Open Access Article
Minyoung Kima,
Meredith Zannackerb,
Yuxuan Zhanga,
Reilly Eiynckb,
Reese Resheskeb,
Donghun Leea,
Ella Mackb,
Elijah Behnkeb,
Sunghwan Lee
*a and
Sujat Sen
*b
aSchool of Engineering Technology, Purdue University, West Lafayette, IN 47907, USA. E-mail: sunghlee@purdue.edu
bDepartment of Chemistry & Biochemistry, University of Wisconsin–La Crosse, La Crosse, WI 54601, USA. E-mail: ssen@uwlax.edu
First published on 28th May 2026
The electrochemical conversion of CO2 into useful chemicals remains an active area of investigation, especially towards higher order C2 and C3 products such as ethylene, ethanol and n-propanol. Herein, we demonstrate that oxalate modified copper surfaces on porous gas-diffusion electrodes (GDEs) can be used to modify the selectivity of the electrochemical CO2 reduction reaction (eCO2RR) towards higher order chemicals using a flow-type electrochemical cell at near-neutral pH and industrially viable current densities. These multi-layer composite cathodes consisting of a Teflon substrate, coated with copper, and then modified with copper oxalate exhibit up to 79% selectivity to C2+ products at varying current densities ranging from 50 up to 250 mA cm−2, representing a shift in electrocatalytic behavior as compared to the pristine copper/Teflon cathode. The oxalate modified copper surface enables further modification with a conductive polymer such as polypyrrole, tunable to varying thicknesses, demonstrating the feasibility of performing oxidative electropolymerization on copper-based GDEs and subsequently using them for the eCO2RR. We also investigate the changes occurring in these electrodes with respect to particle/grain size, morphology and surface chemistry using SEM, XRD and XPS.
A number of studies have investigated the electrochemical conversion of CO2 to C1 products and more recent studies have increasingly focused on the generation of C2+ chemicals,11–15 given their higher intrinsic and often commercial value. Many of these chemicals are commodity chemicals produced through traditional thermochemical methods using fossil fuel-based sources. Due to the higher energy density of n-propanol (n-PrOH), it could potentially replace conventional fuels16 or at the very least serve as a superior fuel additive, e.g., replace the ethanol (EtOH) added to gasoline at the pump. Hence, it is attractive to explore whether n-PrOH could be generated efficiently through electrolysis using renewable electricity and catalysts that are stable, efficient, abundant, and cheap.
Modification of the copper surface has been investigated through a variety of means. Most notably, the studies by Kanan et al.17 demonstrated that oxide-derived copper exhibits a significant shift in product selectivity compared with the pristine equivalent. Several additional studies have investigated the role of oxide-derived copper synthesized through various thermochemical/electrochemical treatments, resulting in restructured surfaces that promote C–C coupling events leading to higher order hydrocarbons.18–23 Additional studies have also performed in-depth investigations into the mechanistic aspects of this observed shift in catalytic behavior, attributed to sub-surface oxygen20 species allowing for a special coordination environment with CO2 and its intermediates. Evidence of a rich population of undercoordinated sites Cuδ+(0 < δ < 1)24 has been more recently presented in the form of high resolution X-ray photoelectron spectroscopy (XPS) scans and Auger spectra. It has also been suggested that oxide-derived copper promotes higher local pH,25 promotes chemisorption of CO intermediates,26 and enhances grain boundaries.27 Finally, theoretical studies28 have also been proposed to explain the enhanced activity of copper metal embedded in an oxidized matrix to promote CO2 activation and CO dimerization to deeply reduced products. However, conclusive proof remains elusive that can explain how these meta-stable copper sites can remain active in spite of the thermodynamic considerations of the highly reducing environment under which the eCO2RR is typically conducted.29–32
These studies motivate further investigation into the use of Cu-based catalysts, particularly regarding the impact of surface modification and processing on gas-diffusion type electrodes that are necessary to move from lab to industrial scale implementation of this technology. Towards this goal, physical vapor deposition (PVD) techniques5,33,34 have also been used to generate layers of catalysts and their performance has often been found to differ as compared to their conventional counterparts. These include sputter coating, e-beam evaporation, and thermal evaporation methods, which are all scalable methods that would allow for rapid production of multi-layer GDE-type composite cathodes with accurate control of layer thickness.
Organic/inorganic hybrid interfaces have also been actively investigated in the past decade for the eCO2RR.35 These include a variety of organic moieties with appropriate functional groups that can interact with CO2 as well as bind to the metal catalyst through physical or chemical methods. Polypyrrole (pPy) and other conductive polymers such as polyaniline have been widely explored as candidates for such organic/inorganic hybrid interfaces across a variety of electrochemical applications given their low cost, intrinsic electrical conductivity, ion exchange mechanisms and ease of synthesis.36 Specifically discussing the use of pPy for the eCO2RR, existing studies that have used pPy/copper interfaces have done so using conventional chemical methods for synthesizing the catalyst (e.g. solvothermal) followed by casting of the catalyst onto electrodes using physical methods such as drop-casting or spray coating.37 In contrast, electrochemical polymerization of pyrrole onto a variety of metallic substrates has been demonstrated to produce uniform, highly adherent and highly controllable thin films of varying thicknesses from <50 nm to several microns, which is not the case for conventional chemical polymerization methods.
Select studies have successfully electropolymerized pyrrole onto planar metallic copper surfaces, which in principle poses a challenge given their relative thermodynamic potentials for oxidation, i.e. E° for copper oxidation (0.34 V vs. SHE) is less than E° for pyrrole (>0.5 V vs. SHE) electro-polymerization.38 In order to prevent the continuous dissolution of the copper surface during the polymerization of pyrrole, prior studies39–42 have previously reported on the passivation of the copper electrode surface using oxalate salts or oxidative scanning in the presence of oxalic acid electrolytes. The in situ created copper oxalate has a very low solubility in aqueous media (pKsp = 10.6)43 and is mechanically stable, forming a semi-stable surface on which further oxidation of pyrrole can take place. The electrochemical behavior of copper in the presence of complexing agents such as phosphoric or oxalic acids has been investigated for industrial applications, especially in chemical mechanical planarization (CMP)44 and post-CMP cleaning. However, the use of oxalate-derived copper surfaces as catalysts has not been previously explored for the eCO2RR. Collectively taken, practical eCO2RR electrolyzers must be able to operate at acidic or neutral pH45,46 and at industrially relevant current densities >100 mA cm−2. A brief summary of recent publications that employ gas-phase reactant delivery with a Teflon-based GDL, Cu-based catalysts and near-neutral pH media can be found in Table S1 (SI).
In this study, we investigate the performance of two composite catalysts, namely (a) copper oxalate derived surface and (b) polypyrrole coated copper surface. We find that the oxalate-derived catalyst is more selective for C2+ products, especially n-PrOH, produced at efficiencies as high as ∼12 ± 3% compared to the <3 ± 0.3% efficiency at the pristine copper counterpart under equivalent conditions. Using DFT studies, we attribute this enhanced catalytic behavior to the favorable reaction energetics for recently identified intermediates involved in the production of C2+ species. We demonstrate that these copper-oxalate coated GDEs can be further modified with layers of a conductive polymer like polypyrrole (pPy) that is in turn used for the eCO2RR. The use of the pPy-coated GDE shows marked suppression of oxygenate product formation in favor of hydrocarbon products such as ethylene. We provide an analysis of the changes occurring in the particle size, morphology and surface chemical composition using a combination of XPS, XRD and SEM. Furthermore, we demonstrate that the thickness of these individual layers of the composite catalyst – either the copper oxalate or polypyrrole – can be controlled carefully from a few 100 nm to several microns accurately through electrochemical means – this would enable careful control over the properties of the catalyst and custom design to a given reactor size. Finally, all tests are performed under neutral pH conditions that are favorable for industrial application, distinct from multiple recent studies that use highly alkaline electrolytes.
XPS data were acquired using a Thermo Fisher instrument equipped with a monochromatic Al Kα, argon ion sputtering beam source and a gas cluster ion bombardment source. Survey scans were conducted using a 200 eV pass energy and a 400 micron aperture averaged over 2 scans. High resolution scans were taken with a pass energy of 50 eV averaged over 10 scans for each element. The deconvolution and analysis of the high-resolution core-level binding energy spectra were performed using XPSPEAK software (Version 4.1). For the detailed analysis of the Cu L3M4,5M4,5 Auger spectra, CasaXPS software was employed to distinguish and quantify the copper oxidation states. The fitting model for the Auger spectra was constructed based on the characteristic peak parameters and line shapes reported by Biesinger,47 as well as the experimental peak signatures obtained from the copper oxalate sample synthesized in this study.
The successful deposition of a Cu layer on the GDL TE35 substrate via thermal evaporation was further corroborated by XRD analysis, as shown in Fig. 1g. The Cu/TE35 sample exhibited characteristic diffraction peaks corresponding to the cubic Cu phase (PDF 04-009-2090), specifically the (111), (200), and (220) peaks located at 2θ values of 43.33°, 50.45°, and 74.15°, respectively. These polycrystalline Cu signals were observed alongside minor peaks arising from the TE35 substrate at 2θ in 20–40°, as confirmed by the bare TE35 pattern (black line). Furthermore, the absence of any discernible peaks corresponding to copper(I) or copper(II) oxide patterns indicates that no significant oxidation of the surface occurred during or after the deposition process. To further evaluate the crystallinity of the deposited copper in the Cu/TE35 sample, the average crystallite size was calculated using the Scherrer equation based on the Cu (111) and (200) peaks (Table S2). The resulting average crystallite sizes were determined to be 18.55 nm and 11.70 nm, respectively, for Cu (111) and (200), which are significantly smaller than the particle dimensions observed in the SEM image in Fig. 1e, indicating that the thermally evaporated particles are polycrystalline in nature and composed of multiple smaller crystallite domains.
To further explore the effect of the number of cycles on morphology, thickness and grain size, copper oxalate samples were prepared at a constant scan rate but with an increasing number of cycles. These are hereon referred to as CuOA 3, CuOA 10, and CuOA 50, where the number indicates the number of cycles scanned during the deposition. Photographs of these passivated surfaces are shown in Fig. 2a–c, revealing a grey-colored surface that becomes progressively more uniform (with fewer patches) and acquires the characteristic blue color of copper oxalate powder. Notably, similar trials of oxalate deposition on commercially available planar copper substrates did not yield uniform thin films, but rather scattered and patchy deposits as seen in Fig. S4. This could be due to a lack of adhesion of the growing oxalate layer onto the planar metal surface, unlike the porous substrate, and this aspect will be explored further in future studies.
The thicknesses and surface morphologies of the copper oxalate-deposited samples were analyzed using SEM images. For the CuOA 3 sample, the cross-sectional image (Fig. S5a) exhibited a distinct bilayer structure. The relatively larger copper oxalate particles covered the copper layer, which retained the characteristic vertical texture as previously observed in the cross-sectional image of Cu/TE35 in Fig. 1d. The thickness of the copper layer in CuOA 3 was ∼1.09 µm, and the copper oxalate layer was ∼0.988 µm. The top-view SEM image of CuOA 3 (Fig. 2e) showed a surface covered with the oxalate particles; however, some areas indicated that the underlying copper layer might not have been completely covered. In contrast, the CuOA 10 sample displayed a surface completely covered with copper oxalate particles (Fig. 2f), and the characteristic vertical texture of the copper layer observed in Cu/TE35 was not apparent in its cross-sectional image (Fig. S5b). Consequently, a clear interface between the copper and copper oxalate layer was challenging to delineate precisely. The morphology of the cross-section appeared to consist of a relatively smooth top layer, presumed to be copper oxalate, and a bottom layer composed of smaller particles, presumed to be copper; the overall catalyst layer thickness was ∼1.44 µm. The CuOA 50 sample also exhibited a surface completely covered with copper oxalate particles (Fig. 2g) with an overall catalyst layer thickness of ∼2.90 µm (Fig. S5c). The particle size of the copper oxalate also varied significantly with the extent of electrodeposition, as determined from SEM images (Fig. 2i–k). The CuOA 3 sample exhibited the largest average particle size at 1.50 ± 0.40 µm (Fig. S6a). For the CuOA 10 sample (Fig. S6b), the average particle size significantly decreased to 0.459 ± 0.20 µm. The CuOA 50 sample (Fig. S6c), with the highest electrodeposition charge, showed the smallest average particle size, measured at 0.109 ± 0.35 µm.
XRD analysis was performed to investigate the crystal structure and average crystallite size of the copper oxalate deposited samples (Fig. 2m). The XRD pattern of the CuOA 3 sample exhibited new peaks matching those of copper oxalate powder (CuC2O4, PDF 04-021-4364), while also preserving the strong peaks from underlying Cu/TE35, implying that an additional copper oxalate phase layer was successfully electrodeposited onto the Cu/TE35 substrate. Notably, as the number of deposition cycles increased, the diffraction peak corresponding to crystalline Cu diminished completely for the CuOA 10 and CuOA 50 samples, while the peaks from deposited CuC2O4 clearly appeared. The diminished Cu signal in XRD indicates that the underlying Cu layer was largely consumed during the copper oxalate conversion process. In addition, since SEM primarily revealed a bulk surface morphology rather than internal microstructures, we further investigated the nanoscale crystallinity by estimating the average crystallite sizes of the Cu and electrodeposited copper oxalate phases using the Scherrer equation from two representative diffraction peaks from each phase: (111) and (200) for Cu and (110) and (120) for the copper oxalate phase (Table S2). CuOA 3 exhibited crystallite sizes of 22.60 nm and 13.54 nm for Cu (111) and (200), respectively, whereas CuOA 10 and 50 did not show any analyzable diffraction peak of Cu. For the CuC2O4 phase, CuOA 3 exhibited the smallest crystallite sizes for both (110) and (120) peaks of 23.82 nm and 10.23 nm, which then gradually increased upon repeating the electrodeposition cycles. The CuC2O4 crystallite size of (110) was 33.47 nm and 33.28 nm for 10 and 50 cycles, respectively, and that of (120) was 13.81 nm and 18.28 nm for 10 and 50 cycles. The smallest crystallite size of the copper oxalate phase in CuOA 3 suggests a higher degree of defectiveness and/or structural disorder, which could significantly affect electrocatalytic performance. Specifically, as widely reported in the eCO2RR literature,27,49 such defect-rich and structurally disordered domains can provide a higher density of catalytically accessible sites and favorably modify intermediate binding behaviors, thereby enhancing the overall catalytic activity.
After this activation or pre-reduction treatment, CO2 electrolysis experiments were conducted galvanostatically at various current densities using a flow cell for at least 1 h or longer as described in the Experimental section. Equivalent potentiostatic experiments were tried but found to be unstable, leading to I/V overloads. Fig. 3 and Fig. S12 show the faradaic efficiency (FE) or current efficiency (CE) of the electrolysis process using a pristine copper-coated TE35 GDE made using thermal evaporation (see the Experimental section). It generated a range of gaseous and liquid products detected by gas chromatography (GC) and 1H NMR respectively. Major products (>20% FE) included CO, C2H4, H2 and CH4, while all liquid products (e.g. C2H5OH, n-PrOH, and HCOOH) were found to account for less than 20% CE. Such trends are consistent with other literature reports that have used metallic copper as a catalyst in a flow cell with gas-diffusion substrates.46 Cumulatively, the CEs of all C2 and C3 products were assessed for all pristine copper (Cu), oxalate-derived CuOA 3 and polypyrrole coated copper (CuOA3_pPy2), as shown in Fig. 3. At pristine copper surfaces, the CEs for such products ranged from 30 to 70% across varying current densities, consistent with prior literature reports that have used similar electrochemical conditions.46,52,53 Table S1 provides a detailed comparison of the current work using CuOA 3 and CuOA3_pPy2 with comparable reports using copper-based catalysts in a GDE-type flow cell at near neutral pH. For the oxalate modified copper electrode (CuOA 3), the same products were generated at consistently higher CEs across all three current densities ranging from 54 to 79%. Specifically, at 50 mA cm−2, the pristine Cu produced 30% CE as compared to 54% for the oxalate modified electrode, demonstrating a significant shift in selectivity towards higher carbon products. The pPy coated cathode (CuOA3_pPy2) demonstrated efficiencies slightly higher than that of the pristine copper but significantly less than that of the oxalate-derived CuOA 3 surface. Interestingly, a comparison of the hydrocarbon products vs. the oxygenates (see Fig. 3) reveals additional trends in catalyst selectivity.54,55 At low current densities, the selectivity between oxygenates and hydrocarbons is nearly the same across the three samples, although the latter are slightly preferred on the CuOA3_pPy2 sample. This preference for hydrocarbon production over oxygenates becomes much more pronounced at higher current densities for all three samples, but is especially dominant for the CuOA3_pPy2 catalyst. At the same time, this polymer coated catalyst exhibits higher levels of H2 and CO (see Fig. S12). While such trends align with the literature,56,57 additional experimental evidence would be needed to corroborate such hypotheses. Notably, these multi-layered composite cathodes exhibited no flooding over the course of 1 h electrolysis at 50 and 100 mA cm−2. For the higher current density electrolysis conducted at 250 mA cm−2, minimal flooding was observed after the cell was taken apart, visible as liquid droplets on the back of the GDL, suggesting that electrowetting phenomena are still relevant as with carbon-based GDLs, albeit more resistant.
Finally, Fig. S13 shows the cathode potential as a function of applied current density during the galvanostatic electrolysis tests. Within the margin of error, the pristine copper and oxalate modified copper cathodes exhibited similar iR-corrected potentials across the range of applied currents. However, the CuOA3_pPy2 cathode demonstrated distinctly more negative (higher) cathode potentials, indicating an energy penalty due to the added layer. Such higher potential could also explain the observed increase in H2 and CO production at CuOA3_pPy2 surfaces (see Fig. S12). These pPy coated samples showed more reproducible results over repeated trials as well as a smaller deviation in cathode potential during the course of 1 h electrolysis (Fig. S14), suggesting possible benefits of the polymer layer for long term operation. However, such claims will need to be further studied via long term studies and will be the subject of future studies.
:
C
:
O stoichiometry of the prepared catalyst samples was further analyzed. CuOA 3 showed a distinct increase in the Cu
:
O ratio (1
:
3.77) compared to the pristine Cu/TE35 (1
:
1.88). With further deposition cycles, CuOA 10 exhibited a Cu
:
C
:
O stoichiometry of 1
:
3.05
:
4.01 that most closely matched that of theoretical anhydrous copper oxalate (CuC2O4), indicating the successful formation of the target material. However, with additional electrodeposition cycles, the CuOA 50 sample exhibited a higher proportion of oxygen with Cu
:
C
:
O as 1
:
4.24
:
4.65. This deviation suggests the potential formation of a hydrated phase (CuC2O4·nH2O), further supported by the bluish color of the sample's surface (Fig. 2c), which is characteristic of hydrated copper(II) salts. The reduced particle size in CuOA 50 (Fig. S6) further supports the idea, as smaller and more defective morphologies are likely more susceptible to hydration. After the deposition of the pPy layer, CuOA3_pPy2 showed no Cu signal detected, while a significant nitrogen signal (12.30%) emerged, demonstrating the formation of a complete and uniform polypyrrole film covering the underlying substrate. Such a contiguously coated layer implies that the pPy layer could function as a physical and chemical barrier, potentially enhancing the stability of the active catalyst during the CO2 electroreduction reaction.
The modification of the copper surface via electrodeposition was further corroborated by high-resolution XPS analysis. In the C 1s spectrum of the CuOA 3 sample (Fig. 4a), a prominent O–C
O peak emerged at 288.40 eV, alongside adventitious hydrocarbons (284.41 eV) and C–O species (286.1 eV).58,59 This spectral feature distinguishes the oxalate-modified surface from the pristine Cu/TE35 (Fig. S15a), which showed a lower carboxylate signature. The corresponding evidence regarding the oxalate-derived bonding environment was also observed in the O 1s region.58–60 While the pristine Cu/TE35 (Fig. S15b) exhibited a major Cu–O peak at 531.07 eV (accounting for 92.2% of the total area) from native oxidation under ambient conditions and a minor O–C
C peak at 531.82 eV, the CuOA 3 sample (Fig. S16a) showed a dominance of the oxalate-derived O–C
C peak, comprising 90.68% of the total area, with a minor H2O signal at 531.73 eV. Notably, in the CuOA 50 sample, the H2O signal became the dominant feature, occupying 89.79% of the peak area. This significant increase of the H2O peak confirms that excessive oxalate deposition leads to the formation of a hydrated phase, as previously inferred from its appearance (Fig. 2c) and stoichiometry (Table S3).
The chemical structure of the deposited pPy layer was also elucidated through XPS. In the C 1s spectrum of CuOA3_pPy10 (Fig. 4a), the dominant C–C peak at 284.8 eV and a new peak at 286.6 eV are attributed to the polymer backbone and C
N bonds in the pyrrolic ring, respectively, providing clear evidence of successful polymerization. Furthermore, the peak positions of C–O (286.10 eV) and O–C
O (288.40 eV) observed in CuOA 3 shifted to lower binding energies in the CuOA3_pPy10 sample. This shift implies an increase in the number of carbon atoms bonded to nitrogen, namely C–N (285.80 eV) and C
N+ (288.25 eV), which has a lower electronegativity compared to oxygen.61,62 Detailed information regarding the chemical state of the deposited pPy was obtained from the N 1s spectrum. As shown in Fig. 4b and Fig. S17, neutral pyrrolic nitrogen (NH-Py) at 399.84 eV and positively charged nitrogen species (C–N+ and C
N+ at 400.92 eV and 402.20 eV, respectively), often referred to as polarons, were both observed in the CuOA3_pPy10 sample. The presence of these species confirms that a conductive pPy overlayer was successfully deposited onto the catalyst layer.
The XPS spectra in the Cu 2p region were analyzed to understand the evolution of copper's oxidation state during the surface modification process (Fig. 4c and Table S4). The deconvoluted Cu 2p3/2 spectrum of the pristine Cu/TE35 exhibits a peak at 933.55 eV, which accounts for 51.67% of the fitted area and represents a mixture of metallic copper (Cu0) and copper(I) oxide species since distinguishing Cu0 from Cu+ is challenging based solely on the 2p spectrum due to their overlapping binding energies. Additionally, a Cu2+ peak is observed at 934.72 eV (48.33%), likely originating from a thin native oxide layer (Cu(OH)2) formed naturally on the metal surface under ambient conditions. Upon the formation of an oxalate layer in the CuOA 3 sample, a new prominent peak appeared at a higher binding energy of 936.25 eV, which occupies 64.94% of the fitted area. This peak is the characteristic signature of copper oxalate, and it shifted significantly due to the strong electron-withdrawing effect of the coordinating carboxylate ligands.58,59,63 Notably, the Cu0/+ peak shifted positively from 933.55 eV (pristine Cu/TE35) to 933.69 eV, suggesting an enrichment of Cu+ species at the surface. For the samples with thicker oxalate layers, CuOA 10 and CuOA 50 (Fig. S16b), the copper oxalate peak remained dominant; specifically, the area percentage of the oxalate species increased to 84.72% for the CuOA 50 sample, consistent with the XRD and SEM (Fig. 2) results that indicated a significant growth of the copper oxalate phase. To investigate the chemical state of copper beneath the polymer layer, the thinner CuOA3_pPy0.25 sample was examined for XPS in the Cu 2p region. The Cu 2p spectral profile closely resembles that of the CuOA 3 substrate, with the oxalate peak occupying 63.40% of the area, indicating that the chemical state of the underlying copper oxalate was well-preserved during polymerization. However, the Cu0/+ peak shifted back to 933.55 eV from 933.69 eV in CuOA 3. This negative shift suggests a potential increase in the metallic Cu0 component after the pPy deposition process.
Since quantifying the ratio of Cu0 and Cu+ species is challenging from the Cu 2p spectrum alone, the Cu L3M4,5M4,5 Auger spectra were deconvoluted to distinguish these species and perform a quantitative analysis (Fig. 4d and Table S4).58,59,63 The LMM analysis of the pristine Cu/TE35 surface confirms the presence of Cu0 (19.03%), Cu+ (40.54%), and Cu(OH)2 (40.43%) species. The detection of the Cu0 signal indicates that oxidation is limited to the uppermost few nanometers of the surface, while the underlying bulk material retains its metallic Cu state. In the CuOA 3 sample, the Cu Auger signal is dominated by the copper oxalate species (69.44%) and Cu+ (30.56%), without any metallic Cu0 signal observed. The absence of the Cu0 feature suggests that the CuOA layer is sufficiently thick to prevent the detection of the underlying copper metal, as previously confirmed by the cross-sectional SEM images (Fig. S5). Similarly, the CuOA 10 sample (Fig. S16c) exhibits a composition of CuC2O4 (63.51%) and Cu+ (36.49%), maintaining a ratio comparable to that of CuOA 3. The CuOA3_pPy0.25 sample largely reflects the composition of the CuOA 3 substrate even after the conductive polymer layer deposition, with a dominant oxalate signal (70.85%). However, a distinct metallic Cu0 signal (∼5.01%) was detected, which may be attributed to minor copper dissolution or the presence of exposed copper metal areas that were not fully covered with the initial CuOA layer during the polymerization process.
Finally, the effect of the pre-reduction treatment was examined for the pre-reduced CuOA 3 sample (oxalate-derived surface). The characteristic copper oxalate peak completely disappeared in both the Cu 2p and LMM spectra; instead, a weak Cu(OH)2 peak emerged. The Auger spectrum analysis revealed a surface composition dominated by Cu+ (76.89%) with a minor metallic Cu0 signal (5.55%). This specific Cu+-rich surface environment may be a contributing factor to the high C2+ selectivity observed in the electrochemical tests (Fig. 3 and Fig. S12).
To investigate the structural and chemical changes in the catalysts under eCO2RR operating conditions, SEM, XRD and XPS were performed on the electrodes after the CO2 reduction reaction. Fig. S18 shows the SEM images for pristine copper, CuOA 3 and CuOA3_pPy2 electrodes after undergoing electrolysis. In the case of both the Cu and CuOA 3 electrodes, some restructuring of the particles is seen in the form of larger clusters compared to both the originally deposited electrode (see Fig. 1 and 2) and the activated or pre-reduced electrode (Fig. S10). The post-electrolysis XRD patterns in Fig. 5a confirm that metallic copper is the primary crystalline phase for all catalyst samples, while copper oxalate peaks have diminished for the CuOA 3 and CuOA3_pPy2 samples. The oxalate phase was reduced and did not persist as a crystalline phase under strong reductive conditions, although localized oxidized Cu species may still remain in amorphous or non-crystalline forms. For the Cu (111) peak of all the samples, a positive shift in the 2θ angle was observed, indicating a contraction of the lattice d-spacing after electrolysis. Moreover, significant crystallite growth occurred in all the catalyst samples, which is likely due to an Ostwald ripening mechanism involving dissolution and redeposition in the electrolyte, resulting in minor XRD peaks of copper carbonate hydroxides.51,64 After the electrolysis, the average Cu (111) crystallite sizes of the Cu/TE35 and CuOA 3 samples increased from 18.55 nm and 22.60 nm to 27.44 nm and 54.64 nm, respectively, showing 18.0% and 49.78% increases in crystal sizes, respectively. In contrast, the CuOA3_pPy2 sample nearly retained its initial crystallite size (25.51 nm), which is a nominal 6.70% size increase, showing remarkable structural stability presumably due to the additional polymer layer. Considering that the crystallite growth mainly occurs via a dissolution–redeposition process, the pPy layer likely suppresses this process by acting as a physical or chemical barrier.65 Such structural stabilization of the catalysts can help maintain a large active surface area by keeping the crystallite size small. It can also be hypothesized that this mitigates changes in the local reaction microenvironment and promotes metastable copper species, which in turn leads to stable catalytic performance.
To probe the redox states of the copper-based catalysts after the eCO2RR, the Cu 2p and Cu Auger spectra were analyzed (Fig. 5b and c, Fig. S19, and Table S5). Overall, all post-electrolysis samples showed the complete disappearance of the characteristic CuC2O4 peak in both spectral regions. Instead, the surface species redistributed into metallic Cu0, Cu2O, and Cu–OH, which may have originated from copper-based carbonate hydroxides during electrolysis as confirmed in XRD analysis (Fig. 5a). The extensive formation of Cu(OH)2 is consistent with the presence of copper carbonate hydroxides, as previously identified in the post-electrolysis XRD patterns in Fig. 5a. In the Cu 2p region (Fig. 5b), the distribution of oxidation states varied significantly among the samples. For the Cu/TE35 sample, the area percentage of the Cu0/+ peak (932.47 eV) increased to 63.70% compared to the pristine state (51.67%), indicating a reduction of the surface during electrolysis. In contrast, the post-CuOA 3 sample exhibited a sharp contrast to its pre-reduced state; the proportion of Cu(OH)2 increased substantially to 67.30%, while the Cu0/+ species accounted for only 32.70%. The post-CuOA3_pPy0.25 sample showed a recovery of the Cu0/+ fraction to 59.86%, and mild surface etching further increased this proportion to 68.24%. Additional discussion of the changes occurring in the CuOA3_pPy0.25 XPS spectra before and after electrolysis is provided in section S4.
The Cu LMM Auger spectra were further deconvoluted to quantify metallic Cu and Cu+ species (Fig. 5c). For the post-Cu sample, Cu+ emerged as the dominant phase (65.25%), while the proportions of Cu0 (7.26%) and Cu(OH)2 (27.49%) decreased compared to the pre-electrolysis sample. Conversely, the post-CuOA 3 surface was dominated by Cu(OH)2 species (68.01%), with a corresponding Cu+ content of 29.56% and a minor Cu0 signal of 2.44%. This composition suggests that the oxalate-derived surface is highly susceptible to reconstruction with a Cu+-rich surface state, which may contribute to high C2+ product selectivity as shown in Fig. 3.66,67 The impact of the polypyrrole coating is evident in the post-CuOA3_pPy0.25 sample (Fig. S19b and c). The Cu(OH)2 area percentage decreased to 51.58% compared to the uncoated CuOA 3 sample, while the Cu+ fraction increased to 42.26%. This trend was further pronounced upon etching; the post-CuOA3_pPy0.25-Etch sample revealed an enrichment of reduced species, with Cu0 increasing to 8.48% and Cu+ to 49.48%, accompanied by a further reduction in Cu(OH)2 (42.04%). These results corroborate the N 1s analysis, indicating that the conductive polypyrrole sublayer effectively protects the underlying catalyst from excessive dissolution. Considering the higher Cu+ fraction relative to Cu0 and the superior C2+ selectivity observed for CuOA 3, together with the excellent structural stability of the pPy-modified samples, these findings suggest that simultaneously exploiting these two characteristics could enable the development of eCO2RR catalysts better suited for C2+ production.
For both EtOH and n-PrOH, the acetyl intermediate (CH3CHO*) obtained by the reduction of a methyl carbonyl intermediate (CH3CO*) is recognized as a key intermediate and has been reported by recent studies,68 although this is still an active area of investigation (see Fig. S20). The two selectivity determining steps (SDS-1 and SDS-2) were identified as part of a larger reaction network and were chosen to be the focus of this theoretical study at both the (a) CuOA 3 oxalate-derived catalyst and (b) cuprite surface (Cu2O). Next, three different Cu2O facets were chosen, and their adsorption energies with the key intermediate were calculated and compared, allowing us to identify the preferential surface on which the reaction is most likely to initiate. As shown in Fig. 5d, the lowest adsorption energy is seen on the (110) facet, making it most likely to be the anchor site during the early stages of the reaction, where subsequent catalytic transformations are expected to occur.69,70 The optimized adsorption configurations of related reaction intermediates on both cuprite Cu2O and oxalate-derived surfaces were also explored (Fig. S21) and subsequently used for the reaction energy barrier analysis.
Next, the reaction energy barriers along the eCO2RR pathway, identified as SDS-1 and SDS-2,68 were evaluated on the (110) facet applied to both catalytic systems. Fig. 5e shows that the oxalate-derived surface exhibits consistently lower reaction barriers compared with pristine cuprite along both reaction pathways. For the conversion from the methyl carbonyl intermediate to the acetyl intermediate on the pristine cuprite surface, the reaction energy barrier is calculated to be 0.78 eV, which is higher than that on the oxalate-derived surface (0.46 eV). The subsequent transformations toward either the EtOH precursor or the C3 intermediate leading to n-PrOH are thus energetically more favorable on the oxalate-derived surface, indicating improved reaction kinetics. This behavior can be attributed to the different coordination environments of Cu at the oxalate-derived surface compared to cuprite.
Additional data will be available on request.
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