Open Access Article
Sanaz
Soodi‡
a,
Eleonora
Calì‡
b,
Shailza
Saini‡
a,
William S.
Skinner
c,
Alex Martinez
Martin
a,
Gwilherm
Kerherve
c,
Marco Pietro
Mezzapesa
b,
Samir
Bensaid
b,
David J.
Payne
cd,
Melis S.
Duyar
a and
Kalliopi
Kousi
*a
aSchool of Chemistry and Chemical Engineering, University of Surrey, Guildford, GU2 7XH, UK. E-mail: k.kousi@surrey.ac.uk
bDepartment of Applied Science and Technology, Politecnico di Torino, Corso Duca degli Abruzzi, 24, Turin 10129, Italy
cDepartment of Materials, Imperial College London, Exhibition Road, London SW7 2AZ, UK
dNEOM Education, Research, and Innovation Foundation, Al Khuraybah, Tabuk 49643-9136, Saudi Arabia
First published on 17th October 2024
An intimate Cu–ZnO interface that allows for the conversion of CO2 to methanol even at atmospheric pressures was produced using the exsolution method. Detailed characterization and operando IR spectroscopy were employed to deconvolute the materials' properties that allow for this to happen.
Industrially, methanol is currently produced at relatively high temperatures and pressures (200–300 °C, 50–100 bar) over a Cu/Zn/Al2O3 catalyst using syngas produced through the steam reformation of natural gas.6 CO2 hydrogenation to methanol has large-scale application prospects using existing infrastructure and while the conventional industrial methanol process uses syngas that contains CO2, the majority of the carbon feedstock consists of CO.7 There are a lot of catalysts that have been studied with various compositions, presenting a range of active metal sites such as Cu, Ni and Pt interfaced with oxides of Ga, In or Zn.8–13 Although scale up of a CO2 hydrogenation process has been carried out using these industrial Cu/Zn/Al2O3 catalysts,14 switching from a CO to CO2 feed presents major kinetic and stability challenges for the materials used.15 Specifically, due to the production of formate as intermediate of CO2 hydrogenation, Cu catalysts demonstrate a “poisoning” effect from high formate coverages.16,17 High surface coverages of water which occur during CO2 hydrogenation also lead to deactivation of Cu catalysts.18 To improve kinetics of CO2 hydrogenation, catalyst synthesis strategies adopting weakening the binding energy of the formate19 intermediate on the surface or promoting its conversion to methanol can be adopted. Various active sites have been reported for hydrogenation of CO2 including metallic Cu, oxidized Cu, Zn decorated Cu, and isolated Cu–Zn interfaces14,20–26 while for the commercial catalyst, there is not a consensus regarding the active interface, and both CuZn bimetallic sites27,28 and ZnO/Cu29 interfaces have been proposed as active sites. Creating highly active Cu–Zn interfaces that remain stable under CO2 hydrogenation conditions (i.e. rapid generation of water) and can overcome limitations of Cu–Zn catalysts for CO2 hydrogenation, are needed to make this process economically favourable.
Exsolution has attracted a lot of interest the last few years as a method to produce stable and highly active catalysts.30,31 As a disassembly method where nanoparticles are born from within the material, exsolution provides us the opportunity to create systems where the active sites (nanoparticles) have increased interactions with their supports as they are crystallographically aligned with and partly embedded in them.32 This leads to materials that possess high stability and increased activity as compared to their traditionally prepared analogues and there have already even been some efforts to exsolve copper from different matrixes for different applications.33–35
Herein, for the first time, we take advantage of the unique features of the exsolution method to create an intimate relationship between exsolved copper particles and ultra-high dispersed ZnO. We designed a material capable of exsolving Cu surrounded by a pool of Zn and create a powerful interface that allows us to produce methanol from CO2 at even atmospheric pressures.
The perovskite was originally synthesised with a solid-state method to ensure control over stoichiometry and was sintered at 1000 °C for 12 h. Fig. 1b demonstrates the microstructure of the as-synthesised catalyst that appears to have a small grain size, a result of the low sintering temperature. The material was indeed of high purity as indicated by X-ray diffraction and Rietveld refinement (Fig. 1c and d) seemingly adopting an orthorhombic crystal structure. The Cu and Zn dopants seem to have been fully incorporated in the structure apparent when compared to the undoped sample (Fig. S1a†) (La0.4Ca0.4TiO3).
After a 10 h reduction at 500 °C, the microstructure of the catalyst remains intact as seen in Fig. 2a, keeping its grain size. X-ray diffraction showed that the sample retained overall its crystallographic properties (Fig. 2b). Two extra peaks appear with the main one at 43.2° (Fig. 2c) and are assigned to metallic Cu particles. Using the Scherrer equation (Fig. S1b†) but also Scanning and Transmission electron microscopies we identify that the metallic copper phase did indeed exsolve in the form of hundreds (∼25
000 particles per μm2) of small ∼2–6 nm sized particles (Fig. 2d–f and S2†). We did not pinpoint the presence of any other phase exsolving with any of the analyses conducted, hence we believe that we have created a sample where metallic Cu particles sit within a pool of atomically dispersed Zn ions. This is expected to produce a highly intimate interface between the two phases leading to the production of a highly active new catalyst. The overall calculated amount of Cu exsolved41 seems to be approximately 10% (∼0.32 wt%) (see calculations in ESI†) of the originally doped copper. This value was further corroborated by the refinement of the XRD pattern of the exsolved catalyst. Rietveld refinement showed a 0.3% metallic Cu with high accuracy (Rwp = 5.18) (Fig. S1c†).
Nevertheless, the newly prepared samples were tested for their activity and selectivity to methanol in the CO2 hydrogenation reaction at ambient pressure (Fig. 3a and b) at the 200–350 °C temperature range. Our results show that the newly designed material is capable of converting CO2 to methanol starting at 200 °C. Methanol production keeps increasing throughout the temperature range tested as can be seen in Fig. 3e which is interesting as published literature and theory (Fig. S3†) suggests that methanol production would peak at ∼250–280 °C and then decrease while CO would increase with temperature.42,43 In contrast, here we see an increase in CO production, accompanied by an increase in methanol as well. The TOF values, i.e., the no. of CO2 molecules hydrogenated per Cu site per sec (s−1) increased significantly from 0.4 × 10−3 at 200 °C to 3.2 × 10−3 at 350 °C (Fig. 3c). This value is ∼4 times higher than reported value 0.4 × 10−3 (measured at high p, 3 MPa) for Cu–Zn–Zr catalysts with copper ∼45 wt%.44 This suggests that our catalyst design is of great interest potentially due to the strained nature of the copper sites or the enhanced interaction of Cu with the support i.e. ZnO phase.44 And while the main product is indeed CO, methanol formation at atmospheric pressure is remarkable. Almost the entirety of the published literature that reports methanol production from CO2 hydrogenation, is mainly under high-pressures (∼30–50 bars).45 In addition,46 the apparent activation energy (Ea) of CO2 hydrogenation was also determined (Fig. 3d) and compared to Ea values reported for other catalysts (from 65–86 kJ mol−1) in the literature17,43 (typically measured at high pressure, 2 MPa) (see Table 1). The Ea for our material was found to be ∼36 kJ mol−1, which is significantly lower than the Ea values reported for other catalysts containing much higher copper contents (>50 wt%)43 and also much lower than its impregnated equivalent (104 kJ mol−1) (Fig. S8c†) (Table 1). Our results indicate that although only a small percentage of the doped copper phase was actually exsolved, indicating that there is still a lot of room for improvement in the material design to be able to drive more copper to the surface of the support, methanol production is possible at atmospheric pressure while using merely 0.3% wt of metal loading, probably owing to the unique interface of the Cu with the Zn containing support. The Cu–Zn interface is known to be crucial for achieving CO2 conversion to methanol and the production of methanol at ambient pressure is an indication of the successful interface formation upon exsolution, which complements our characterisation data. Materials characterisation after testing using SEM, TEM, XRD and XPS showed that the micro and nanostructure of the catalyst are intact (Fig. 3f–g and S7†). Specifically, comparison of the Cu 2p and Zn 2p core levels of the exsolved sample measured before catalytic testing (Fig. 4b and d) with those measured afterwards (Fig. S7†) does not indicate any change in chemical state of Cu or Zn, suggesting that the surface is stable under reaction conditions. STEM-EDX elemental maps acquired on several areas of the CuZn exsolved sample after catalytic testing showing dispersed Cu NPs of the same size as the ones found for the reduced sample while XRD showed no additional phases being generated after testing.
| Material | Activation energy (kJ mol−1)/TOF (s−1) | P (bar) | MeOH yield (mmol gcat−1 h−1) | Byproducts | Ref. |
|---|---|---|---|---|---|
a Authors of the study conducted CO2 hydrogenation at H2 : CO2 ratio different of 3 : 1.
|
|||||
| Ru/In2O3 (Ru wt% = 2) | E a not provided/1.77 | 1 | 0.12 | CO | 47 |
| Au–Ni–Ga (Ni wt% = 49) | E a not provided/3 | 10 | 1 | CO | 48 |
| Au/CeO2 (Au wt% = 1) | E a not provided/1.67 × 10−3 | 1 | 0.15 | CO, CH4 | 49 |
| Au/ZrO2 (Au wt% = 1) | E a not provided/2.3 × 10−2 | 5 | 0.66 | CO | 50 |
| NiGa alloy (ni wt% = 68) | E a not provided/4.8 × 10−4 | 10 | 0.29 | CO | 51 |
| NiO–Ga2O3/m-SiO2/Al2O3 fibers (Ni/Ga wt% = 7.5) | E a not provided/9 × 10−4 | 1 | 0.60 | CH4, CO | 52 a |
| Cu–Al/ZnO rods (Cu wt% = 15) | 45.9/4.7 × 10−4 | 1 | 1.9 | CO | 53 |
| Cu/ZnO/Al2O3–La2O3 support (Cu wt% = 54) | E a not provided/5.21 × 10−5 | 1 | 0.60 | CO | 54 |
| Cu/ZrO2 (Cu wt% = 5) | E a not provided/4.5 × 10−2 | 1 | 0.43 | CO | 55 |
| Cu/ZnO (Cu wt% = 5) | E a not provided/7.57 × 10−4 | 1 | 0.21 | CO | 56 |
| Pd–Cu–Zn (Cu wt% = 71) | E a not provided/8.5 × 10−6 | 1 | 0.29 | CO | 57 |
| Cu/Zn/Al2O3 Commercial | E a not provided/Cu wt% not provided | 1 | 0.15 | CO | 58 a |
| Cu/ZnO (Cu wt% = 15) | 75/7.8 × 10−5 | 7 | 0.11 | CO | 59 |
| CuZn–LCT (Cu wt% = 0.3) | 36/3.2 × 10−3 | 1 | 0.8 | CO | This work |
To get a deeper understanding of the relationship between copper (Cu) and the support material, X-ray photoelectron spectroscopy (XPS) was employed to measure the sample before and after exsolution. Examination of the XPS data revealed that for both the as-prepared and the exsolved sample the oxidation state and coordination environment of the A-site is essentially unchanged throughout, indicative of A-site stability throughout the redox process (the A-site core level spectra (La 3d, Ca 2p) can be found in the ESI (Fig. S4†), alongside full survey scans along with a table, Table 1, with the measured energies). The signals of La3+, Ca2+, Ti4+ and O2− are characteristic of the ones usually reported for a lanthanum calcium titanate. The La 3d and Ca 2p core levels remain essentially unchanged following reduction. Similarly, the Ti 2p core level also remains stable following reduction, aside from the slight change in the relative amounts of Ti3+ and Ti4+ (Fig. S4†), which could be linked to an increase in the concentration of oxygen vacancies upon reduction. No considerable changes are observed in the O 1s core level following reduction.
The measured Zn 2p (Fig. 4b) and Zn L3M45M45 (Fig. 4c) spectra of the as prepared and exsolved samples suggest a predominance of Zn(II). The Zn 2p3/2 peak position of the sample before and after reduction (1021.0 eV) matches closely that of ZnO in previous XPS measurements carried out by Biesinger et al.60 The Zn L3M45M45 Auger signal at 989.7 eV has the characteristic shape of Zn(II), but its position is 1.5 eV higher than has previously been observed,61 corresponding to a modified Auger parameter (2p3/2, L3M45M45) of 2011.7, which is 1.5 eV higher than that previously calculated for ZnO.60,61 This could be a result of the difference in chemical environment between Zn(II) as a dopant in the lanthanum calcium titanate perovskite lattice and Zn(II) in ZnO. The considerable similarity between the Zn XPS and Auger spectra of the as prepared and exsolved samples suggests that reduction does not have an observable effect on the chemical state of Zn. In contrast, the measured Cu 2p (Fig. 4d) and Cu L3M45M45 (Fig. 4e) spectra of the as prepared and exsolved samples suggest that all Cu(II) present in the as prepared sample is reduced to either Cu(I) or Cu metal following reduction, owing to the disappearance of the characteristic Cu(II) satellite previously observed for CuO.60,61 The Cu 2p3/2 peak position of the sample before reduction (932.8 eV) is approximately 1 eV lower than that typically measured for CuO, lying between the measured binding energies of Cu2O and CuO.60–62 Despite considerable overlap with the Ti 2s and Zn Auger peaks, it is still possible to identify the point of highest intensity in the Cu L3M45M45 Auger region, which lies at approximately 915.2 eV. This is 1.3 eV lower than that previously observed for Cu2O, and 2.6 eV lower than that observed for CuO.61 We expect that this mismatch between the measured Cu 2p3/2 and Cu L3M45M45 energies of the as-prepared sample and literature values for Cu2O and CuO could be explained by either (1) a single chemical state of Cu(II) in the lanthanum calcium titanate perovskite lattice that is distinctly different to that of both Cu2O and CuO but still presents the characteristic Cu(II) satellite, or (2) a mixture of Cu(I) and Cu(II) states that manifests as a signal lying somewhere between those observed for Cu2O and CuO. Following reduction, the disappearance of the characteristic Cu(II) satellite feature is accompanied by a 0.3 eV downwards shift in the Cu 2p3/2 peak position to 932.5 eV, and the apparent emergence of a higher kinetic energy feature in the Cu L3M45M45 Auger region at approximately 918 eV. While it is difficult to be certain of the initial chemical state of Cu in the as prepared sample, we see evidence of reduction in the exsolved sample to either Cu(I) or Cu metal.
The variation in the relative atomic percentage of the different B-site components is plotted in Fig. 4f. In comparing the as-prepared and exsolved samples, a notable decrease in Zn content and corresponding increase in Cu content are observed following reduction, while the overall Ti content remains relatively unchanged. This suggests that some form of exchange may have taken place between Cu ions in the bulk and Zn ions in the near-surface region, with Cu ions preferentially migrating towards the surface which alters their ratio after reduction. Additionally, despite the overall proportion of Ti remaining relatively unchanged, an increase in the relative proportion of Ti3+ to Ti4+ is observed following reduction. This may be linked to an increase in the concentration of positively charged oxygen vacancy defects upon reduction, which is compensated by reduction of Ti4+ to Ti3+.
:
25% CO2 reagent mixture was introduced in the gas cell over a temperature range between 180–350 °C (7 bar, 15 mL min−1) and outlet signal measured by mass spectrometry (Fig. S5†). Fig. 5 shows the main results obtained while studying the reaction in real time. To investigate intermediate species evolution, the region where formates and carbonates are expected was analysed (∼1300–1650 cm−1). Temperature increase resulted in an increase of formate species present between 1560–1600 cm−1.63 coupled with a decrease of carbonate and carboxylate species associated to TiOx-based materials (1610–1630 cm−1),64 as visible in Fig. 5a. This is in line with the already proposed CO2 hydrogenation mechanism, which suggests an initial formation of carbonates at the interface between the support and the metal,64 Cu in our case. In the literature, this was followed by reduction of the formed carbonates to formates, with consequent CO evolution, and a rapid formate decomposition to surface hydroxyl groups and CO, with production of water.64 Similarly, here, peaks associated with the presence of formates on Ti4+, Cu0, and ZnO can be seen at the 1575–1587 cm−1 region (Fig. 5b), that would suggest that indeed the mechanism involved in the CO2 hydrogenation to methanol occurs via carbonate–carboxylate consumption and formate evolution over temperature. The support does play an important role in this mechanism, as it has been proposed that CO2 can be adsorbed over titania surfaces rich in oxygen vacancies, with consequent oxidation of Ti3+ to Ti4+, causing CO2 activation through electron transfer occurring from the Ti in the reduced form to the adsorbed CO2. To quantitatively verify the CO2 adsorption properties of our system, CO2 TPD tests were carried out and the results are reported in the ESI (ESI, Table 2 and Fig. S9†). Three main peaks were identified for our system when running the test up to 500 °C, specifically at ∼139 °C, ∼232 °C and ∼350–360 °C. The first peak can be attributed to CO2 desorption from weak basic sites on titanate structures, as reported in other works,65–67 whereas the higher T peaks have been attributed to the presence of medium-strength basic sites from TiO2 and Cu/TiO2 structures reduced in the same temperature range as our system,67,68 and La-based oxides,54 respectively, with the latter also suggested to increase the adsorption capacity of titanate-based samples.65 Moreover, the identification of a small amount of Ti3+ measured through XPS on the reduced sample after exsolution seems to corroborate this hypothesis, highlighting the role of the high oxygen vacancy concentration in these novel samples for the investigated reaction. A final interesting feature is the broad band observed increasing at ∼1500 cm−1 when the sample was tested at 300 °C and 350 °C (Fig. 5c), which has been assigned to the ZnO contribution in the CO2 hydrogenation reaction. Specifically, the intensity of such broad band might be indicative of the amount of defect ionized VO+ sites during catalytic reaction, and therefore contributing to the conversion of CO2 to methanol.69 This band is already present after N2 pretreatment in our case which is not surprising, since the analysed sample had undergone extensive reduction to induce exsolution (100% H2, 500 °C, 10 h), hence also inducing formation of a high extent of VO. Under operando FTIR conditions, photoionization induced by the measurement conditions would cause partial thermal ionization of such mono-ionized oxygen vacancies to VO2+, thought responsible for the presence of this broad band. The increase in intensity observed in our case under reaction mixture at 300 and 350 °C compared to what was seen for the exsolved sample pre-testing might suggest formation of VO+ donor-type defects by CO2 during methanol synthesis. The intensity of such band has recently been related to the existence of the metal-oxide (Cu–ZnO) interaction, with higher catalytic activity connected to a higher intensity of the band. This could imply that Znδ+ sites in partially reduced ZnO under reaction conditions act as CO2 adsorption sites and reaction intermediates, while the metallic Cu sites interact with H2 atoms, highlighting the synergy of the active sites present in our exsolved system69 as also previously reported in various studies.70,71 Finally, some methane was also detected by MS during the operando test. Previous works reported production of methane on pure TiO2 (011) faceted surfaces through deoxygenation of methoxy groups from Ti cations-VO vicinity. In our case, a high concentration of oxygen vacancies is produced after nanoparticle exsolution, which could also explain the amount of methane observed.72
Post testing analysis verified the presence of nanoscale Cu nanoparticles still present on the support, surrounded by a pool of ZnO (Fig. S6†) which demonstrates the stability of the materials presented here even after submitting them to harsh reaction environments.
Footnotes |
| † Electronic supplementary information (ESI) available. See DOI: https://doi.org/10.1039/d4ta05812g |
| ‡ All authors contributed equally. |
| This journal is © The Royal Society of Chemistry 2025 |