The electrochemical reduction of CO2 is a pivotal technology for the defossilization of the chemical industry. Although pilot-scale electrolyzers exist, water management and salt precipitation remain a major hurdle to long-term operation. In this work, we present high-resolution neutron imaging (6 μm) of a zero-gap CO2 electrolyzer to uncover water distribution and salt precipitation under application-relevant operating conditions (200 mA cm−2 at a cell voltage of 2.8 V with a Faraday efficiency for CO of 99%). Precipitated salts penetrating the cathode gas diffusion layer can be observed, which are believed to block the CO2 gas transport and are therefore the major cause for the commonly observed decay in Faraday efficiency. Neutron imaging further shows higher salt accumulation under the cathode channel of the flow field compared to the land.
While there are clear pathways for the defossilization of the energy or transport sector, solutions are still needed for other sectors, which rely on fossil feedstock like oil and natural gas1. One technology that emerged as a promising candidate to provide fossil-free feedstock to the chemical industry is the electrochemical reduction of (captured) CO22. Many different reactor designs and target products have been proposed for this application, ranging from C1 to C3 products like carbon monoxide, formic acid, ethylene, and 1-propanol3,4. Gas-fed zero-gap electrolyzers comprising an anion exchange membrane (AEM) are currently the most promising reactor design to meet the requirements for industrial commercialization5 and electrolyzers having carbon monoxide (CO) as target product are already reaching pilot scale6. In spite of reported peak partial current densities of up to 1.0 A cm−27 and Faraday efficiencies (FE) for CO above 90% (at lower current densities), these types of electrolyzers still face major challenges regarding operation stability and durability8,9. Especially electrode dry out and flooding events, as well as salt precipitation are often made responsible for performance loss or even cell failure in such systems10,11,12,13. However, a clear understanding of these limiting effects is still missing.
The main reactions and transport mechanisms during electrochemical CO2 reduction in alkaline environments are displayed in the schematic drawing in Fig. 1a. The CO2 reduction reaction on the cathode side as well as the competing hydrogen evolution reaction (HER) consume water (reaction I–III).
By humidifying the CO2 gas stream, water is introduced to the cathode compartment. Through a concentration gradient of water between cathode and anode, additional water is transported from the anode side to the cathode side by diffusion. The hydroxide ions produced in the cathode reactions rapidly react with the gaseous CO2 forming bicarbonate (HCO3-) and carbonate (CO32-) ions in the following carbonation reactions:
Jeng et al. showed that bicarbonate and carbonate ions are thereby the primary charge carriers passing the membrane, dragging water in their hydration shell with them from the cathode to the anode compartment14. On the anode side, hydroxide ions are oxidized producing oxygen and water.
Although the AEM hinders potassium cations from crossing the membrane in bigger quantities by Donnan exclusion, a small amount of cations is still migrating through the membrane. As cations move from the anode to the cathode side, they drag water in their hydration shell with them. Over time potassium, carbonate and bicarbonate ions can accumulate at the cathode. When exceeding the solubility limit, by increasing ion concentration or by consumption of water, salt crystallites can precipitate on the cathode side. Figures 1c, d illustrates how precipitates supposedly influence the processes in the cathode gas diffusion electrode (GDE). Carbonate precipitates are normally porous and hydrophilic, increasing the capillary pressure inside the cathode GDE15. Hence, the precipitates make the GDE prone to electrode flooding. Liquids and precipitates can clog pores in the catalyst layer, microporous layer and the gas diffusion layer of the cathode GDE, and thereby impede the gas transport11. With an increasing amount of precipitates, the mass transport resistance for the CO2 to reach the active sites of the catalyst layer increases and the CO2 concentration at the catalyst surface will eventually decrease. The lower CO2 concentration may cause a selectivity shift towards the HER, as water can still be sufficiently supplied from the anode side through the membrane.
In situ neutron radiography has proven to be a powerful tool to investigate water transport in multiple electrochemical applications, such as fuel cells or water electrolyzers16,17. The technological advances of neutron imaging detectors significantly improved the resolution of neutron radiography in recent years. Nonetheless, only two neutron-imaging studies investigating CO2 electrolyzers have been published up to now. The first study investigated bubble formation in a liquid buffer layer on the cathode side18. Besides high cell potentials, cells with a liquid catholyte between the membrane and cathode GDE often exhibit fast electrode flooding, as the cathode is in direct contact with the liquid electrolyte. The circulating electrolyte, however, can wash away precipitates and depending on its chemical composition change the ion concentration at the cathode side compared to a zero-gap cell. The second study conducted neutron imaging of a zero-gap cell but with a cation exchange membrane19. Zero-gap cells using cation exchange membranes show significantly lower CO selectivity compared to cells using AEMs, as they provide an acidic reaction environments to the cathode, facilitating the competing HER20. Furthermore, protons moving from the anode to the cathode are responsible for the ionic charge transfer between the anode and cathode. The ionic transport and the electroosmotic drag are directed in the opposite direction compared to cells using AEMs, drastically changing the water balance. As the water balance and flooding behavior in the above-mentioned studies strongly differ, their results cannot be applied to AEM-based zero-gap CO2 electrolyzers. Etzold et al. have recently highlighted this lack of neutron studies for zero-gap CO2 electrolysis in a review21. This work therefore uses high-resolution operando neutron radiography to elucidate the water transport in an alkaline zero-gap CO2 electrolysis cell converting gaseous CO2 to CO.
Results and discussion
Figure 2 shows the electrochemical performance of two identical cell assemblies with a Sustainion® membrane, an IrO2 GDE anode and an Ag GDE cathode (all purchased from Dioxide Materials™). As can be seen from Fig. 2a, the first cell, which was neutron-imaged, had a slightly higher high-frequency resistance (HFR) than the second cell (average ∆HFR ≈ 0.1 Ω cm2) and thus a generally higher voltage (e.g. 2.9 V vs. 2.8 V at 200 mA cm−²). This could be caused by different durations of membrane storage in potassium hydroxide solution, variance in temperatures during the experiments (lab vs. beamline) or slight inaccuracies during cell assembly.
The corresponding CO Faraday efficiencies (FECO) measured for cell 2 stay above 92% between 25–200 mA cm−2 with a maximum FECO of 99% at 200 mA cm−2 (Fig. 2b). At higher current densities (300 mA cm−2) the FECO drops to 77% while the hydrogen evolution accounts for 6% of the product gas. Yet, the rise in FEH2 does not fully compensate for the drop in FECO resulting in a combined FEtotal = FECO + FEH2 of 83%. As seen in Fig. 2c, for 25–200 mA cm−2 the partial current density for CO does only slightly differ from the total current density. However, at 300 mA cm−2 approximately 51 mA cm−2 is going into other faradaic processes, with products that are not detected by the gas chromatography, potentially formate (HCOO−)10,22. Despite small deviations in cell voltage and HFR, both cells show a similar electrochemical performance in a range relevant for industrial commercialization (i > 200 mA cm−2 below 3 V and FE > 90%23,24,25).
Water transport and salt precipitation
Representative normalized neutron radiographic images of the electrolyzer at different operation points are shown in Fig. 3a. On the cathode side (left) channels and gas diffusion layer (GDL) appear bright (lower attenuation) as they are filled with gaseous CO2, while the anode side (right) is generally darker due to the aqueous KOH solution in the channel and GDE (see Fig. 1b for a detailed labeling of all cell parts). At 0 mA cm−2 the corners and edges of the cathode flow field are wetted by condensing water, visible as a dark shading along the edges. With increasing current density, the water consumption of the cathode reactions rises and the shading in the cathode channel gets gradually lighter and at 200 mA cm−2, the condensate has fully dried off.
Dark dents on the backside of the cathode GDE are reaching into the flow field channels and are penetrating the gas diffusion layer (a representative dent is marked with * in Fig. 3a). Their attenuation reduces with rising current density, indicating drying in that area. Nevertheless, at 300 mA cm−2 these bulges are still clearly visible, whereas the liquid condensate in the channel has fully dried off. Even though the images are averaged over several minutes, the bulges show sharp contours, indicating an immobile solid phase. The precipitation of carbonic salts is a widely known problem in zero-gap AEM CO2 electrolyzers. Various groups reported that after the experiments, precipitates in flow channels and on the backside of the GDE were even visible to the bare eye11,26,27,28,29. Kong et al. recently presented a study, quantifying the distribution of potassium carbonate (K2CO3) and potassium bicarbonate (KHCO3) in the GDEs post-mortem and showing precipitated salts penetrating the entire depth of the GDEs30. Endrődi et al. made similar observations31. K2CO3 shows significantly lower neutron absorption and scattering rates than water (see Supplementary Table 1 and Supplementary Fig. 6 for neutron transmission rates). Due to its low neutron attenuation, K2CO3 can only be observed indirectly, by imaging the retained water. Considering the deliquescent properties of K2CO3 and the moist reaction environment (humidified cathode gas stream, aqueous anolyte, a membrane with a high water uptake32 and low temperatures 23 ± 3 °C) carbonates inside the cell are very likely hydrated15. This should be the case, especially in the zero current state, when no water is consumed by the cathode reactions and condensing water in the cathode flow field is observed.
KHCO3 instead contains a hydrogen atom in its structure, yielding higher interactions with neutrons than K2CO3. To some extent, even dry KHCO3 salt should be visible in neutron radiography (see Supplementary Fig. 6). Nonetheless, KHCO3 is also strongly hygroscopic and retains water, which might more drastically affect the neutron opacity in a humid environment. Post-operation scanning electron microscopy and energy dispersive X-ray spectroscopy (SEM/EDX) measurements of a cathode cross section further show precipitates containing potassium in the silver catalyst layer, the micro-porous layer and in the gas diffusion layer (see Supplementary Fig. 7). The presence of KHCO3 in the catalyst layer was additionally verified by post-operation Raman measurements (see Supplementary Fig. 8). Considering those results and the mentioned observations made by other groups30,31, it can be assumed that the dark dents originate from precipitated KHCO3 and water retained by the precipitates in that area.
By that, the intensity differences alongside the cathode GDE allow us to deduce where precipitates are mainly located in the electrode. For example, as the cathode GDE is brighter in the land area of the cathode flow field even at 0 mA cm−2, it can be assumed, that less precipitates are located in that area (note that KHCO3 and K2CO3 might have accumulated in the cathode GDE already in the preceding electrochemical measurements described in the methods section). The brightening of the dark areas with rising current density indicates drying either by consumption of water or by its transportation to the anode via electro-osmotic drag (see Fig. 1a).
On the anode side, a slight brightening, especially at the interface between GDE and channel can be observed with increasing current density. Due to the poor contrast in that area, further evaluation of those images is difficult. Therefore, all images were normalized with respect to the cell at zero current by dividing the image of interest by the zero current image (Fig. 3b). Values below one indicate a decrease in intensity and therefore an increase of water content compared to the zero current state. Values greater than one indicate drying of that region. These normalized images show the afore-mentioned observations more clearly. With rising current density, the oxygen evolution on the anode side leads to visibly higher accumulation of gas bubbles in the anode flow channels. In addition, spatial differences of the bubble accumulation alongside the flow channel can be observed. On the cathode side, the relation of water distribution and applied current density is less univocal. While at 25 mA cm−2 the condensate accumulation at the edges of the flow channels is reduced, the cathode GDE is slightly wetter than without current. At 50 mA cm−2, the whole cathode starts to become dryer, while the degree of dry-out significantly differs between channel and land area of the cathode GDE. With increasing current densities, the whole cathode GDE is gradually drying. Especially the region with precipitates and a thin layer close to the membrane become dryer. Going from 200 to 300 mA cm−2 this trend for the cathode GDE is coming to halt and the intensity in some regions of the cathode gas diffusion layer even decreases. As the water consumption significantly increases from 200 to 300 mA cm−2, it is unlikely that water causes this drop in intensity. However, besides water, two other processes could be responsible for that intensity drop: the formation of either KHCO3 or potassium formate (HCOOK) salts.
Weng et al. simulated the processes in a zero-gap CO2 electrolysis cell. The simulations predict that the solubility limit of carbonates produced at the cathode is reached at approximately 750 mA cm−2 33. Under less ideal conditions, this solubility limit can already be reached at significantly lower current densities, as shown by Wheeler et al. (visible precipitation at 100 mA cm−2)29. The electrochemical reduction of CO2 to HCOO−, as depicted in Eq. (III), has been reported by several groups as an occurring side reaction on silver catalysts in CO2 electrolysis cells10,22. Considering the drop in Faraday efficiency at 300 mA cm−2 and the potentially high local alkalinity at the electrode surface, it can be assumed that HCOO− is produced also in this case34.
Both HCOOK and KHCO3 salts show similar neutron attenuation and high concentrations should be visible in neutron radiography (see Supplementary Fig. 6 for neutron transmission rates). By only looking at the radiographic images, it is not possible to differentiate between the contribution of water or the different salts to the intensity decrease. However, considering the afore-mentioned points and the post-operation Raman and SEM/EDX measurements (see Supplementary Figs. 7 and 8), it is most probable that the accumulation of KHCO3 causes the observed drop in intensity.
To better discriminate potential non-stationary effects, Fig. 4 displays the time evolution of the cell voltage and of the neutron image intensity of the membrane including electrode layers, the cathode gas diffusion layer and the anode flow channels (see Supplementary Fig. 4 for selected regions). The cell voltage is stable during each current step (∆U < 2.0 mV min−1), with the exception of two small spikes at 100 mA cm−2 and 300 mA cm−2, most probably caused by condensate from the gas humidification entering the cathode inlet. By increasing the water content in the cathode, the condensate droplets lead to a decrease in intensity, visible as intermediate intensity drop in the cathode GDL and membrane area. From 25 to 200 mA cm−2 all intensity values are on average increasing with each current step, indicating higher bubble accumulation on the anode side and more water consumption on the cathode side. This coincides with the observations made in Fig. 3. However, after an initial rise of the cathode GDL intensity at 100 and 200 mA cm−2, the intensity is continuously decreasing with a similar rate for both currents. Reaching 300 mA cm−2, the intensity starts decreasing more drastically, even falling below the average intensity measured at 50 mA cm−2. Moreover, at the end of the 15 min period, the intensity has not yet reached a plateau.
Again, if the change in intensity would only account for water content, this observation would be counterintuitive, as the increased reaction rate leads to higher water consumption and electro-osmotic drag from cathode to anode (see Fig. 1a). This observation in the cathode GDL suggest that KHCO3 is continuously accumulating during cell operation. The different slopes of the cathode GDL intensity curve translate to KHCO3 accumulation already starting at 100 mA cm−2 and significantly increasing at 300 mA cm−2.
As clear differences between channel and land area were observed in cathode drying and anode gas formation (Fig. 3), the spatial differences are studied in more detail. Figure 5 shows the relative change in intensity along the cell profile, for each current density relative to the zero current cell. Each curve represents the average of three land and three channel profiles (see Supplementary Fig. 5). The drying of the cathode GDE is more pronounced in the channel area, which indicates that the CO2 gas stream is generally removing more water than bringing into the cell. This implies a net water flux from anode to cathode, which is probable in the current conditions of a fully humidified gas in the cathode and liquid 0.1 M KOH in the anode29.
Figure 5 also shows that the bubble accumulation on the anode side is more pronounced in the region of the cathode land, indicating higher local currents in the cathode land region. This implies that ions or electrons and not gaseous reactants generally limit the cathode reaction, since the land region has a higher current despite the typically lower gas concentration. This is in line with the electrochemical data, which does not feature the typical mass transport limitation that causes an overpotential, bending the IV-curve above the linear relation (Fig. 2a)35. While this might be surprising, one has to consider that a region depleted of CO2 might still have a sufficiently high water content for the hydrogen evolution reaction. The utilized Sustainion® membranes were reported to have a very high water uptake of ∼80%32,36 and are only getting slightly drier during cell operation (see Fig. 5), directly providing water to cathode catalyst layer. CO2, however, has to reach the active sites of the cathode catalyst layer by diffusing from the cathode flow field channel through the gas diffusion layer, the micro-porous layer and finally the pores of the catalyst layer. With rising current density, more CO2 is consumed by the CO2 reduction reaction and the carbonation reaction, lowering the CO2 concentration at the electrode surface. Precipitates in the electrode add an additional diffusion barrier for CO2 (see Fig. 1d). Thus the reaction shifts to the HER resulting in lower faradaic efficiency of the CO2 reduction at high current densities (Fig. 2c) instead of increasing the overpotential.
The previously mentioned wetting of the cathode GDE at 25 mA cm−2 is also easily distinguished in this graph for both channel and land. In line with the current understanding of electro-osmotic drag, the hydroxide ions drag along water, humidifying the cathode and even slightly the membrane. At higher currents, however, the cathode and membrane are dryer than in the zero current state, which indicates that water consumption and electro-osmotic drag are higher than water-sorption/resupply from the gas phase and diffusion from the anode.
Although precipitates and associated electrode flooding are visible in the neutron images over the entire current range (precipitates potentially already formed during pretests), the cell is demonstrating good cell performance with FECO above 90% for current densities below 300 mA cm−2. This indicates that gas transport is still sufficient in that region. Only reaching 300 mA cm−2, when HCOO- formation and salt precipitation are increasing significantly, the FECO decreases. This shows that the electrochemical data alone is a poor indicator for the presence of precipitates.
Several strategies have been proposed in literature to mitigate salt precipitation on the cathode side11,26,27,31, but no approach has emerged as the most promising so far. Recent publications reporting high partial current densities for CO are most often operating at elevated temperatures of up to 65 °C7,37. Therefore, after the replication of the neutron imaging experiments, further measurements at a cell temperature of 50 °C were conducted with the identical cell 2 (see Supplementary Fig. 3). The elevated temperature facilitates enhanced CO2 reduction performance (FECO of 99% at 300 mA cm−2 and 2.8 V). The cell reaches a maximum in CO partial current density of 435 mA cm−2 and the FECO starts decreasing at 500 mA cm−2. The positive effects of the elevated temperature could be due to a multitude of factors like improved kinetics, enhanced mass transport, higher solubility or ion conductivity.
In summary, this work investigates the spatio-temporal evolution of water distribution in a gas-fed, zero-gap CO2 electrolyzer cell at different operation points by employing high-resolution neutron radiography. The cell shows industrially relevant cell performance (200 mA cm−2 at a cell voltage of 2.8 V and FECO of 99%). Even though intrinsic material restrictions (wet assembly of Sustainion®) or generation of side products with high neutron interaction complicate the quantification of water in CO2 electrolyzers compared to water-based applications like fuel cells or water electrolyzers, several important findings can be derived: A drop in faradaic efficiency at 300 mA cm−2 was observed, indicating HCOO- formation. Precipitated salts and precipitate-associated electrode flooding in the cathode GDE are visible throughout the entire experiment. At higher current densities, the accumulation of precipitates further increases. The water distribution on the cathode side is heavily influenced by the hygroscopic properties of the precipitated salts. The high spatial resolution makes these small structural changes apparent on a scale of some µm. More precipitates are visible in the cathode channel area than in the land area. Furthermore, bubble accumulation was clearly visible on the anode side. The observed local differences suggest higher local reaction rates in the cathode land region, which indicates that the overall cathode reaction is not limited by gaseous transport up to 300 mA cm−2 but is rather shifting to hydrogen evolution reaction when CO2 is depleting. Furthermore, higher local reaction rates can lead to local dry-out and hotspots potentially leading to ionomer degradation and finally cell failure. The influence of flow field design and local cell compression should therefore be included in future development to further increase the performance and durability of CO2 electrolyzers. The same applies for the mitigation of the observed salt precipitation in AEM CO2 electrolyzers. In summary, this work demonstrates that high-resolution neutron radiography is a powerful tool to investigate in-situ processes like water transport as well as salt precipitation and local current density distributions in gas-fed CO2 electrolyzers.
A zero-gap electrolysis cell (2 cm × 1 cm active cell area) was custom-built (see Supplementary Fig. 1 and 2 for schematics of the experimental setup). The cell fixture is designed for in-plane neutron imaging. It consists of two stainless steel (AISI 904 L) end plates and two flow fields made from titanium grade 2.0 coated in gold. A serpentine flow field design has been chosen for the gas flow on the cathode side, whereas the anode comprises a vertical parallel flow field. Figure 1b shows an enlarged section of a representative neutron radiography, labeling the different cell components and their corresponding thicknesses. The flow channels on either side are 500 µm wide and deep. The utilized silver cathode GDE, the IrO2 anode GDE (both described under Dioxide Materials™ US patent 9,555,367) as well as the Sustainion® X37-50 RT anion exchange membrane were purchased from Dioxide Materials™. The received electrodes (5 cm × 5 cm) were cut into smaller pieces (2 cm × 1 cm). They were then compressed to a thickness of 500 µm (∼30% compression) with two 250-µm PTFE gaskets acting as “hard stop”. Custom punching tools were used to reproducibly cut gaskets and electrodes. Two centering pins ensure precise alignment of all fixture components during assembly. The membrane thickness was measured ex situ with a micrometer gauge (74 µm) and is assumed incompressible. Before cell assembly, the membrane was ion exchanged by immersing it in a 1 M potassium hydroxide solution (made from ACS reagent ≥85% pellets, Sigma-Aldrich and deionized water) for 24 h and was then stored in a sealed container filled with fresh 1 M KOH solution until needed. The ion exchange of the electrodes, also in 1 M KOH, was conducted approximately 12 hours before the cell measurements. Before stacking the electrodes and membrane, excess liquids were carefully removed with paper tissue. The cell was mounted onto an electronically controlled motion stage for precise alignment of the cell between the detector and neutron beam. The neutron beam enters through an in-cut window of the flow fields. In the window region the flow fields measure 2 cm in beam direction and the active cell area measures 2 cm vertically and 1 cm horizontally (in beam direction).
The cathode was supplied with a mixture of 47.5 sccm CO2 (grade 4.5, Messer Industriegase GmbH) and 2.5 sccm Nitrogen (grade 5.0, Linde) by two digital mass flow controllers (Bronkhorst). A bubbler heated to 50 °C was used to humidify the cathode gas stream. 0.5 L of a 0.1 M KOH solution was circulated on the anode side at a flow rate of 20 mL min−1 with a peristaltic pump (Reglo ICC 7800-58, Ismatec). A Biologic Galvono-/Potentiostat VSP-300 was used for all electrochemical measurements. The cell performance was evaluated by applying different current densities from 0 mA cm−2 to 300 mA cm−2. Each current was applied for 15 minutes and at the end of each current step, a galvanostatic electrochemical impedance spectroscopy measurement (1–500 kHz and 5% amplitude) was conducted to determine the high-frequency resistance. Gas compositions were quantified with an Agilent micro gas chromatograph (GC) 990 equipped with a CP-COX column. The Faraday efficiencies were only determined using an identical cell (electrodes and membranes from the same batch) with the same setup and measurement procedure as for the imaging experiments. GC measurements were conducted after 14 minutes of each current step.
After cell assembly the cell was put on the holder and connected to the tubing as quickly as possible to avoid drying of the cell. Gas flow and anolyte flow were started immediately after connecting the tubing. The cell was flushed with electrolyte for approximately 10 min before starting the first measurements. Before the presented measurements, several pretests were conducted. The pretest protocol starts with several voltages steps from 1.5 to 3.2 V of 50 s each followed by an EIS measurement and a linear sweep voltammetry. Immediately after that, the first current step experiment was started with a bubbler temperature of 30 °C. Due to the very short pause between the pretests and the current steps, the cell did not have enough time to reach an equilibrated state. The effects on the water content of the pretests were superposing the actual effects of the low current densities (25–50 mA cm−2) applied in the current step experiment. Therefore, that data was not evaluated.
The cell potential corrected by the contribution of ohmic overpotential (UiRfree) was calculated as follows:
Ucell stands for the measured cell potential, i for current density and HFRi for the high frequency resistance at the specific current density. The HFR was determined by taking the x-axes intercept of a Nyquist plot of the EIS measurements conducted at each current density.
The Faraday efficiency for the product x was calculate using this equation
Where nx is the measured mole fraction of the individual product measured by GC, F the Faraday constant, z the charge transfer number, p the pressure, R the ideal gas constant, T the temperature, V̇ the volume flow and I the total current. The nitrogen flow rate is assumed to be constant and not to be affected by processes in the cell. The change of the nitrogen fraction of the product gas is used to calculate a corrected volume flow to compensate for the reduction in volume flow due to CO2 crossover. The partial current density of the product x was calculated by multiplying the corresponding Faraday efficiency with the total current density
Neutron radiographic imaging
The neutron radiography measurements were performed at the NeXT instrument at the Institut Laue-Langevin38. The neutron beam has a white spectrum with wavelengths between approximately 1.5 Å and 20 Å. The through-plane direction of the assembled cell was oriented horizontally. To enhance the resolution in this horizontal direction, while maximizing flux, the beam aperture was set to a width of 5 mm and a height of 30 mm by a slit, yielding for the collimation ratio L/D values of 2000 and 333 in the horizontal and vertical directions, respectively. The neutron imaging detector used in this experiment is an intensified neutron microscope from the ANTARES beamline of Forschungs-Neutronenquelle Heinz Maier-Leibnitz (FRM II)39,40. It uses a 5-µm-thick Gd1572O2S scintillator that absorbs neutrons and emits scintillation light at green wavelengths. The microscope is built with two infinity corrected lenses facing each other, with a Zeiss 55 mm f/1.4 lens as the objective lens and a Nikon 70–200 mm f/2.8 zoom lens as the tube lens. A 1:1 relay is mounted between intensifier and camera. In all the experiments, the Nikon lens was set at f = 200 mm, yielding a magnification of 3.63. A Photonis 1-stage image intensifier (Cricket, 18 mm diameter) is used to amplify the scintillation light coming out of the light microscope and the 1:1 relay. The camera is a Hamamatsu Fusion BT sCMOS camera with 2304 × 2304 pixels, 6.5 µm in size. With the magnification of 3.63, the setup yields a maximum field of view of about 5.7*5.7 mm, with an effective pixel pitch of 1.79 µm and an estimated spatial resolution of about 6 µm. The exposure time of each neutron radiography is 10 s. For each neutron radiographic image gamma spot noise was removed41. Electrolysis cell images, open beam images (90 frames) and camera dark images (30 frames) were taken to calculate the normalized neutron radiographic images. The normalization of the neutron radiographic images was conducted as:
Where IMGnorm represents the normalized image; IMGcell represents the obtained radiography of the electrolysis cell; IMGdark represents the dark image of the detector; IMGopen represents the open beam image taken without electrolysis cell. Each image presented in this work represents an average of the images taken in a 15 min current hold period (90 frames with 10 s exposure time), neglecting the first 100 s (10 frames) for cell equilibration and the period of 2 single condensate events observed at 100 mA cm−2 and 300 mA cm−2 (see Fig. 4).
To highlight the intensity changes at the different operating points, the images were referenced to an image of the zero current cell. This was done by dividing the averaged and normalized image of the particular current density (IMGi) by the averaged and normalized image of the zero current cell (IMG0):
All data displayed in the figures of the manuscript and the supplementary information are provided in the Source Data file. The single averaged neutron radiographic images presented in Fig. 3 are provided with this paper. The neutron radiography raw data of this study is available from the corresponding author upon request due to the large size. Source data are provided with this paper.
Hepburn, C. et al. The technological and economic prospects for CO2 utilization and removal. Nature 575, 87–97 (2019).
Senocrate, A. & Battaglia, C. Electrochemical CO2 reduction at room temperature. Status and perspectives. J. Energy Storage 36, 102373 (2021).
Liang, S., Altaf, N., Huang, L., Gao, Y. & Wang, Q. Electrolytic cell design for electrochemical CO2 reduction. J. CO2 Utilization 35, 90–105 (2020).
Kuhl, K. P., Cave, E. R., Abram, D. N. & Jaramillo, T. F. New insights into the electrochemical reduction of carbon dioxide on metallic copper surfaces. Energy Environ. Sci. 5, 7050 (2012).
Weekes, D. M., Salvatore, D. A., Reyes, A., Huang, A. & Berlinguette, C. P. Electrolytic CO2 reduction in a flow cell. Acc. Chem. Res. 51, 910–918 (2018).
Masel, R. I. et al. An industrial perspective on catalysts for low-temperature CO2 electrolysis. Nat. Nanotechnol. 16, 118–128 (2021).
Endrődi, B. et al. High carbonate ion conductance of a robust PiperION membrane allows industrial current density and conversion in a zero-gap carbon dioxide electrolyzer cell. Energy Environ. Sci. 13, 4098–4105 (2020).
Park, S., Wijaya, D. T., Na, J. & Lee, C. W. Towards the large-scale electrochemical reduction of carbon dioxide. Catalysts 11, 253 (2021).
Malkhandi, S. & Yeo, B. S. Electrochemical conversion of carbon dioxide to high value chemicals using gas-diffusion electrodes. Curr. Opin. Chem. Eng. 26, 112–121 (2019).
Mardle, P., Cassegrain, S., Habibzadeh, F., Shi, Z. & Holdcroft, S. Carbonate Ion crossover in zero-gap, KOH anolyte CO2 electrolysis. J. Phys. Chem. C. 125, 25446–25454 (2021).
Leonard, M. E., Clarke, L. E., Forner-Cuenca, A., Brown, S. M. & Brushett, F. R. Investigating electrode flooding in a flowing electrolyte, gas-fed carbon dioxide electrolyzer. ChemSusChem. https://doi.org/10.1002/cssc.201902547 (2019).
Jesus Gálvez-Vázquez, M. de et al. Environment matters. CO2 RR electrocatalyst performance testing in a gas-fed zero-gap electrolyzer. ACS Catal. 10, 13096–13108 (2020).
Reyes, A. et al. Managing hydration at the cathode enables efficient CO2 electrolysis at commercially relevant current densities. ACS Energy Lett. 1612–1618. https://doi.org/10.1021/acsenergylett.0c00637 (2020).
Jeng, E. & Jiao, F. Investigation of CO2 single-pass conversion in a flow electrolyzer. React. Chem. Eng. https://doi.org/10.1039/D0RE00261E (2020).
Li, M. et al. The role of electrode wettability in electrochemical reduction of carbon dioxide. J. Mater. Chem. A 9, 19369–19409 (2021).
Breitwieser, M. et al. Water management in novel direct membrane deposition fuel cells under low humidification. Int. J. Hydrog. Energy 41, 11412–11417 (2016).
Strobl, M. et al. Advances in neutron radiography and tomography. J. Phys. D Appl. Phys. 42, 243001 (2009).
Krause, K. et al. Electrolyte layer gas triggers cathode potential instability in CO2 electrolyzers. J. Power Sources 520, 230879 (2022).
Shafaque, H. W. et al. Boosting membrane hydration for high current densities in membrane electrode assembly CO2 Electrolysis. ACS Appl. Mater. interfaces https://doi.org/10.1021/acsami.0c14832 (2020).
Delacourt, C., Ridgway, P. L., Kerr, J. B. & Newman, J. Design of an electrochemical cell making syngas (CO+H2) from CO2 and H2O reduction at room temperature. J. Electrochem. Soc. 155, B42 (2008).
Etzold, B. J. M. et al. Understanding the activity transport nexus in water and CO2 electrolysis. State of the art, challenges and perspectives. Chem. Eng. J. 424, 130501 (2021).
Larrazábal, G. O. et al. Analysis of mass flows and membrane cross-over in CO2 reduction at high current densities in an MEA-Type Electrolyzer. ACS Appl. Mater. interfaces 11, 41281–41288 (2019).
Salvatore, D. & Berlinguette, C. P. Voltage matters when reducing CO2 in an electrochemical flow cell. ACS Energy Lett. 5, 215–220 (2019).
Burdyny, T. & Smith, W. A. CO2 reduction on gas-diffusion electrodes and why catalytic performance must be assessed at commercially-relevant conditions. Energy Environ. Sci. 12, 1442–1453 (2019).
Verma, S., Kim, B., Jhong, H.-R. M., Ma, S. & Kenis, P. J. A. A gross-margin model for defining technoeconomic benchmarks in the electroreduction of CO2. ChemSusChem 9, 1972–1979 (2016).
Xu, Y. et al. Self-Cleaning CO2 reduction systems. Unsteady electrochemical forcing enables stability. ACS Energy Lett. 809–815; https://doi.org/10.1021/acsenergylett.0c02401 (2021).
Verma, S. et al. Insights into the low overpotential electroreduction of CO2 to CO on a supported gold catalyst in an alkaline flow electrolyzer. ACS Energy Lett. 3, 193–198 (2017).
Wang, R. et al. Maximizing Ag utilization in high-rate CO2 electrochemical reduction with a coordination polymer-mediated gas diffusion electrode. ACS Energy Lett. 4, 2024–2031 (2019).
Wheeler, D. G. et al. Quantification of water transport in a CO2 electrolyzer. Energy Environ. Sci. 13, 5126–5134 (2020).
Kong, Y. et al. Visualisation and quantification of flooding phenomena in gas diffusion electrodes used for electrochemical CO2 reduction. A combined EDX/ICP–MS approach. J. Catal. 408, 1–8 (2022).
Endrődi, B. et al. Operando cathode activation with alkali metal cations for high current density operation of water-fed zero-gap carbon dioxide electrolyzers. Nat. Energy 6, 439–448 (2021).
Kaczur, J. J., Yang, H., Liu, Z., Sajjad, S. D. & Masel, R. I. Carbon dioxide and water electrolysis using new alkaline stable anion membranes. Front. Chem. 6, 263 (2018).
Weng, L.-C., Bell, A. T. & Weber, A. Z. Towards membrane-electrode assembly systems for CO 2 reduction: a modeling study. Energy Environ. Sci. 12, 1950–1968 (2019).
Seifitokaldani, A. et al. Hydronium-induced switching between CO2 electroreduction pathways. J. Am. Chem. Soc. 140, 3833–3837 (2018).
O’Hayre, R., Cha, S.-W., Colella, W. & Prinz, F. B. Fuel Cell Fundamentals (John Wiley & Sons, Inc, Hoboken, NJ, USA, 2016).
Lindquist, G. A. et al. Performance and durability of pure-water-fed anion exchange membrane electrolyzers using baseline materials and operation. ACS Appl. Mater. interfaces https://doi.org/10.1021/acsami.1c06053 (2021).
Wakerley, D. et al. Gas diffusion electrodes, reactor designs and key metrics of low-temperature CO2 electrolysers. Nat. Energy 370, eaba6118 (2022).
Tengattini, A. et al. NeXT-Grenoble, the Neutron and X-ray tomograph in Grenoble. Nucl. Instrum. Methods Phys. Res. Sect. A Accel. Spectrom. Detect. Assoc. Equip. 968, 163939 (2020).
Schulz, M. & Schillinger, B. ANTARES. Cold neutron radiography and tomography facility. JLSRF 1, https://doi.org/10.17815/jlsrf-1-42 (2015).
Calzada, E., Gruenauer, F., Mühlbauer, M., Schillinger, B. & Schulz, M. New design for the ANTARES-II facility for neutron imaging at FRM II. Nucl. Instrum. Methods Phys. Res. Sect. A Accel. Spectrom. Detect. Assoc. Equip. 605, 50–53 (2009).
Li, H., Schillinger, B., Calzada, E., Yinong, L. & Muehlbauer, M. An adaptive algorithm for gamma spots removal in CCD-based neutron radiography and tomography. Nucl. Instrum. Methods Phys. Res. Sect. A Accel. Spectrom. Detect. Assoc. Equip. 564, 405–413 (2006).
Han, Y., Disch, J. L., Koch, S., Schulz, M. & Tengattini, A. Investigation of water transport in anion-exchange membrane electrolyzers via events reconstruction based neutron imaging. https://doi.org/10.5291/ILL-DATA.1-05-51 (2021).
This work was funded by the Vector Foundation (CO2-to-X, S.V.) and the German Federal Ministry of Education and Research (NeutroSense, O5K19VFA, M.B. and 05K19WO2, M.S.). The authors want to thank the Institute Laue-Langevin (ILL) for hosting the neutron radiography experiment42.
Open Access funding enabled and organized by Projekt DEAL.
The authors declare no competing interests.
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Disch, J., Bohn, L., Koch, S. et al. High-resolution neutron imaging of salt precipitation and water transport in zero-gap CO2 electrolysis. Nat Commun 13, 6099 (2022). https://doi.org/10.1038/s41467-022-33694-y
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