Christian Berger,
Tolga Acartürk
,
Ulrich Starke
,
Joachim Maier
and
Rotraut Merkle
*
Max Planck Institute for Solid State Research, Stuttgart, Germany. E-mail: r.merkle@fkf.mpg.de
First published on 28th May 2025
The ion transport of triple-conducting Ba0.95La0.05(Fe1−xYx)O3−δ perovskites (x = 0 and 0.2) containing mobile protons, oxygen vacancies and electron holes is investigated. Proton diffusion coefficients are determined from hydration with D2O and time-of-flight secondary ion mass spectroscopy line scans, the oxygen vacancy conductivity is measured in an oxygen pumping cell. Oversized Y3+ dopants on the Fe site are found to decrease the effective proton as well as oxygen vacancy mobility. At 300–500 °C in 20 mbar H2O, the proton conductivity amounts to 3 × 10−6 to 10−4 S cm−1 with an activation energy 0.3 eV for x = 0, and 0.5 eV for x = 0.2. The vacancy conductivity covers a larger range of 3 × 10−6 to 10−2 S cm−1 with activation energies of 0.9–1 eV. The consequences of these conductivities for the kinetics of porous triple-conducting oxygen electrodes on protonic electrolytes are discussed. Importantly, both the proton and vacancy conductivity contribute to extending the active zone for the O2 ↔ H2O reaction.
![]() | ||
Fig. 1 (a) Electrode processes in SOFC/SOEC versus PCFC/PCEC. Sketch of (b) a dense, and (c) a porous oxygen electrode (positrode) on a protonic ceramic electrolyte. |
However, challenges of electrolyte processing and the need of developing adapted oxygen electrode (positrode) materials had impeded the manufacturing of PCFC and PCEC with competitive performances relative to SOFC and SOEC that benefit from a much longer history of technological optimization.6 First significant improvements were achieved for fuel cell mode.7–9 Motivated by the need of long-term energy storage from intermittent renewable energies the interest in the electrolysis mode increased. In recent years strongly improved PCFC and PCEC performances were reported (see e.g.5,10–15 and reviews16–19).
Key to high performances of both PCFC and PCEC is a fast oxygen reduction or steam oxidation reaction at the positrode. In cells based on oxide ion conducting electrolytes, positrodes with mixed electronic and oxide ion conductivity represent the state of the art because they allow extension of the oxygen exchange reaction from the triple phase boundary to larger regions of a porous positrode.20,21 For pore-free model positrodes on protonic electrolytes (Fig. 1b) it is obvious that the positrode material needs a certain proton conductivity, because in actual dense film electrodes the lateral width is orders of magnitudes larger than the film thickness, and the contribution of the triple phase boundary to the overall positrode kinetics becomes marginal. The corresponding scaling of the electrode resistance with reciprocal electrode area has exemplarily been demonstrated for PrBa0.5Sr0.5Co1.5Fe0.5O5+δ on an BaZr0.4Ce0.4Y0.1Yb0.1O3 electrolyte.5 In actual cells, porous electrodes are used, which may further complicate the situation. It is still obvious that a substantial bulk proton conductivity of the positrode material is beneficial, as it increases the region where protons are supplied to the positrode surface to drive direct oxygen reduction to water (or the inverse reaction) there (Fig. 1c). However, as discussed later in the present publication, for porous positrodes also the oxygen ion conductivity may play a role. Indications for such a more complex situation have also been presented by Amezawa in ref. 22 and 23. In this context, one should keep in mind that also for mixed-conducting SOFC/SOEC positrodes the overall electrode resistance is governed by a combination of surface exchange and bulk transport parameters, in that case specifically and
for oxygen (Adler–Lane–Steele (ALS) model21).
While in actual PCFC/PCEC often multi-phase positrode materials are employed to achieve the required properties, we focus here on the transport properties of single-phase triple-conducting perovskites; these single-phase properties are indispensable for a detailed understanding of any composite. Typical materials are (Ba,Sr)(Fe,Co,Ni)O3−δ perovskites (see e.g. overviews in ref. 24 and 25); also layered perovskite-related materials such as PrBa0.5Sr0.5Co1.5Fe0.5O5+δ (PBSCF), BaGd0.8La0.2Co2O6−δ (BGLC), Sr3Fe2O7−δ have been used.5,26,27 They all combine p-type electronic conductivity with proton and oxide ion conductivity. In several studies B-site dopants have been included, e.g. to prevent the materials from transforming into a hexagonal perovskite9 or to increase proton uptake.24,28 Protonic defects (hydroxide ions on oxide ion sites ) and oxygen vacancies
may come into close contact with B-site dopants and thus experience perceptible defect interactions. Calculations for BaFe0.875(Sc,Ga,In,Y)0.125O3 perovskites using density functional theory indeed indicate the presence of perceptible and complex defect interactions.29 Therefore, in the present investigation we compare the ion transport properties of Ba0.95La0.05FeO3−δ (BLF) without and Ba0.95La0.05Fe0.8Y0.2O3−δ (BLFY) with B-site doping (the 5% La doping on the A-site is necessary to keep BLF in the cubic perovskite structure30 but not expected to significantly affect the defect chemistry, cf. Fig. S3 in the ESI†). Owing to the substantial experimental effort, we concentrate on these two compositions: Y-free Ba0.95La0.05FeO3−δ, and Ba0.95La0.05Fe0.8Y0.2O3−δ which represents the maximum Y solubility in BaFeO3−δ. Measurements on lower Y contents and other dopants with different size and/or chemical character such as Sc3+, In3+ remain for future studies.
The proton incorporation of BaFeO3−δ-based perovskites is dominated by the hydration reaction (dissociative water incorporation into oxygen vacancies forming protonic defects
= hyroxide ions on oxide ion sites)
![]() | (1) |
The measurement of proton mobility or conductivity in such triple-conductors is much more challenging.18,32 As electrode materials, they exhibit predominant electronic conductivity approximately in the range of 1–100 S cm−1. Furthermore, the ionic conductivity – expected to be below 10−3 S cm−1 in the relevant temperature range of 300–600 °C – comprises proton as well as oxide ion conductivity which need to be properly separated. Attempts to determine the proton conductivity from DC measurements utilizing proton-selective contacts (Hebb–Wagner type experiments33,34) are hampered by the fact that for example the Ba(Zr,Ce,Y,Yb)O3−δ “protonic electrolytes” actually have a non-negligible hole conductivity when completely exposed to oxidizing atmosphere35 (in FC/EC application this hole conductivity is suppressed in the region close to the hydrogen electrode). Thus in ref. 36 and 37 a La1−xCaxNbO4 ceramic was used which has much lower electronic transport (but also lower proton conductivity) than Ba(Zr,Ce,Y,Yb)O3−δ electrolytes. Alternatively, the measurement temperature had to be restricted to ≤ 300 °C when using a SrZr0.9Y0.1O3−δ electrolyte.38 Proton mobilities in triple-conducting perovskites have also been extracted from hydrogen permeation measurements (applying a dense Pd layer intended to protect the samples from decomposition by reduction, e.g. in ref. 14, 39 and 40), but this approach has received also some scepticism (can the hydrogen-permeable Pd layer sufficiently protect the sample).18 In ref. 41 electromotive force measurements in pH2O and pO2 gradients were performed for triple-conducting BaCeO3–BaFeO3 composites, but owing to the low proton transference number (<1% in oxidizing conditions) the authors also indicate that the accuracy of this approach to measure is limited.
Measurements of chemical diffusion coefficients by relaxation experiments (e.g. conductivity relaxation such as ref. 42 for oxygen exchange, ref. 43 for hydration kinetics of triple conductors) in principle allow one to determine diffusivities of ionic defects in predominantly electronically conducting materials. However, such integral measurements face two challenges: (i) they crucially rely on the absence of cracks during the whole experiment series. This is not easy to ensure and to verify in materials such as Ba0.95La0.05(Fe1−xYx)O3−δ which exhibit substantial chemical expansion upon hydration as well as upon changes of oxygen stoichiometry by redox reaction. (ii) The separation of surface exchange (k) and bulk diffusion coefficient (D) may be ambiguous, in particular when the measured data contain some noise.
In ref. 44 and 45 triple-conducting PrBa0.5Sr0.5Co1.5Fe0.5O5+δ and Sr0.9Ce0.1Fe0.8Ni0.2O3−δ samples were hydrated with D2O and the D and DO profiles recorded by secondary ion mass spectroscopy (ToF-SIMS) in depth profiling mode. However, given the high proton and deuterium diffusivities even at low temperatures, depth profiling might not be the optimum measurement technique. In the present investigation we decided to perform a chemical diffusion experiment (hydration with D2O) combined with ToF-SIMS line scans to measure space-resolved deuterium profiles over a penetration depth of several hundred micrometers. In such profiles cracks – if present – can easily be recognized from locally enhanced deuterium concentrations, and respective regions (or complete samples) are excluded from the analysis. Owing to their comparably large lattice parameters and the absence of cobalt, Ba(Fe,Acc)O3−δ perovskites (Acc3+,2+ = redox-inactive dopant, being an acceptor relative to Fe4+) have only moderate electronic conductivities (e.g. 8 and 0.8 S cm−1 for Ba0.95La0.05FeO3−δ and BaFe0.8Y0.2O3−δ at 600 °C in air28). In an oxygen pumping cell, the range of intermediate oxygen partial pressures 10−25 ≤ pO2 ≤ 10−5 bar can be accessed, and the present Ba0.95La0.05(Fe1−xYx)O3−δ perovskites reach an ionic plateau of pO2-independent oxygen vacancy conductivity. Finally, we use the obtained proton and oxygen vacancy conductivities
to discuss their impact on the overall oxygen exchange kinetics in porous oxygen electrodes of PCFC/PCECs.
We concentrate in the present publication on the effect of ion transport within the positrode material on the overall surface kinetics. Direct measurements of the surface kinetics of oxygen reduction to water (the relevant surface reaction for PCFC cathodes) and related mechanistic investigations are beyond the scope of the present investigation. Such measurements come with their own specific challenges, as briefly discussed at the end of the present publication.
Chemical diffusion of water refers to the coupled incorporation of oxide ions and protons/deuterons in response to a step in μH2O or μD2O at the surface of the oxide. Such a combined transport of positive and negative ions (or correspondingly oxygen vacancies in the opposite direction) is also denoted ambipolar diffusion. The two charged defects and
are coupled by the bulk electroneutrality condition, and thus the chemical diffusion of the incorporated overall neutral compound-D2O-can be described by a single single chemical diffusion coefficient
which depends on the
and
diffusivities. For oxides in which only the concentrations of
and
(or
) are variable (i.e. no pronounced redox activity) and no pronounced association effects are present, it can be shown that the water chemical diffusion coefficient is bounded by the defect diffusivities
, and can be expressed as
![]() | (2) |
![]() | (3) |
Some more detailed aspects of water chemical diffusion and isotope effect in H/D exchange in a mixed conducting oxide (but with largely fixed oxidation states) are further discussed in the ESI Sections 4–6.†
For the majority of experiments we chose approach (ii) for operational reasons: It allows us to obtain deuteron concentration profiles without extensive equilibration times that otherwise would be required to ensure full equilibration of ≈6 mm thick dense samples with pH2O at comparably low temperatures. In the present investigation, the Ba0.95La0.05(Fe1−xYx)O3−δ samples are first annealed in dry N2, which brings iron predominantly into 3+ oxidation state.28 Then the proton incorporation is carried out at 300–500 °C by reaction (1), i.e. without any redox process. Thus the Ba0.95La0.05(Fe1−xYx)O3−δ samples under the present experimental conditions approach the behavior of a perovskite containing solely fixed-valence B-cations. In first approximation we can therefore use relation (3) which equates values from approach (ii) to the deuteron diffusivity
. As a crosscheck, some experiments were performed as actual H/D exchange (approach (i)) directly yielding
. As shown below in Fig. 3 the respective
values agree well with the data from approach (ii) and relation (3).
In ESI Section 6† the influence of a trapping on protons/deuterons (for example at Fe-site dopants) is discussed. With proton trapping, approaches an effective diffusion coefficient
including a differential trapping factor χH instead of directly using the diffusivity
of an untrapped deuteron.
As detailed in the Experimental section, the profiles are normalized to the range of [1:
0] and the water chemical diffusion coefficient is fitted for the case of semi-infinite diffusion according to eqn (7). As illustrated in Fig. 2b, the measured profiles of the D signal as well as of the OD signal could be well fitted with a single, constant diffusion coefficient. As detailed in ESI Section 3 and Fig. S5,† the applied normalization procedure might lead to an underestimation of the diffusion coefficient by up to 30%. This may appear as a large uncertainty, but compared to the large scatter of proton conductivities for closely related materials – but measured with different techniques – we consider this not to be critical. ESI Section 4† gives some further details why under the present measurement conditions the D2O chemical diffusion can be described by a single diffusion coefficient.
The extracted D2O chemical diffusion coefficients are summarized in Fig. 3. As derived form eqn (2), this is expected to approach the deuteron diffusion coefficient
for low degrees of hydration. To confirm that the samples actually fall into this regime, several D2O experiments were conducted with a decreased pD2O of 2 mbar. The obtained diffusivities agree well with the data from pD2O = 20 mbar. As a further crosscheck, two experiments for BLFY were performed as H/D exchange experiments with samples prehydrated in H2O for extended time. As discussed in more detail in ESI Section 5,† proton and deuteron diffusivity differ (not exactly by a factor of √2, but typically not by more than a factor of 1.5,49) and the H/D exchange averages over that. The proton/deuteron diffusivities from these H/D exchange experiments agree well with the
data, supporting that under the present conditions the D2O hydration procedure yields diffusion coefficients that closely match the respective deuteron diffusivity
. In presence of pronounced proton trapping, instead of the untrapped carrier diffusivity this analysis yields an effective diffusivity
(ESI Section 6†).
![]() | ||
Fig. 3 D2O chemical diffusion coefficients of BLF and BLFY for pD2O = 2 mbar and pD2O = 20 mbar, stars correspond to H/D exchange of H2O-prehydrated samples (extracted from D profiles; results from OD shown in Fig. S6†). The grey dashed lines show the proton diffusivities of BaCe0.84Y0.16O3−δ and BaZr0.9Y0.1O3−δ electrolytes.50,51 |
For BLFY for which overall the largest number of measurements was carried out, the uncertainty range for the extracted values is estimated to amount to approximately a factor of 2.
The main observations from Fig. 3 are the following. (i) The deuteron/proton diffusivity of BLF is lower than, but still within an order of magnitude close to BaCe0.84Y0.16O3−δ and BaZr0.9Y0.1O3−δ electrolytes. (ii) The presence of oversized Y dopants on the Fe site in BLFY decreases
by a factor of about 6–9 compared to BLF. (iii) The activation energy of BLFY amounts to ca. 0.7 eV at 400–500 °C, and it increases for lower temperatures. Taken together, the latter two features point towards the presence of strong defect interactions in BaFeO3−δ, in particular in its highly Y-doped variant. These interactions may comprise several contributions, for example trapping effects at B-site dopants.52,53 Proton trapping at acceptor dopants has been observed in BaZrO3 electrolytes, and leads to an increased effective activation energy in the low-temperature region (however, a proper description has to extend beyond simple two-state models3,63). Indications for proton trapping in B-site doped BaFeO3 have been obtained from DFT calculations; the most pronounced trapping was found for Y.29 Furthermore, that investigation revealed a repulsion zone for protons in the first coordination shell around Y3+, with a site energy substantially higher than in the second shell trapping zone, and also higher than for large distances. Such repulsion impedes the formation of percolating low-energy paths for long-range transport. Also in BLF without B-site dopants, some trapping might be caused by the presence of a high
concentration under the present experimental conditions. DFT calculations for BaFeO3−δ indicate an energy landscape with varying site energies for protons depending on their position relative to
and the lattice distortions and modifications of Fe–O bonding character caused by oxygen vacancies.54
The magnitude of deuteron mobility decrease for BLFY by almost an order of magnitude compared to BLF is reasonably consistent with the proton trapping energy of 0.2 eV in the second shell around Y3+ from DFT.29 Assuming that the standard entropy of the trapping reaction is negligible, the mass action constant K of the de-trapping reaction eqn (S3)† amounts to 0.03. Together with the total concentration of Y3+ trapping centers of 0.2 this yields a differential trapping factor of 0.15 (eqn (S7)†). So the trapping accounts for the major part of proton mobility decrease. An additional contribution stems from the repulsion of protons from the first shell around Y3+, which hinders the formation of long-range low-energy percolating paths. Nevertheless, these numbers are only a first estimate.
From the deuteron/proton diffusivities in Fig. 3 and the proton concentrations measured by thermogravimetry (Fig. S3 in the ESI†) the proton conductivity of BLF and BLFY can be calculated according to the Nernst–Einstein relation (eqn (8) in “Experimental details”). In case of proton trapping, the trapping factor contained in Deff serves to converting the total proton concentration from thermogravimetry to the untrapped proton concentration. The resulting
is shown in Fig. 4a. The proton conductivities of BLF and BLFY are significantly lower than that of Ba(Ce,Zr,Y,Yb)O3−δ electrolytes which are largely hydrated at temperatures below approx. 500 °C, i.e. have much higher proton concentrations. Owing to the higher proton concentrations of BLFY, the conductivities of BLF and BLFY differ less than their (effective) proton diffusivities. Since the proton concentrations of both BLF and BLFY decrease with increasing temperature in the measured range, the activation energy of
of approx. 0.3–0.5 eV (extracted from log(σT) versus T) is lower than that of the proton diffusivity.
![]() | ||
Fig. 4 (a) Proton conductivity of BLF and BLFY for pH2O = 17 mbar calculated from proton diffusivity (Fig. 3) and concentration at 17 mbar (Fig. S3†). The grey dashed line shows the bulk proton conductivity of BaZr0.9Y0.1O3−δ.51 (b) Comparison to literature data. Open symbols = DC measurements with proton-selective layer: BGLC: BaGd0.3La0.7Co2O6−δ,36 LaSrNi: La1.2Sr0.8NiO4,38 La2Ni: La2NiO4.37,38 Filled symbols = hydrogen permeation: BCFZr: BaCo0.4Fe0.4Zr0.2O3−δ, BCFY: BaCo0.4Fe0.4Y0.2O3−δ,40 BCFZrY: BaCo0.4Fe0.4Zr0.1Y0.1O3−δ,39 BCFZnY: BaCo0.4Fe0.4Zn0.1Y0.1O3−δ,55 D-BFZr: Ba0.875Fe0.875Zr0.125O3−δ.14 |
Fig. 4b compares the present of BLF and BLFY to literature data of triple-conducting perovskites and perovskite-related materials. The spread by 6 orders of magnitude reflects not only the pronounced variation of proton transport with materials composition, but also the fact that such measurements of a minority carrier in a triple conducting materials are challenging.
Fig. 5a shows the total bulk conductivity of BLFY measured over the extended pO2 range that can be covered in the oxygen pumping cell. At high pO2 the total conductivity is mainly dominated by electron holes (h˙) and almost temperature-independent. The plateau in the intermediate pO2 range corresponds to the conductivity of oxygen vacancies; iron is completely in 3+ oxidation state and electronic transport involving Fe4+ (holes h˙) or Fe2+ (electrons e′) falls below the conductivity. With decreasing pO2, n-type electronic conductivity dominates. The respective data for BLF in Fig. S8a† also exhibit an extended pO2-independent plateau from which
can be extracted. The Arrhenius plot of
in Fig. 5b shows that BLFY has a significantly lower
conductivity compared to the Y-free material, and also a slightly increased activation energy. The BLF and BLFY activation energies for
of 0.9–1 eV (under conditions of fixed
concentration) are within the typical range encountered for perovskites,60 albeit at the upper end. When comparing with data for BaCo0.4Fe0.4Zr0.2O3−δ and BaCo0.4Fe0.4Y0.2O3−δ,61 also there the Y-containing material exhibits the lower conductivity.
![]() | ||
Fig. 5 (a) Total conductivity of BLFY as a function of pO2 measured in the oxygen pumping cell. (b) Arrhenius plot of oxygen vacancy conductivity of BLF and BLFY extracted from the plateau region. Grey symbols: ![]() ![]() ![]() ![]() ![]() ![]() ![]() ![]() |
The oxygen vacancy diffusivity is shown in Fig. 5c. Since the molar fraction of in the conditions of
extraction is identical for BLF and BLFY, the lower
for BLFY directly translates into lower
for the Y-doped material. This trend is similar to that observed for
in BaZr1−xYxO3−δ (DFT and KMC calculations63), where an increased Y concentration decreases the effective long-range
mobility owing to a combination of trapping effects and increased migration barriers. While Y3+ (ion radius 0.9 Å) is only moderately oversized relative to Zr4+ (0.72 Å) in BaZrO3, the size difference to Fe (Fe3+ 0.645 Å, Fe4+ 0.585 Å) in BaFeO3−δ is much larger, which may further aggravate the defect interactions and decrease the
mobility.64 DFT calculations indicate repulsion of
in the first sphere around Y3+, followed by attraction in the second sphere. For comparison, also
values for BaCo0.4Fe0.4Zr0.1Y0.1O3−δ are shown.59 They come close to the present BLF data, which might be related to the lower Y content compared to the present BLFY, and that the material contains cobalt which in perovskites often increases the
mobility.
![]() | ||
Fig. 6 Proton (symbols and solid lines) and oxygen vacancy conductivity (dashed lines) of BLF and BLFY in conditions where iron is predominantly in Fe3+ oxidation state. |
For a pore-free thin film air electrode, the positrode-air two phase boundary dominates the oxygen exchange kinetics (the contribution of the triple phase boundary is negligible). The proton transport through the electrode film and oxygen surface reaction are serial processes (Fig. 1b). Unless the film is extremely thick or its bulk proton conductivity very low, the typically large surface reaction resistance dominates clearly over the proton transport resistance within the film.
For porous triple-conducting electrodes on protonic electrolytes the situation becomes more complex as illustrated in Fig. 7. For simplicity we concentrate here on the case that the protonic electrolyte has a negligible transference number. This holds for typical Ba(Zr,Ce)(Y,Yb)O3−δ protonic electrolytes up to about 600 °C, cf. grey lines in Fig. 6 (the
conductivity in humidified operating conditions is much lower than the depicted
in dry conditions, see also).65 (If the
transference number becomes significant, this opens a parallel path in which the cell operates as a conventional
-conducting solid oxide device).
![]() | ||
Fig. 7 Sketch of a porous air electrode under slight cathodic bias, i.e. operating in oxygen reduction mode (for simplicity only one particle is shown; in an actual electrode these processes will typically extend over several particles (Fig. 1c), but this does not fundamentally change the picture). The electrolyte (grey) is assumed to be a pure proton conductor. |
The porous electrode has a region close to the electrolyte δO/H2O in which owing to of the triple-conductor protons can be transported through the grain interior of the particles to reach the gas/electrode two-phase boundary, and are directly involved in the reduction of O2 to H2O. This region can be treated analogously to a hole/
mixed conducting electrode on an oxide ion conducting electrolyte as done in the ALS model.21 We concentrate on the case that ion transfer at the electrolyte/electrode interface and gas diffusion are not limiting. For a mixed conductor with mobile oxygen defects (here
) and electronic defects on an oxide ion conducting electrolyte, the thickness δO of the active zone is co-determined by surface reaction kinetics
and bulk oxygen transport
according to21
![]() | (4) |
Factors in the order of unity such as symmetry factors and tortuosity are dropped; α is the specific surface area of the porous electrode, cO the concentration of regular oxide ions. If the surface kinetics is slow, then bulk oxygen transport occurs in the electrode material up to larger distances from the electrolyte to increase the active surface area, until the point is reached where resistive contributions from surface reaction and bulk transport become comparable. A mixed conductor of and electronic defects under DC bias develops a gradient in oxygen nonstoichiometry starting at the electrolyte/electrode interface, and δO represents the characteristic length of the nonstoichiometry decay.21 The overall reaction rate is proportional to
.
In order to apply this model to a hole/proton mixed conducting electrode on a protonic electrolyte, eqn (4) needs to be adapted (ESI Section 8†):
![]() | (5) |
This δO/H2O (red arrows in Fig. 6) would be the overall characteristic length of the active zone if no oxygen transport was possible within the electrode particles or along the particle surface (adsorbed and partially ionized atomic oxygen species on a largely ionic oxide surface do not necessarily have a high mobility).66 In materials with low proton conductivity (but unchanged surface rate constant ) this zone may become rather thin.
However, if the electrode material has also a perceptible conductivity, i.e. is a real triple conductor, the zone above δO/H2O will still feel the applied cathodic bias (ESI Section 9†). Then O incorporation occurs also in a certain region beyond δO/H2O such that protons are not involved directly in the surface reaction. But since the overall reaction is the reduction of O2 to H2O, the incorporated O needs to be transported towards the electrolyte (blue arrows in Fig. 7) to finally meet protons and desorb as H2O. This process expands the overall active area for the sluggish oxygen reduction reaction, and thus decreases the overall electrode resistance. As a first approximation we use the same expression for δO as in the ALS model in absence of humidity:
![]() | (6) |
Since both the reduction of O2 to water and to oxide ions require the kinetically difficult splitting of the strong OO double bond,
is used as a first approximation. The higher
of BLF and BLFY compared to their
yields a wider active zone δO/O2− for oxygen incorporation to oxide ions than δO/H2O for direct reduction to water immediately involving protons. It needs to be kept in mind that each oxide ion incorporated into the triple conductors in the upper zone of the electrode still needs to combine with protons, i.e. the resistance of this reaction path still has a serial contribution from proton transport.
For a numerical example, we take α = 30000 cm−1 for the specific surface area of a representative porous electrode, and
(k* of a pore-free Ba0.5Sr0.5Co0.8Fe0.2O3−δ film67). This yields δO/H2O = 2 μm, δO/O2− = 11 μm for BLF, and δO/H2O = 1 μm, δO/O2− = 2 μm for BLFY with moderately lower
but strongly decreased
. Thus, the total width of the active zone is significantly extended by
the conductivity of the triple-conducting air electrode material. This extension is larger for higher
ratios, i.e. for comparable
and
values, the materials with higher is expected to show better performance. However, an increase of
at expense of
is not recommended as it would decrease δO/H2O.
The value of k* = 10−6 cm s−1 at 500 °C is at the upper end of typical k* values (but found also for uncontaminated La0.8Sr0.2(Co,Fe)O3−δ films68). For dense BaCo0.4Fe0.4Zr0.2−xYxO3−δ ceramics, k* values around 10−8 cm s−1 were obtained at 500 °C.59 Using this lower k* increases δO/H2O, δO/O2− from eqn (5) and (6) by one order of magnitude, but does not change the ratio between them. Such extended δO/H2O, δO/O2− values imply that the active zone comprises several triple-conducting electrode particles (only for graphical simplicity, the scheme in Fig. 7 uses a single particle). The ALS model in ref. 21 and 69 already implicitly considers an extension over several electrode particles. As long as the active zone width does not exceed the thickness of the porous electrode, the overall model remains unchanged. The grain boundaries of triple-conducting electrode particles typically do not show pronounced blocking effects for protons or .70
While for simplicity we considered here the direction of oxygen reduction, similar considerations hold also for the water oxidation to O2 because of microscopic reversibility (for not too large driving forces). Overall, apart from electrode morphology (specific surface area etc.) the resistance of a triple-conducting porous electrode on a proton-conducting electrolyte will be co-determined by ,
, and
,
.
Finally, we want to mention further aspects relevant for positrode kinetics in protonic ceramic cells. (i) Under anodic bias, the enhanced oxygen chemical potential in the active region71 may decrease the degree of hydration and correspondingly also , because many triple conductors exhibit a detrimental defect interaction between electron holes and protons.24,28 Typically, in electrolysis mode increased steam concentrations are applied which may compensate this effect.
(ii) For more detailed insight into the kinetics of porous positrodes on protonic electrolytes including proton and current distribution, numerical modelling accounting for transport of all three carriers and surface reaction coefficients
,
is expected to be helpful (including also the nonideal dependence of
on local μO).
(iii) The determination of surface reaction coefficients for positrodes on protonic electrolytes comes with its own challenges. For porous electrodes, the fact that both δO/H2O and δO/O2− regions contribute to the active area (and might vary with local μO) causes perceptible uncertainty when attempting to extract
,
values from measured overall reaction resistances. On the other hand, measurements on pore-free model electrodes with well-defined geometry which proved very useful for positrodes on oxygen ion conductors (e.g.71,72) encounter a specific issue in the case of protonic ceramic electrolytes. In contrast to Y-stabilized ZrO2, Ba(Ce,Zr,Y,Yb)O3−δ electrolytes develop a perceptible electronic transference number when exposed to oxidizing conditions on both sides (half-cells in symmetrical oxidizing atmosphere) at elevated temperature.35 When the true electrode resistance becomes comparable to the electronic resistance of the electrolyte-which may easily happen for pore-free electrodes because of their lower active area-the measured apparent electrode resistance approaches the latter instead of the true electrode surface reaction resistance.26,73
The width of the electrochemically active zone of a porous triple-conducting positrode on a purely protonic electrolyte is estimated based on adapting the Adler–Lane–Steele model. For BLF and BLFY, the zone width for direct reduction of O2 to water is in the range of 1–2 μm. However, owing to there is a more extended upper part of the positrode in which under cathodic bias oxygen is incorporated as oxide ions, which are subsequently transported towards the protonic electrolyte and finally also combine with protons to desorb as H2O. This process enhances the overall oxygen reduction rate, but relies also on proton transport within the triple-conductor (for a more detailed picture, numerical modelling is required).
These findings indicate that to improve materials for porous positrodes, proton and conductivity as well as the effective surface rate constant for oxygen reduction need to be optimized together, not at expense of each other. This differs from the situation of a pore-free electrode film, for which oxygen reduction at the surface can proceed only with immediate proton participation to directly form H2O, i.e. oxide ion conductivity is not decisive for steady state operation. For the surface kinetics, operation in atmospheres with high humidity represents a particular challenge because adsorbed OH species may largely poison reactive sites such as oxygen vacancies. Multi-phase electrode materials (e.g. from exsolution or surface decoration) exposing also less hydrophilic surfaces might be one approach to overcome this obstacle.
For H/D isotope exchange, the sample was pre-hydrated in pH2O = 20 mbar for extended time at the planned exchange temperature (7 days for the 400 °C experiment; for the 300 °C experiment the hydration was performed in three steps with decreasing temperature: 3 days 400 °C, then 3 days 350 °C, then 10 days 300 °C), quenched, and then exposed to pD2O = 20 mbar for the desired exchange time. After D2O hydration or H/D exchange the samples were embedded in a Cu: PMMA resin (Technovit 5000), cut and polished such that SIMS line scans can be recorded in the direction perpendicular to the D2O-exposed surface (more details in Fig. S4a†). Between processing steps, the resin-embedded sample was stored in a −18 °C freezer.
![]() | (7) |
Proton conductivity was calculated from the proton/deuteron diffusivities in Fig. 3 using the Nernst–Einstein equation
![]() | (8) |
Inserting the respective proton concentrations from thermogravimetry (Fig. S3†). Proton and deuteron diffusivities differ by a factor which is typically not larger than ≈1.5 (ESI Section 5†). In lack of precise information of the exact H/D isotope effect in BaFeO3-based triple-conducting perovskites, we use the deuteron diffusivities from and the H/D interdiffusion coefficients (stars in Fig. 3) without further correction factor as proxy for
. Within the unavoidable scatter within the present experiments, and the even larger variation of proton conductivities for closely related materials but measured with different methods (Fig. 4b) this approximation is considered acceptable.
If a material such as BLFY shows trapping of protons, then the diffusivity extracted from the SIMS line profiles corresponds to an effective diffusivity including the proton trapping factor χ which for this specific situation is a constant factor (cf. Section 4 in the ESI†). Using this Deff in the Nernst–Einstein equation together with the total proton concentration
from thermogravimetry (free and trapped protons) gives the correct proton conductivity because
yields the concentration of untrapped protons (ESI Section 6†).
Two-point impedance measurements were performed with an Alpha-A frequency response analyzer (Novocontrol, Germany) using voltage sinusoids of 20 mV (rms) amplitude between 10 MHz and 1 or 0.1 Hz. Ca. 100 nm Pt was sputtered on both sides of the samples as electrodes. As it is typical for this type of mixed conducting perovskites, the samples exhibited only a bulk semicircle at high frequencies, and-also depending on gas atmosphere-a low frequency arc that is attributed to the electrode response (i.e. no sign of blocking grain boundaries).
Footnote |
† Electronic supplementary information (ESI) available. See DOI: https://doi.org/10.1039/d5ta03014e |
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