.07 mg/cm2 for the mixed Ce–In catalysts. For operando XAS analysis, a GDE was prepared without activated carbon and PTFE particles employing a higher catalyst loading of 1.04 ± 0.12 mg/cm2 on a commercial GDL (Sigracet 22BB, Ion-Power).
Characterization
Inductively Coupled Plasma Optical Emission Spectrometry (ICP-OES)
The elemental composition of the FSP-synthesized nanoparticles was determined using an AMETEK ICP optical emission spectrometer (Spectroblue) with axial plasma viewing, equipped with a free-running 27.12 MHz generater (1400 W). Around 25 mg of the sample was dissolved in 5 mL concentrated H2SO4 at 220 °C. After cooling, the solution was diluted to 50 mL with demineralized water. Two solutions were prepared to perform the measurements in duplicate. A calibration line with concentrations between 0 to 20 mg/L In, 0 to 10 mg/L Ce, 0 to 5 mg/L Zr, and 0 to 3 mg/L for Co and Ni was used. A second calibration line with concentrations between 0 and 5 mg/L Pd was used due to the overlap of the emission lines of Pd and In.
X-ray Photoelectron Spectroscopy (XPS)
XPS was performed with a K-Alpha XPS apparatus (Thermo Scientific) using an Al anode (Al Kα monochromatic irradiation, 1486.6 eV) operating at 72 W. A spot size of 400 μm was used. Survey and core level spectra were recorded at pass energies of 200 and 50 eV, respectively. The background pressure inside the analysis chamber was kept below 8 × 10–8 mbar. During measurements, a maximum pressure of 3 × 10–7 mbar was observed due to using low energy Ar+ ions for charge neutralization. Catalyst powders were pelletized before XPS analysis to prevent the charging of the insulating In2O3 particles. All spectra were energy corrected by the U‴ component at 916.7 eV of Ce.31 After energy correction of the Ce-containing catalysts, the resulting C 1s peak position of adventitious carbon was used to correct the energy scale for the samples that did not contain Ce. The core level spectra were deconvoluted using a Shirley background and using GL(30) line shapes for most contributions. The metallic In peak was fitted using an LA(1.1,1.7,3) line shape obtained from an In reference sample, which was etched in the vacuum chamber of the XPS apparatus (Figure S8a). The Ce 3d core-line spectra were fitted according to the literature.31−33
X-ray Absorption Spectroscopy (XAS)
Operando XAS analysis was performed at the ROCK beamline at the SOLEIL synchrotron (Paris, France). Data was collected in fluorescence mode at the In K-edge (27940 eV). An electrochemical cell developed in-house by SOLEIL was used. The GDE prepared as described above was used as the working electrode. A gas flow chamber with a Kapton window was placed at the back of the working electrode, while the catholyte chamber was in front of the working electrode. The cell was positioned at a 39° angle with respect to the incoming X-ray beam, and the fluorescence signal was measured from the back of the electrode by an avalanche-photodiode fluorescence detector positioned perpendicular to the beam. A Nafion proton exchange membrane (N324, Ion Power) was used to separate the catholyte and anolyte chambers. Pt foil and Ag/AgCl (6 mm, redoxme, measured at 0.23 V vs SHE at pH 1) electrodes were used as counter and reference electrodes, respectively. An IviumStat potentiostat was used to set the potential and record the electrochemical response of the working electrode. The anolyte (0.5 M H2SO4) was pumped using a peristaltic pump at a flow of 12 mL/min. Catholyte (0.5 M KHCO3) was introduced in the catholyte chamber. A mass spectrometer (MKS Cirrus LM99 Analyzer) was used to detect CO2, H2 and CO in the gas exit line from the gas chamber at the back of the GDE. Catholyte was not pumped around to avoid leakage through the GDE into the gas exit toward the mass spectrometer. The catholyte was refreshed in each experiment. CO2 was passed at the back of the GDE at a flow rate of 5 mL/min (flow-by mode). A spectrum was recorded every 0.5 s. As 10 spectra were averaged to increase the signal-to-noise ratio, the temporal resolution of the measurements was 5 s. Energy calibration was done using an In foil. The X-ray absorption near-edge structure (XANES) data were background-subtracted, normalized, and fitted using linear combination analysis with XAS viewer as implemented in the Larch software package. The extended X-ray adsorption fine structure (EXAFS) analysis on k3-weighted In K-edge data was also performed with XAS viewer. Scattering paths were calculated with FEFF8 using crystal structures of In2O3, In and In(OH)3. The amplitude reduction factor S02 (0.77) used for fitting the Ce–In-oxide EXAFS spectra was determined by fitting the two In–In scattering paths of the first shell of reference In foil, fixing the coordination numbers to, respectively, 4 and 8 (Table S2).
X-ray Diffraction (XRD)
XRD was performed using a Bruker D2 Phaser diffractometer using Cu Kα radiation (1.5406 Å). The XRD diffractograms of catalyst powders were recorded between 2θ = 10° and 90° at a scan rate of 1 s/step and a step size of 0.02°. XRD patterns on a GDE were obtained at a scan rate of 2 s/step and a step size of 0.01°. The crystallite size was calculated using the Scherrer equation as implemented in the DIFFRAC.EVA software package.
Wide Angle X-ray Scattering (WAXS)
Ex situ WAXS measurements were performed at beamline ID31 of the ESRF synchrotron (Grenoble, France). The incident photon energy was 75 keV (l = 0.0165 nm) using a Pilatus CdTe 2 M detector set up in the Debye–Scherrer geometry. Kapton tubes were filled with powder samples and sealed with bee wax before analysis. The WAXS peaks were fitted with a Voigt function to determine the full width at half-maximum (fwhm). The average crystal size was calculated using the Scherrer equation. Rietveld refinement was performed using GSAS-II software. In2O3 and CeO2 crystal structures were used to fit the diffraction patterns of the as-prepared catalysts. The patterns were fitted between 2θ = 1.5 and 9. The background was fitted using a chebyschev-1 function with 3 coefficients. Instrument parameters were determined by fitting a reference CeO2 sample and fixed for all samples. Sample displacement parameters were determined by fitting the pure In2O3 sample and fixed for all Ce-doped In2O3 samples. The fitting was performed by subsequent fitting of the phase fractions, micro strain and lattice parameter in the given order. After several iterations (>3), the size and lattice parameters were fitted simultaneously. The fit of the Ce(50)-In2O3 sample was optimized by subsequent fitting of the atom fractions, atom displacement and thermal displacement.
Transmission Electron Microscopy (TEM)
Transmission electron images were obtained using an FEI Tecnai (type Sphera) instrument operating at an acceleration voltage of 200 kV and an FEI cryoTITAN instrument operating at an acceleration voltage of 300 kV. Catalyst particles were dispersed in ethanol via ultrasonication and deposited on a holey Cu support grid. The particle size and lattice constants of the catalysts were obtained using the software ImageJ.
Scanning Transmission Electron Microscopy Energy-Dispersive X-ray Spectroscopy (STEM-EDX)
The distribution of In and Ce in the In2O3–Ce samples was studied using STEM-EDX. Measurements were carried out on a FEI cubed Cs-corrected Titan operating at 300 kV. In2O3–Ce samples were dispersed in ethanol via ultrasonication and deposited on a Cu support grid with a holey carbon film. Elemental analysis was done with an Oxford Instruments EDX detector X-MaxN 100TLE.
Electrochemical Experiments
Electrocatalytic CO2 Reduction
In flow-through mode, CO2 electroreduction was performed in a flow cell with an electrode with a geometric surface area of 1 cm2 (Micro Flow Cell, ElectroCell). A Nafion proton exchange membrane (N324, Ion Power) separated the catholyte and anolyte chambers. The Nafion membrane was pretreated in a 10 vol % H2O2 solution (diluted from 33 vol % solution, VWR Chemicals) at 80 °C for 1 h and subsequently in a 3 M H2SO4 (≥95%, Merck) solution (80 °C, 1 h). An Autolab 302N potentiostat was used for electrochemical analysis for cyclic voltammetry and chrono-potentiometry measurements. A three-electrode system was used with a Pt mesh as a counter electrode and a leakless Ag/AgCl electrode (1.6 mm, EDAQ, measured at 0.37 V vs SHE at pH 1) as the reference. The as-prepared GDEs were used as working electrodes. Potentials are specified against the Ag/AgCl reference electrode. As catholyte, 0.5 M KHCO3 solution was prepared by dissolving high purity KHCO3 (analysis grade, Merck) in ultrapure water (18.2 MΩ·cm). As anolyte, 0.5 M H2SO4 solution was used by diluting H2SO4 (>95%, Sigma-Aldrich) in ultrapure water. The catholyte solution was degassed by N2 and saturated with CO2 before use. The backside of the GDE was supplied with a gaseous flow of 10 mL/min CO2. The catholyte and anolyte liquid flows were set at 50 mL/min. Cyclic voltammetry and galvanostatic measurements were performed for 1 h at a current density of 200 mA/cm2 during and after which the catholyte was analyzed for products. Faradaic efficiencies toward formate were calculated from the ratio of charge that is needed to produce the obtained formate over the total amount of charge that was consumed at the cathode:
with [FA] being the concentration of formate in the cathode compartment, V the catholyte volume, n the number of consumed electrons (two) per formate molecule, F Faraday’s constant, J the current density, and t time. The experiments were repeated at least twice with a fresh GDE with the same loading to estimate the experimental error. The current densities are reported based on the exposed geometrical surface area of the GDE. This study uses the Faradaic efficiency and current density as major indicators for the catalyst performance and is used to analyze and optimize the cathodic catalyst. As pointed out by, e.g., the group of Seger and co-workers,34,35 for industrial applications, the system also needs to be optimized for CO2 conversion efficiency, which is considered outside the scope of this work.
High-Performance Liquid Chromatography (HPLC)
Dissolved reduction products were analyzed by HPLC. A Shimadzu HPLC containing a Polar C18 column (Luna Omega 3 μm, 150 × 3.0 mm) was used to determine the formic acid concentration. A potassium phosphate buffer (pH 2.0) was used as eluent, which was prepared by dissolving 1.4150 g KH2PO4 (≥99%, Sigma-Aldrich) and 1.6854 g H3PO4 solution (85%, Merck) in 1.0 L ultrapure water. The column oven temperature was set at 30 °C and the UV–vis detector cell temperature at 40 °C. Samples were taken from the catholyte by diluting 100 μL of electrolyte to 1.0 mL with 900 μL 0.1 M H3PO4 solution (1:10) to convert bicarbonate to CO2. An injection volume of 10 μL and a total eluent flow of 500 μL/min was used. The retention time of the formic acid peak was about 2 min. Reference solutions from 263.434 mM down to 5.268 mM formic acid (≥98%, Sigma-Aldrich) were used to obtain a calibration curve for HPLC analysis. Two stock formic acid solutions (263.434 mM and 105.60 mM) were prepared by diluting 1.0 mL formic acid to 100 and 250 mL in 0.5 M KHCO3 in ultrapure water and were further diluted for reference solutions. The calibration solutions were also prepared by 1:10 dilution in 0.1 M H3PO4 (85%, Merck) and analyzed in triplicate. Peak integration was performed using the ICIS algorithm included in the Shimadzu software package.
1H Nuclear Magnetic Resonance Spectroscopy (1H NMR)
Dissolved reaction products were analyzed by 1H NMR spectroscopy. NMR spectra were recorded using a 400 MHz Bruker spectrometer. An aliquot of 450 μL was taken directly from the catholyte, followed by the addition of 50 μL of D2O (99.9%, Sigma-Aldrich) containing 10 mM DMSO (>99.9%, Biosolve) and 50 mM phenol (≥99%, Sigma-Aldrich) as internal standards. Standard solutions for HPLC calibration were used to verify the DMSO and phenol concentrations. The NMR signal due to protons of water was suppressed by a solvent presaturation sequence. The signal-to-noise ratio was improved by averaging 48 scans with a 16 s delay time. The resulting spectra were calibrated with reference to the DMSO peak position, set at 2.600 ppm in accordance with Kuhl et al.36 Then, the peak belonging to the carbon bonded proton in formic acid was observed at 8.33 ppm.
Gas Chromatography
Gaseous products were analyzed online using a TRACE 1300 gas chromatograph (Thermo Fisher). The permanent gases (H2, CO, CO2) and the hydrocarbons (methane, ethylene) were analyzed on separate channels. A Hayesep Q precolumn and a Shin-Carbon ST column with TCD were used for permanent gas analysis. An Al2O3/KCl column with FID was used to separate the light hydrocarbons.
Results and Discussion
Catalyst Characterization
In2O3 nanoparticles and In2O3 nanoparticles doped with Zr, Ce, Pd, Ni, and Co were obtained by FSP. Their physicochemical properties are summarized in Table 1.
The Zr, Pd, Ni and Co contents were targeted at 5 wt % with respect to the total weight of the particles, while the content of the Ce dopant was aimed at 10 wt %. The atomic and weight loadings of the promoters are given in Table 1. The average size of the In2O3 nanoparticles determined by TEM was 6.2 ± 1.4 nm (Figure S1). The size of the doped In2O3 nanoparticles was close to that of pure In2O3 with the average particle size falling in the range of 5.8–7.3 nm with a nearly dopant-independent size distribution. This shows that doping did not strongly affect the particle size (Figure S1). Both In2O3 and doped In2O3 particles are made up of cubic In2O3 as follows from the XRD patterns in Figure S2. The dopants are highly dispersed, as seen from the absence of other diffraction lines. This suggests that the promoters are doped into the In2O3 lattice, albeit they can also be present as very small oxide particles.37 The shift of the In2O3 diffraction lines for the Ce–In2O3 sample toward lower angles indicates lattice expansion by incorporating Ce ions in the In2O3 crystal structure. The radii of Ce4+ and Ce3+ ions of respectively 101 and 115 pm are larger than the radius of 81 pm of In3+. The cations of the other dopants in their most likely oxidation states are too similar to that of In3+ to judge their incorporation in the In2O3 lattice from XRD.25,38 The average crystal sizes of the (doped) In2O3 nanoparticles calculated by the Scherrer equation are also listed in Table 1. The crystallite sizes of the In2O3 particles doped with Pd, Ni and Co are very similar to that of In2O3 (∼9 nm), while those for the Zr- and Ce-doped In2O3 particles are slightly smaller (∼8 nm).
XPS was used to analyze the surface composition of the samples. The surface concentration of the dopants is determined from the core level XPS spectra of In and the dopants. The results are listed in Table 1. The surfaces of Pd- and Ni-doped In2O3 are slightly enriched in dopant compared to their nominal contents. While the Zr-doped In2O3 nanoparticles contain slightly less Zr at the surface than the nominal content, the bulk and surface dopant contents for Ce- and Co-doped In2O3 are nearly the same. Overall, the minor differences observed point to a high dispersion of the dopant with some indications of dopant enrichment in the surface for Ni and Pd. For a similarly prepared Ni-doped In2O3 catalyst used in CO2 hydrogenation, it was found that Ni is highly dispersed as Ni cations in the bulk and at the surface of In2O3.39 The group of Pérez-Ramirez also used FSP to prepare a range of metal-doped In2O3 nanoparticles and found that most metal dopants were evenly distributed in the bulk and surface of In2O3.25Figure 1 shows the In 3d XPS spectra of the In2O3 and doped In2O3 samples. The spectra consist of two main features representing the In 3d5/2 and In 3d3/2 states. Two contributions are included to fit these In spectra. The main peak at an In 3d5/2 binding energy of 444.4 eV is attributed to In2O3,40 The shoulder, with a higher binding energy of 445.4 eV, is due to In-hydroxide or defects in In2O3 (Figure S3).40 Doping with Ce and Zr results in a small shift (0.2 eV) of the binding energy of the In 3d5/2 peaks. The main In 3d5/2 binding energy shifts from 444.4 to 444.6 eV, as was also observed for Zr doping by Pinheiro Araújo and co-workers.41,42 This shift indicates a higher effective charge on the In ions, which can be caused by transfer of electrons from In to Ce and Zr.43 The contribution of In(OH)3/In2O3-defects does not change upon Zr doping and decreases for Ce. An opposite shift in the binding energy is observed when In2O3 is doped with Ni and Co, resulting in a shift of the main In 3d5/2 peak to respectively 444.2 and 443.8 eV. The Co-doped In2O3 sample contains a higher contribution of In(OH)3/In2O3-defects of 36% as compared to the contribution of 13% for In2O3. This, together with the relatively large binding energy shift of In and the homogeneous distribution of Co in the In2O3 particles, indicates the well-mixed nature of the Co–In-oxides as observed previously for FSP-prepared Co-doped In2O3.25 There are no significant changes in the In 3d spectra upon introducing Pd in In2O3. The same trends in binding energies are observed when comparing the O 1s spectra (Figure S4). The O 1s binding energy of lattice oxygen in In2O3 is observed at 529.9 eV and shifts to 530.1 eV upon doping with Ce and Zr, while a slight shift to lower energies of 529.7 and 529.5 eV is observed for the Ni- and Co-doped In2O3, respectively.
Figure 1.

XPS spectra of the In core-line region of the FSP-synthesized doped In2O3 catalysts. All spectra were energy corrected by the U‴ component at 916.7 eV of cerium. The resulting C 1s binding energy (measured at 285.1 eV) was used to energy correct spectra of samples that contain no cerium.
The XPS spectra of the dopants were deconvoluted, as shown in Figure S5. The Ce content in the In2O3 particles is 9.7 at%, close to the nominal Ce content (Table 1). Deconvolution of the Ce 3d spectrum of the Ce-doped In2O3 using contributions of Ce3+ and Ce4+ reveals a substantial amount of 24% Ce3+ (Figure S5a).37,44 The existence of Ce in the +3 oxidation state suggests the presence of oxygen defects.45 Ce3+ might be included in the lattice of In2O3 as supported by the shift of the XRD diffraction lines in Figure S2.46,47 Ce4+ could also substitute In3+ in the lattice of In2O3,46 but the presence of a significant amount of Ce4+ can most likely be attributed to the presence of small CeO2 particles, which can also generate Ce3+.45 The Co 2p3/2 region was fitted using a model from the literature (Figure S5d).48,49 The satellite feature at 786 eV indicates the predominant presence of CoO and Co(OH)2 and, in line with this, the Co 2p3/2 region could be fitted by contributions due to Co2+ at 782 and 780 eV. A minor feature at a lower binding energy of 779.3 eV can be attributed to fully oxidized Co3O4.48 These results are in line with previous reports where Co forms small CoOx clusters and dopants in FSP-synthesized In2O3.25 The Ni 2p3/2 core-line region spectrum contains a main peak at 855.5 eV and a broad satellite feature at 861 eV (Figure S5c). A small feature at 854 eV indicates the minor presence of NiO.39 The main peak at 855.5 eV has been attributed to Ni3+ before,50 but this assignment is not unequivocal. Based on reference spectra, it could also be assigned to Ni(OH)2,50,51 but a more likely explanation is that it represents small NiO clusters in strong interaction with In2O3.39 The Pd 3d core-line region spectrum reveals a large variety of Pd species. Besides the presence of PdO and a feature assigned to oxygen-deficient PdO, some metallic Pd is also present (Figure S5e).52−54 Overall, XPS indicates that the dopants cause minor (Ce–In2O3) to significant (Co–In2O3) shifts in the In 3d binding energy, indicative of their introduction in the In2O3 lattice. Nevertheless, it is also clear that part of the dopants are present as separate oxide phases. Regarding doping, Zr and Ce cause a slight increase of the In 3d binding energy for In2O3 of 0.2 eV, reflecting a slightly higher positive charge of In3+.41 Doping with Ni and Co results in an opposite shift toward lower binding energies.
CO2 Electroreduction
The GDEs containing the In2O3-based electrocatalysts, carbon and PTFE were evaluated for their catalytic performance in the CO2ER in a flow cell. The measurements were carried out at (geometrical) current densities of 100, 150, and 200 mA/cm2 to compare the catalyst at industrially relevant conditions. In a previous study, the electrode configuration employed here was optimized to avoid mass transport limitations and ensure sufficient catalytic surface area.55 We earlier showed that, above a catalyst loading of 0.17 mg/cm2, a current density of 200 mA/cm2 can be obtained without affecting the Faradaic efficiency toward formate (FEformate). Here, using an electrode with a catalyst loading of 0.5 mg/cm2, we could reach a current density of up to 300 mA/cm2 while maintaining a constant FEformate (Figure S7). This indicates that CO2 transport is not limiting the FEformate at the employed current densities. The main products observed here were formate, CO, H2, and hydrocarbons. The FE of hydrocarbons, mainly CH4, was always less than 1%. Figure 2 shows the FE toward these products as a function of the current density. Figure S6 shows the potentials required to maintain these current densities. At current densities of 100 and 150 mA/cm2, the FEformate reaches ∼86% for In2O3 and the Zr- and Ce-doped In2O3. For Pd- and Ni-doped In2O3, the FEformate is slightly lower, namely at 79% and 74%, respectively, at these current densities. The FEformate for Co-doped In2O3 is very low at 37% due to the much higher FE to H2. Increasing the current density to 200 mA/cm2 results in a minor but significant difference in FEformate between Zr- and Ce-doped In2O3 (85 and 86%, respectively) compared to In2O3 (81%). The presence of Pd shows, at all current densities, the highest FE to CO, which is most likely due to the formation of metallic Pd or Pd-hydrides, which are active in CO2 reduction to CO instead of formate.56,57 The data show a trend of increasing FE toward H2 and CO when a lower potential is applied to maintain a given current density (Figure S6). This can be attributed to a lower overpotential of the competing HER and CO2 to CO reduction reaction for the samples that contain Pd, Ni, and Co.
Figure 2.

Faradaic efficiency as a function of current density on doped In2O3 catalysts after 1 h CO2ER in 0.5 M KHCO3. Catalysts nanoparticles are deposited on a GDE (0.30 ± 0.06 mg/cm2). Experiments were done in triplicate (Note: the larger deviation from 100% in the total Faradaic balance for the Co-doped In2O3 is caused by an underestimation of the hydrogen concentration in the exit gas stream due to the high quantities of hydrogen exceeding the linear region of hydrogen detection in the GC setup).
Surface Characterization of Ce- and Co-Doped In2O3
Based on the galvanostatic measurements at a current density of 200 mA/cm2, the FEformate decreases in the order Ce-doped In2O3 > Zr-doped In2O3 > In2O3 > Pd-doped In2O3 > Ni-doped In2O3 > Co-doped In2O3. This order trends with the minor shift in the binding energy of the main In3+ 3d5/2 state, suggesting that the impact of dopants on the electronic state of In cations at the surface correlates with the CO2ER to formate. Care must be taken, however, as some of the dopants can be active for electrochemical CO2 reduction, especially for the HER. Moreover, some of the compositions might reduce to the metallic form during the CO2ER. To study this aspect further, we characterized three samples in more detail by cyclic voltammetry (CV).
Figure 3 compares the CVs of In2O3 doped with Ce and Co with the one of In2O3. The CV of In2O3 contains a cathodic peak at −1.0 V vs Ag/AgCl, which corresponds to the reduction of In3+ to metallic In, and an anodic peak at −0.9 V vs Ag/AgCl due to reoxidation of metallic In to In3+.21 As such, these potentials represent the reversible character of the In3+/In0 redox couple in this sample. The oxidation peak in Co–In2O3 is shifted to a significantly higher anodic potential of −0.4 V vs Ag/AgCl, while the reduction is hardly affected. Based on the observation of the identical location of the reduction peak, and the absence of other peaks, we speculate that the CV still represents the In3+/In0 redox couple and that doping Co in In2O3 makes the In3+/In0 redox couple significantly less reversible. This is attributed to Co doping of the metallic In phase obtained upon reduction. This results in a higher barrier for oxidation of Co-doped In compared to monometallic In. We explain this by the formation of a Co–In alloy for which the In oxidation potential shifts closer to the oxidation potential of Co metal to Co2+.58 On the other hand, XPS analysis before and after CO2ER reveals a slight increase in Co-concentration from 12 to 15 at% (Figure S8d). This can indicate that Co migrates to the surface of the particle, which can explain the shift of the oxidation peak closer to that of pure Co. As such, the formation of a monolayer of Co cannot be fully excluded. Doping with Ce does not affect the oxidation and reduction potentials of In2O3.
Figure 3.

Cyclic voltammetry in 0.5 M KCHO3 saturated with CO2, on GDEs with In2O3 (0.35 mg/cm2, blue line), Ce–In2O3 (0.46 mg/cm2, orange line), and Co–In2O3 (0.27 mg/cm2, red line). Scan rate: 100 mV/s.
XPS before and after CO2ER was used to analyze possible changes in the surface composition. The electrocatalysts used for CO2ER were transferred through air to the XPS apparatus, which might lead to oxidation of the surface. Figure 4 shows the In 3d spectra for the fresh and used In2O3, Ce–In2O3, and Co–In2O3 GDEs, which were used to determine the surface composition of the samples (Table S1). The surface concentration of Ce decreased from 10.1 to 5.6 at% after 1 h CO2ER, indicating that there was some migration of In to the surface of the nanoparticles during the electrochemical reaction or dissolution of Ce from the surface. On the contrary, the surface concentration of Co increased from 12 to 15 at% (Figure S8c, d). The enrichment in Co of the surface might indicate the formation of a Co-rich alloy close to the surface during CO2ER.
Figure 4.
XPS analysis of the In 3d core-line region before and after CO2ER using a GDE with pure In2O3 (a, blue), Ce-doped In2O3 (b, orange), and Co-doped In2O3 (c, red) GDEs. After electrochemical CO2 reduction, the electrode is removed from the electrochemical flow cell and transferred through air to the XPS apparatus.
The spectra were deconvoluted to determine possible changes in the oxidation state (Figure 4). The In XPS spectra of the used samples contain an additional metallic contribution at an In 3d5/2 binding energy of 443.8 eV (Figure S8a). The In0 contribution is slightly lower (7.2 at%) for used Ce–In2O3 than for used In2O3 (10.6 at%) as shown in Table S1. The In 3d spectrum of used Co–In2O3 sample differs the most from the fresh sample among the set. The contribution of the In3+ due to In2O3 has significantly decreased, while the main feature is at 444.1 eV. Most likely, this reflects the reduction of a significant fraction of In to metallic In. The higher binding energy compared to metallic In can be due to the doping with the slightly more electronegative Co in the lattice. XRD analysis of the GDE after CO2ER hints at the formation of some metallic In (Figure S8b). The diffractogram does not provide enough resolution to conclude on the presence of In2O3 or a CoIn3 alloy, which is due to overlap of peaks from abundantly present PTFE.59
XPS indicates that the oxidation state of the In2O3 phase is influenced by the dopants during CO2ER. Ce might inhibit the reduction of the In2O3 phase as observed from the lower metal In content after CO2ER, while In2O3 reduction is promoted by Co. Metallic Co could be an active catalyst for HER.60,61 The relatively large surface contribution of Co on the surface, possibly forming a Co–In alloy, most likely contributes to the increased FE toward H2 observed in Figure 2. However, the increased reduction of In2O3 to metallic In caused by Co could also negatively impact the adsorption of the oxygen-bound formate intermediate, decreasing the FEformate.10
Ce–In Oxide Catalysts
To further investigate the effect of Ce dopant on In2O3 and its activity in CO2ER toward formate, a range of new catalysts were synthesized by FSP with Ce contents of 0, 10, 50, and 90 at%. The main physicochemical properties of the Ce–In2O3 catalysts are given in Table 2. The catalysts are denoted by their atomic Ce content, i.e., Ce(50)-In2O3 having a Ce content of roughly 50 at%.
TEM was used to determine the shape and size of the Ce–In2O3 nanoparticles, while STEM-EDX revealed the nanoscale distribution of Ce with respect to In. The TEM images and particle size distributions given in Figure 5a and 5b show that the Ce–In2O3 samples are predominantly made up of particles with a size of 6–7 nm as also observed for the other doped In2O3 catalysts. This shows that the particle size for these samples is hardly affected by the composition, with Ce-rich compositions giving nearly the same average particle size. The shape of the In2O3 particles is mostly spherical, although some cubes are also observed. An increase in the Ce content leads to the formation of octahedral particles, which is the dominant shape of CeO2 prepared by FSP.62 The TEM images in Figure 5 reveal the crystallinity of the particles. The lattice spacings as determined from the TEM images (Figure 5c and Figure S9) show a small increase in the In2O3 (222) lattice spacing from 0.29 nm for the In2O3 sample to 0.30 nm for the Ce(10)-In2O3 one. From the images of Ce(50)-In2O3, we can derive the presence of particles with lattice spacings of 0.29 and 0.30, which can be related to (222) planes of (Ce-doped) In2O3 as well as 0.31 nm, which corresponds to the (111) plane of CeO2. For Ce(90)-In2O3, the lattice spacing of 0.31 nm is most frequently observed, indicating the predominance of CeO2 in this sample. HAADF imaging in combination with EDX gives further insight into the dispersion of In and Ce in the particles (Figure 5d and 5e). Ce is well dispersed over the In2O3 particles in Ce(10)-In2O3. For the Ce(50)-In2O3 sample, different phases can be observed with smaller particles predominantly containing In surrounding larger particles rich in Ce. The Ce(90)-In2O3 appears to consist of CeO2 particles, in which In is present at high dispersion next to some regions with more clustered forms of In-oxide.
Figure 5.
(a) TEM images of the FSP synthesized In2O3 and Ce–In2O3 catalysts with corresponding size distributions (b). (c) HRTEM images and FFT showing the high (mono-) crystallinity of the nanoparticles and lattice spacing. (d–e) STEM-EDX imaging of the particles showing the high dispersion of In and Ce atoms in the mixed catalysts.
Synchrotron-based XRD (sXRD) was employed to study the phases present in the Ce–In2O3 samples in more detail (Figure 6). Qualitatively, the patterns suggest that Ce(10)-In2O3 is mainly composed of In2O3 in which Ce was doped, while Ce(50)-In2O3 and Ce(90)-In2O3 are predominantly made up of CeO2 in which In was doped. The (222) and (111) diffraction lines of respectively In2O3 and CeO2 were fitted by a Voigt function to estimate the crystallite size using the Scherrer equation. The results are listed in Table 2. The crystallite size of In2O3 of 8.6 nm determined by sXRD is in good agreement with the value of 9.2 nm determined by lab-based XRD (Table 1). The same holds for the crystallite size of Ce(10)-In2O3 determined by sXRD (8.2 nm) and XRD (7.8 nm). Based on Rietveld refinement of the sXRD patterns, there are no signs of CeO2 admixtures in the Ce(10)-In2O3 sample, indicating that possible CeO2 admixtures should either be very small or absent (Figure S12). The (222) diffraction line of pure In2O3 is located at 30.59 degrees, corresponding to a lattice spacing of 2.92 Å. A small shift to lower diffraction angles for Ce(10)-In2O3 indicates an increase in the lattice parameter. The In2O3 lattice parameter was determined by Rietveld refinement at 10.19 Å, corresponding to an increase of 0.05 Å compared to pure In2O3, which confirms the incorporation of Ce in the In2O3 lattice (Figure 6b and Figure S12). The sXRD pattern of Ce(90)-In2O3 contains a dominant (111) diffraction line representative of the CeO2 fluorite phase. The small shift to higher diffraction angle indicates inclusion of In in the CeO2 lattice. Scherrer analysis shows that the average size of the CeO2 particles is 7.1 nm. No In2O3 phase could be fitted using Rietveld refinement, indicating that possible In2O3 admixtures should either be very small or absent. The CeO2 lattice parameter was determined at 5.40 Å (Figure S12). The minor decrease (0.01 Å) compared to pure CeO2 confirms the inclusion of some In in the CeO2 lattice. The Ce(50)-In2O3 appears to consist of a mixture of CeO2, which contains more doped In than Ce(90)-In2O3, as indicated by the relatively large shift of the CeO2 diffraction lines, and Ce-doped In2O3. The presence of Ce-doped In2O3 can be deduced from the shoulder at the (220) peak of CeO2. Further Rietveld refinement confirms the presence of ∼50 wt % of both phases. The lattice parameters of the In2O3 and CeO2 phases are respectively 10.43 and 5.37 Å. The changes in lattice parameter confirm the inclusion of Ce in the In2O3 phase and In in the CeO2 phase (Figure S12). Scherrer analysis reveals that the CeO2 particles in this sample are much smaller at 4.6 nm than in the other samples. Comparing these findings to the STEM-EDX images in Figure 5e, it can be said that the Ce(50)-In2O3 consists of small 5 nm sized CeO2 particles doped with In, which support small In2O3 particles doped with Ce.
Figure 6.

(a) sXRD patterns of Ce–In2O3 catalysts synthesized by FSP. In2O3 and CeO2 phases are characterized according to PDF cards 00-044-1087 and 01-071-4199 respectively. Besides In2O3, Ce(10)-In2O3, Ce(50)-In2O3, and Ce(90)-In2O3, a reference sample of CeO2 (top) is analyzed. (b) Zoom in on the In2O3 (222) and CeO2 (111) diffraction lines showing the shifts indicative of lattice expansion and contraction by Ce- and In-dopants, respectively.
The surface composition of the Ce–In2O3 catalysts was analyzed by XPS and listed in Table 2. The surface Ce contents are 8.0, 38, and 83 at% for respectively Ce(10)-In2O3, Ce(50)-In2O3, and Ce(90)-In2O3. The slightly lower Ce contents compared to the nominal values of 11, 51.5, and 92.6 at% hint at surface enrichment of In as also found for the Ce–In2O3 sample in the initial set. Qualitatively, this is also in line with the STEM-EDX images for Ce(50)-In2O3, showing small In2O3 surrounding larger CeO2 particles (Figure 5e). The metal distribution in the other samples seems to be more homogeneous (Figure S10 and Figure S13).
The XPS spectra of the In 3d region given in Figure 7a were fitted in the same way as described above. This results in two contributions, a main feature due to In2O3 at an In 3d5/2 binding energy of 444.5 eV and a small one at a higher binding energy due to In(OH)3/In2O3-defects. Figure 7a shows the small shift in the binding energy of 0.2 eV of the main In 3d5/2 peak in Ce(10)-In2O3, as was also observed for Ce-doped In2O3 in Figure 1. The binding energy and the shift compared to In2O3 do not change significantly for the Ce(50)-In2O3 and Ce(90)-In2O3 samples. The contribution of In(OH)3/In2O3-defects increases, however, with increasing Ce content. Especially, the Ce(90)-In2O3 contains a large contribution of 45% of such states (Table 2), which can be attributed to the high dispersion of In-oxide in this sample in line with the high In dispersion observed by STEM-EDX (Figure 5e).
Figure 7.

(a) XPS analysis of the In 3d core-line region of pelletized catalyst particles of In2O3, Ce(10)-In2O3, Ce(50)-In2O3, and Ce(90)-In2O3. (b) XPS analysis of the Ce 3d core-line regions of the Ce–In catalysts. The spectra were deconvoluted into features belonging to Ce3+ and Ce4+ oxidation states in the same way as reported by Muravev et al.33 Ce3+ and Ce4+ related features are shown in blue and green, respectively. All spectra were energy corrected by the U‴ component at 916.7 eV of Ce.31 The resulting C 1s binding energy (measured at 285.3 eV) was used to energy correct the spectrum of pure In2O3.
Figure 7b shows the Ce 3d XPS spectra of these samples including the Ce3+ and Ce4+ contributions. The Ce3+ content is lowest for Ce(90)-In2O3 (16 at%), These Ce3+ ions reflect oxygen vacancies in the CeO2 lattice.45 The Ce3+ content increases to 19 at% in Ce(50)-In2O3 and 24 at% in Ce(10)-In2O3, the latter value being similar to the one for Ce-doped In2O3 in Figure S5a. The higher Ce3+ content at a lower nominal Ce content is most likely due to the smaller size of the CeO2 particles. At the lowest Ce content (highest In content), it can also be that the 3+ oxidation state is preferred for Ce, substituting In. We note that Ce2O3 occurs in the same cubic crystal structure as In2O3 with the Ia3 space group with a Ce–O bond distance of 2.4 Å (In–O bond distance is 2.2 Å), but no Ce2O3 phase was found from Rietveld refinement.45,63,64
X-ray absorption near edge spectroscopy (XANES) spectra at the In K-edge of the In2O3 and Ce–In2O3 samples are shown in Figure 8a. All XANES spectra are very similar to those of In2O3, reflecting the predominant 3+ oxidation state of In. The XANES spectra of reference In metal is plotted in Figure S15, showing the lower edge energy of metallic In. In2O3 forms a cubic crystal structure of the Ia3 space group and contains two different In3+ sites, forming (distorted) InO6 octahedra with In–O bonds around 2.2 Å.65 The extended X-ray absorption fine structures (EXAFS) in Figure 8b show an intense first In–O coordination shell. The second shell corresponds to an In–O–In coordination shell with two different bond distances between the In atoms in the cubic In2O3 crystal structure.65−68 This second shell decreases with increasing Ce content, which can indicate a decrease of the size of the In2O3 particles or the replacement of In in the second shell by Ce. A weak second shell remains for the Ce(90)-In2O3 sample. Fits of these EXAFS are given in Figure S16. The fit parameters in Table S2 reveal a decrease in the second shell ln–O-In coordination number from 11.8 ± 1.7 for In2O3 to 4.1 ± 3.0 in Ce(90)-In2O3 (Table S2). This result is qualitatively in agreement with the findings from STEM-EDX, XPS and sXRD that Ce(90)-In2O3 contains small In-oxide particles covering CeO2.
Figure 8.
(a) In K-edge XANES of for In2O3, Ce(10)-In2O3, Ce(50)-In2O3, and Ce(90)-In2O3 before CO2ER. (b) The k3 weighted FT-EXAFS spectra (In K-edge) of In2O3 and Ce–In2O3 catalysts before CO2ER.
The catalytic performance of the Ce–In2O3 samples was evaluated in the same way as discussed above. The FEformate as a function of the current density are given in Figure 9. In line with the result in Figure 2, the Ce(10)-In2O3 sample exhibits an increased FEformate compared to In2O3 at current densities of 150 and 200 mA/cm2. The maximum FEformate for this sample is 86 ± 3% at 150 mA/cm2, which compares favorably to 78 ± 3% for In2O3. The higher Ce content in Ce(50)-In2O3 results in a maximum FEformate of 83 ± 2% at a current density of 150 mA/cm2. At the highest Ce content in Ce(90)-In2O3, the FEformate decreases slightly to 75% and 74% at respective current densities of 150 and 200 mA/cm2, which is below the performance of In2O3. It should be noted that these values are obtained with a relatively low In content in the GDE (∼0.05 mg In2O3/cm2). This is below the minimum necessary catalyst loading observed in our previous study with this electrode configuration.55 To determine whether CeO2 plays a synergistic role with respect to In2O3, we determined the performance of In2O3 at a loading of the GDE of 0.06 mg/cm2, which is nearly the same as the In2O3 loading used for the Ce(90)-In2O3 (∼0.05 mg/cm2). The results in Figure 9 for current densities above 100 mA/cm2 clearly show that CeO2 has a positive influence on In2O3 by the substantially higher FEformate for the Ce(90)-In2O3. The lower FEformate for the GDE with an In2O3 loading 0.06 mg/cm2 stems from the much larger contribution of the HER. The catalytic activity of CeO2 as shown in Figure S11 demonstrates that CeO2 is a poor electrocatalyst for CO2 reduction, reaching a FEformate of 17% at 100 mA/cm2. The FEformate decreases to 8% at 200 mA/cm2. HER is the main reaction here competing with formate production in addition to the formation of a small amount of CO. On the Pd-, Ni-, and Co-doped In2O3 samples, the FEformate and average applied potential decreased compared to on In2O3 (Figure S6), most likely due to a lower kinetic barrier for hydrogen evolution. The applied potential on Ce(10)-In2O3 and Ce(50)-In2O3 are respectively lower and similar compared to on In2O3 (Figure S14). Nevertheless, the higher FEformate points to a lower kinetic barrier for CO2 reduction to formate. On Ce(90)-In2O3 and CeO2, the applied potential increases, while the FEformate decreases compared to on In2O3. This is most likely, because pure CeO2 is a poor electrocatalyst for both hydrogen evolution and CO2 reduction and cannot maintain a high current density without sufficient In. To understand the changes in intrinsic catalytic activity of the Ce-doped or Ce-supported In2O3, such as the onset potential for CO2ER, potentiostatic measurements on a rotating disk electrode could give better control over the applied potential and more insight in the overpotential of the catalysts toward CO2 electroreduction.
Figure 9.

Faradaic efficiency as a function of current density on In2O3 and Ce–In2O3 catalysts after 1 h CO2ER in 0.5 M KHCO3. Catalyst nanoparticles are deposited on a GDE (0.47 ± 0.07 mg/cm2). Experiments were repeated in duplicate to obtain the error bars.
The increase in FE brought about by the Ce in Ce(10)-In2O3 could be caused by a change in the electronic structure of In2O3. The higher binding energy of the valence electrons on the In atom might stabilize the In2O3 phase. To understand the contribution of Ce to the electronic structure of In2O3, the catalysts were further analyzed using operando XAS.
Structural Evolution of Ce–In Catalysts during CO2ER
Using operando XANES at the In K-edge, the chemical state of In was characterized during cyclic voltammetry and chronoamperometry on a modified GDE during CO2 reduction. The temporal resolution of the XANES measurements (0.5 s/scan) was used to follow the spectral changes at the In K-edge during cyclic voltammetry. The potential on the electrode was cycled between −0.4 V and −2.0 V vs Ag/AgCl for 3 CVs before CO2 reduction was followed at constant potentials of −1.5 and −2.0 V vs Ag/AgCl. Figure S17 shows the corresponding CVs for the In2O3 and Ce–In2O3 samples. During the first cathodic scan for In2O3 (Figure S17a), the current density increases from the onset potential of −1.1 V vs Ag/AgCl onward until the most negative applied potential of −2.0 V vs Ag/AgCl. Linear combination fitting (LCF) reveals the changes in the In oxidation state during CV cycling (Figure 10a). At −1.1 V vs Ag/AgCl, the increase in current coincides with rapid reduction of In2O3 to metallic In, obtaining almost 80 at% metallic In after completion of the cathodic cycle. XANES spectra at −1.0 V, −1.5 V, −2.0 V vs Ag/AgCl and EXAFS spectra during the first cathodic cycle show that In2O3 reduction continues during the cathodic cycle until the potential and current return to the nonfaradaic region in the CV (Figure S18). During the anodic cycle, a minor reoxidation feature of metallic In starting at −0.9 V vs Ag/AgCl can be observed, which results in the presence of ca. 35 at% In2O3. During the second cycle, the maximum cathodic current density is lower than in the first cycle, and two cathodic peaks are observed. The first cathodic peak starting at −0.9 V vs Ag/AgCl coincides with the reduction of reoxidized In2O3, yielding again a metallic In contribution of 80 at%. The second reduction feature starts around −1.4 V vs Ag/AgCl but does not lead to a significant change in the In speciation according to XANES. Most likely, this feature represents the reduction of CO2. In the third cycle, only minor reoxidation occurs. Reduction during the third cathodic scan results in a nearly constant In speciation of 90% metallic In. Subsequent CO2 reduction at constant potentials of −1.5 and −2.0 V vs Ag/AgCl does not further change the In speciation (Figure 10c). Contrary to observations in our previous work using in situ Raman spectroscopy,55 a small amount of In2O3 remains present up to −2.0 V vs Ag/AgCl. The presence of residual In2O3 may have a role in the CO2 reduction reaction, as it was argued to be a more active phase for CO2 reduction to formate.17 A remaining peak of the In–O shell in the EXAFS confirms the presence of In–O and/or In–OH (Figure S19b). Fitting of the first In–O shell shows that the In–O coordination number decreased to 0.8 ± 0.5 and the In–O bond distance decreased from 2.2 to 2.0 Å. All this suggests a predominantly metallic In phase with some residual In–O bonds.
Figure 10.
Potential resolved evolution of In speciation determined by linear combination analysis of XAS spectra for In2O3 (a) and Ce(10)-In2O3 (b) during cyclic voltammetry in 0.5 M KHCO3 at a scan rate of 10 mV/s. The potential is displayed on the X-axis in chronological order, sweeping back and forth between −0.4 V and −2 V vs Ag/AgCl. The green scattered plot gives the recorded current density, reaching a maximum of −2.0 V vs Ag/AgCl at every cycle. (c, d) Time-resolved evolution of In speciation determined by linear combination analysis of XAS spectra for In2O3 (c) and Ce(10)-In2O3 (d) during chrono-amperometry at −1.5 V and −2.0 V vs Ag/AgCl after 3 CVs.
The reduction of In2O3 is slower in the presence of Ce as can be judged from the CV-XANES experiment for Ce(10)-In2O3. After the first CV, the metallic In content is only 30 at% (Figure 10b). During the subsequent 2 cycles, more In is reduced, attaining a metallic In content of 50 at%, significantly less than the nearly full reduction (90 at%) obtained for In2O3. During chronoamperometry at −1.5 V and −2.0 V vs Ag/AgCl, the reduction of In2O3 to metallic In continues, reaching 60% metallic In at −2.0 vs Ag/AgCl after 20 min (Figure 10d).
At a higher Ce content of 50 at%, the reduction of In2O3 to metallic In is strongly suppressed (Figure 11a). The large cathodic current observed for the Ce(50)-In2O3 sample during the first CV (Figure S17c) could be due to the reduction of CO2, CeO2,100,101 or any contamination in the experiment. No further reduction was observed during chronoamperometry at −1.5 V vs Ag/AgCl. Nevertheless, at a constant potential of −2.0 V vs Ag/AgCl, a slight reduction of In2O3 to metallic In was seen (Figure 11c). Suppression of In2O3 reduction by Ce is also evident for the Ce(90)-In2O3 sample, despite the lower signal-to-noise ratio of the XANES spectra (Figure 11b and Figure S20). The low quality of the spectra due to the low In content hampered meaningful LCF. Reoxidation of In was followed at open circuit potential (OCP) after the CO2ER in all experiments (Figure S21). A slight reoxidation of In to In2O3 was observed for all catalysts. The In2O3 fraction was found to increase 2% for In2O3 and 8% for Ce(10)-In2O3 after 5 min.
Figure 11.
Potential and time-resolved evolution of In speciation determined by linear combination analysis of XAS spectra for Ce(50)-In2O3 (a) and Ce(90)-In2O3 (b) during cyclic voltammetry in 0.5 M KHCO3 at a scan rate of 10 mV/s. (c) Ce(50)-In2O3 catalyst during chrono-amperometry at −1.5 V and −2.0 V vs Ag/AgCl after 3 CVs.
The suppression of In2O3 reduction correlates well with the observed decreased efficiency toward H2 and increased efficiency toward CO2 electroreduction. Potentiostatic analysis is needed to provide more information for the change in onset potential toward H2O reduction and CO2 reduction. Besides a high current density, a stable catalyst is also required for industrial applicability. This study is limited to measurements of 1 h to identify the effect of In2O3 promotion. If Ce leaches out from the catalyst, as might be suggested by XPS analysis, stabilization of the Ce–In mixed phase could be explored by adding a structural promotor, as was demonstrated, for example, for In-sulfides by the group of Gao.69
Conclusions
In2O3 nanoparticles were doped with Pd, Co, Ni, Zr, and Ce using flame spray pyrolysis. XRD and XPS show a high dispersion of the dopants in In2O3 in addition to some segregated dopant oxide phases on In2O3. Galvanostatic measurements at a current density of 200 mA/cm2 show a decreasing FEformate in the order Ce-doped In2O3 > Zr-doped In2O3 > In2O3 > Pd-doped In2O3 > Ni-doped In2O3 > Co-doped In2O3. XPS analysis shows that an increasing FEformate goes along with increasing binding energy of the In atoms, suggesting that the dopants can slightly modify the surface properties of the In2O3. Overall, the highest FEformate is obtained with Ce-doped In2O3 (86%), which compared favorably with the FEformate of 81% for In2O3. The lowest FEformate of 37% is observed at the other extreme for Co-doped In2O3. Further characterization indicates stabilization of a metallic Co–In alloy in the latter catalyst, which can explain the significant contribution of the HER. Overall, only Ce and Zr doping of In2O3 improve FEformate. The Ce content of Ce-doped In2O3 nanoparticles was then varied at 10, 50, and 90 at% by FSP. The resulting materials are typically In2O3 with Ce dopants and CeO2 clusters at low Ce content, while CeO2 with In dopants and In2O3 clusters make up the catalyst at Ce contents of 50 and 90 at%. Compared to In2O3, FEformate increases for samples that contain 10 and 50 at% Ce and decreases slightly at 90 at% Ce. The highest FEformate of 86 ± 3% is obtained for Ce(10)-In2O3 at a current density of 150 mA/cm2, significantly higher than the value of 78 ± 3% for In2O3. In situ XAS analysis shows that almost all In2O3 reduces to metallic In during cyclic voltammetry and CO2ER at −2.0 V vs Ag/AgCl. At a Ce content of 10 at%, the degree of In reduction is much lower at 60%, while a further increase to 50 and 90 at% almost completely suppresses In2O3 reduction. The improved FEformate at a low dopant level is attributed to the stabilization of In2O3, which presumably has a lower activity in the competing HER reaction than metallic In. A too-high Ce content decreases the FEformate due to the formation of CeO2, which is a poor catalyst for the CO2ER to formate.
Acknowledgments
This work was conducted under the framework of the C2FUEL project. The project has received funding from the European Union’s Horizon 2020 research and innovation program under grant agreement No 838014. Mengyue Wu (TU Delft) is acknowledged for the HRTEM and STEM-EDX measurements of the mixed Ce–In samples. The authors acknowledge SOLEIL for provision of synchrotron radiation facilities under proposal number 20220746 and thank Stephanie Belin and Laurent Barthe for their assistance using the ROCK beamline. The authors acknowledge ESRF for provision of synchrotron radiation facilities under proposal number CH-6570 and thank Marta Mirolo for her assistance using the ID31 beamline. Thijs Moerkens is acknowledged for support with ICP-OES analysis.
Supporting Information Available
The Supporting Information is available free of charge at https://pubs.acs.org/doi/10.1021/acscatal.4c02619.
Additional tables and figures, containing experimental data, material characterization, and images referred to in this article (DOCX)
Author Contributions
Tim Wissink: Conceptualization, Investigation, Validation, Visualization, Writing. Floriane A. Rollier: XAS and WAXS investigation. Valerii Muravev: XAS investigation, Review and editing. Jason M.J.J. Heinrichs and Rim C.J. v.d. Poll: TEM imaging. Dimitra Anastasiadou and Nikolai A. Kosinov: XAS investigation. Jiadong Zhu: Synthesis In2O3 particles. Marta C. Figueiredo and Emiel J.M. Hensen: Conceptualization, Writing, Review and editing.
The authors declare no competing financial interest.
Supplementary Material
References
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