Sulfur Poisoning and Performance Recovery of SOFC Air Electrodes

Introduction

The need for enhancement in the efficiency and durability of solid oxide fuel cells (SOFC) has stimulated extensive research. Cathode degradation is known to account for the largest portion of the electrochemical losses during long-term SOFC operation (Yokokawa, 2015). A number of studies have reported on the fundamental understanding of SOFC cathode degradation and approaches to minimize the impact of cathode degradation (Simner et al., 2006; Liu et al., 2009, 2012; Zubair et al., 2014; Yang et al., 2017). The main causes of the cathode degradation include microstructure coarsening, phase separation, chemical interaction with electrolyte, delamination at electrode/electrolyte interfaces, and poisoning by airborne contaminants (Chen et al., 2016).

Sulfur dioxide (SO₂) is one of the commonly present representative impurities in addition to Cr vapors (Horita et al., 2009; Hong et al., 2020). Although the concentration of SO₂ is very low in air (75 ppb for hourly primary standard) (National Ambient Air Quality Standards by US Environmental Protection Agency, 2010), the long-term exposure of the cathode to air flow can lead to contaminant deposition and reaction, degrading the cathodic activity for oxygen reduction reaction (ORR) (Singh and Birks, 1978; Mori et al., 2015). Particularly, LSCF is considered vulnerable to sulfur poisoning as the surface-segregated SrO is prone to react with SO₂ forming SrSO₄ (Mori et al., 2015; Yu et al., 2016; De Vero et al., 2018). The airborne SO₂ also contaminates LSM electrodes, although the effect may not be as severe as on LSCF (Liu et al., 2011; Daio et al., 2016). The degradation caused by SO₂ is slow but continuous and severe in the long term. Higher concentrations of SO₂ (0.1, 1, 10, and 100 ppm) showed an accelerated degradation in the SOFC performance (Wang et al., 2020).

The effect of SO₂ on electrode performance degradation has been extensively studied experimentally by maintaining the SO₂ concentration constant during the experiments. However, under the real SOFC operating condition, the SO₂ concentration may fluctuate depending on the ambient atmospheric conditions. The irreversible or recoverable nature of the performance loss, caused by sulfur poisoning when SO₂ concentration is reduced, remains largely unknown. In this paper, we present the findings of our study on the reversibility of sulfur poisoning and recovery of the state-of-the-art air electrodes, i.e., (La₀.₈₀Sr₀.₂₀)₀.₉₅MnO_3±δ (LSM) and (La₀.₆₀Sr₀.₄₀)₀.₉₅Co₀.₂₀Fe₀.₈₀O_3–δ (LSCF), in alternating atmospheres of air and SO₂-air. Their poisoning and recovery mechanisms were elucidated by the electrochemical impedance spectroscopy (EIS) analysis. The accompanying structural evolution and the surface chemistry of LSM and LSCF during exposure to the alternating atmosphere were also investigated using the SEM, XRD, and Raman spectroscopy. The results show that the difference in performance degradation and recovery behavior of LSM and LSCF electrodes is attributed to the presence of SrO and chemical activity of Sr in the electrodes at the solid-gas interface.

Materials and Methods

Operando Electrochemical Analysis

For electrochemical tests, electrolyte-supported solid oxide cells with LSCF and LSM electrodes were prepared (Hong et al., 2020). Gd-doped ceria (GDC; Gd₀.₁₀Ce₀.₉₀O₁.₉₅; Fuelcellmaterials, United States) and yttria-stabilized zirconia (YSZ; 8 mol.% yttria; Fuelcellmaterials, United States) button electrolytes with a diameter of 25 mm were used as supports (La₀.₆₀Sr₀.₄₀)₀.₉₅Co₀.₂₀Fe₀.₈₀O_3–δ (LSCF; Fuelcellmaterials, United States) and (La₀.₈₀Sr₀.₂₀)₀.₉₅MnO_3±δ (LSM; Fuelcellmaterials, United States) inks were screen-printed on the GDC and YSZ electrolytes, respectively, followed by firing at 1,200°C for 2 h (3°C min^–1). The electrode areas were 0.785 cm² and the electrode thicknesses were ∼10 μm. The thin electrode could result in a lower performance (Barbucci et al., 2008), but it would not affect the overall trend of the results here. Pt paste (ESL Electroscience) was applied to the opposite side as a counter electrode. Each electrode surface was attached to the Pt mesh as a current collector. The as-prepared LSCF|GDC|Pt and LSM|YSZ|Pt cells were mounted on alumina tubes with an alumina paste (Zircar Ceramics Inc., United States). A type-K thermocouple was set up close to the cell to monitor and read the exposure temperature accurately. The mounted cells were electrically connected to a potentiostat (VMP3, Bio-Logic, France). An alumina cap was placed over the assemblage to seal the whole assemblage. For details, refer to Ref. (Heo et al., 2019; Hong, 2020). The cell assembly was subsequently inserted in a furnace and heated up at 700°C (3°C min^–1). The electrochemical impedance spectroscopy (EIS) spectra, as well as the current change, were recorded under a bias of 0.5 V in the frequency range of 0.5 Hz to 200 kHz with a 10 mV sinus amplitude at an interval of 1 h. During the measurement, air (Ultra zero grade; 2 ppm H₂O; Airgas, Inc.) and 4 ppm SO₂ (air balance; <3 ppm H₂O) were alternately supplied to the air-electrode side at 120 mL min^–1, for which 10 ppm SO₂ (air balance; <3 ppm H₂O; Airgas, Inc.) and air (Ultra zero grade; 2 ppm H₂O; Airgas, Inc.) gases were blended using a gas mixing system (Series 4000, Environics, United States), while air was injected to the counter electrode side at 120 mL min^–1. The recorded impedance spectra were further processed by a distribution of relaxation times (DRT) analysis (Wan et al., 2015) to better understand the physicochemical process on electrodes.

Characterization

The cross sections of the LSCF/GDC and LSM/YSZ cells, which were exposed to alternating atmospheres of 4 ppm SO₂ and air during the electrochemical test, were observed and analyzed using the field-emission scanning electron microscopy (FE-SEM; Quanta 250 FEG, FEI, United States) equipped with energy dispersive X-ray spectrometry (EDS). Furthermore, LSCF and LSM, layered on YSZ substrates, were exposed to alternating atmospheres of 1 ppm SO₂ (air balance) and air at 700°C for 400 h. Their structural changes were then investigated using the SEM, Raman spectroscopy (Ramanscope 2000, Renishaw, Gloucestershire, United Kingdom) with a laser of 514.5 nm wavelength, and X-ray diffractometer (XRD; D8 Advance, Bruker, Germany) with Cu Kα radiation (λ = 0.1542 nm).

Results

EIS Study of Sulfur Poisoning and Recovery of LSM and LSCF

Total, ohmic, and polarization resistances of LSCF|GDC and LSM|YSZ half cells at 700°C in alternating atmospheres of air and 4 ppm SO₂ are displayed in Figure 1. Their corresponding impedance spectra are exhibited in Figures 2, 3. For the LSCF|GDC cell, the resistance is initially constant in air (Figure 1A: 0–36 h) while the impedance spectra remain constant (Figure 2A: 1–30 h). As SO₂ gas (4 ppm; air balance) is supplied to the LSCF electrode (at 36 h), the impedance arcs are enlarged and the high-frequency x-intercept shifts to the right (Figure 2A: 1–50 h), indicating the increase in the polarization (R_p) and ohmic (R_Ω) resistances, respectively.

FIGURE 1

Figure 1. Ohmic, polarization, and total resistances (R_Ω, R_P, and R_T, respectively) of (A) LSCF|GDC half-cell for ∼360 h at 700°C in alternating atmospheres of air (0–36 h and 215–358 h) and 4 ppm SO_{2 (g)} (air balance) (36–215 h), and those of (B) LSM|YSZ half-cell for ∼530 h at 700°C in alternating atmospheres of air (0–60, 159–268, and 354–528 h) and 4 ppm SO_{2 (g)} (air balance) (60–159 and 268–354 h). The corresponding current densities are displayed in Supplementary Figure 1.

FIGURE 2

Figure 2. Nyquist and bode plots of LSCF|GDC|Pt cell measured for ∼360 h at 700°C in alternating atmospheres of air (0–36 and 215–358 h) and 4 ppm SO_{2 (g)} (36–215 h): (A) 1–50 h, (B) 50–213 h, and (C) 213–348 h.

FIGURE 3

Figure 3. Nyquist and bode plots of LSM|YSZ|Pt cell measured for ∼530 h at 700°C in alternating atmospheres of air (1–58, 158–266, and 353–474 h) and 4 ppm SO_{2 (g)} (58–158 and 266–353 h): (A) 1–58 h, (B) 58–158 h, (C) 158–266 h, (D) 266–353 h, and (E) 353–474 h.

The continuous exposure of the LSCF electrode to SO₂ further degrades the electrochemical performance; both the ohmic and polarization resistances continue to increase (Figure 1A: 36–213 h; and Figure 2B: 50–213 h), indicating the vulnerability of LSCF to SO₂. For a deeper understanding of the physicochemical process during sulfur poisoning and recovery, DRT transformation is performed. DRT analysis has been frequently used, especially in SOFCs, for EIS data interpretation as it allows for deconvolution in a simple way (Wan et al., 2015), compared with the conventional non-linear least square fitting that requires an accurate equivalent circuit model. Figure 4 shows the DRT spectra composed of four main signals (denoted as P1–P4) at different frequency ranges. For LSCF exposed to SO₂ (Figure 4A), all four signals increase overall. In particular, the rise of the low-frequency signal at 10^–2–10⁰ Hz (P4) is remarkable. This indicates the occurrence of physi- and chemisorption of SO₂ on the LSCF surface, inhibiting the catalytic activity for oxygen reduction reaction (ORR), given that the low-frequency response (<1 Hz) is related to O₂ adsorption, reduction, and dissociation into O^2– on air-electrodes (Yang et al., 2000, 2001; Adler, 2004). The increase of high-frequency signal at >10⁴ Hz (P1) is also noticed, which is associated with oxygen ion transport at the cathode/electrolyte interface. The sulfur absorption would lead to SrSO₄ formation and subsequently to Co-Fe exsolution (Wang et al., 2013; De Vero et al., 2018; Budiman et al., 2019). Such structural change near the LSCF/GDC interface is known to switch and elongate the ionic transport pathways, increasing the high-frequency resistance (P1 or R_Ω) (Wang F. et al., 2016).

FIGURE 4

Figure 4. DRT plots of the EIS spectra of (A,B) LSCF|GDC and (C,D) LSM|YSZ half-cells exposed to alternating atmospheres of air and 4 ppm SO_{2 (g)}.

The reversibility of sulfur poisoning and recovery for LSCF is then explored, for which the SO₂ gas flow is switched back to air. Immediately after the air flow, the resistance decreases back, but just slightly (Figure 1A: >213 h). Noticeable changes are found in the Nyquist plots (Figure 2C: 213–348 h). The Nyquist arcs shift to the left and shrink over time, indicating the decrease in both ohmic and polarization resistances, respectively. DRT analysis in Figure 4B shows that both the low- and high-frequency components at 10^–2–10⁰ and >10⁴ Hz (P1 and P4) largely decrease, whereas the intermediate frequency components at 10^–2–10⁴ Hz (P2 and P3) remain relatively unchanged. In principle, the low- and mid-frequency impedances are associated with the surface diffusion of adsorbed oxygen and the bulk diffusion of oxygen ions in air-electrodes, respectively, while the high-frequency impedance is related to the oxygen ion transfer through electrolytes (Adler et al., 1996; Yang et al., 2000, 2001; Adler, 2004; Lang et al., 2008; Nielsen and Hjelm, 2014). It is suggested that the surface LSCF structure, modified by sulfur incorporation, partially returns to its original structure in flowing air, which may include the desorption of SO₂ from LSCF and partial dissolution of exsolved (Co,Fe)O_x. The modified bulk structure, however, is not restored as identified by the comparison of the Nyquist curves before and after the recovery process (see superimposed curves in Supplementary Figure 2B). Further discussion is presented in the following section with a surface morphological analysis performed by SEM.

As for the LSM|YSZ cell, the resistances (R_Ω, R_P, and R_T) decrease for the first 30 h and then becomes constant in air (Figure 1B: 0–58 h) while the corresponding Nyquist curve shrinks and shifts to the left (Figure 3A), indicating the electrode activation and stabilization. The SO₂ gas (4 ppm; air balance) is then fed to the LSM electrode at 59 h for sulfur poisoning. As a result, the polarization resistance soars (Figure 1B: 58–158 h) while the Nyquist arc is enlarged (Figure 3B: 58–158 h). These would be caused by SO₂ adsorption on the LSM electrode surface. As the active sites for ORR and oxygen ion transfer in LSM are concentrated at triple phase boundaries (TPBs) between air, electrolyte, and electrode (Gong et al., 2012; Huber et al., 2014; Pakalapati et al., 2014), it is considered that the area contaminated with SO₂ includes the LSM near the TPBs. Unlike the case of LSCF, the ohmic resistance is not affected by SO₂ exposure and the polarization resistance no longer increases after the initial ascent within ∼35 h (58–93 h), thus implying the chemical stability of LSM electrode to SO_2(g).

The reversibility of sulfur poisoning and recovery for LSM is also investigated, for which the supplied SO_2(g) is replaced by air. Immediately after air flow, the polarization resistance is reduced, eventually being close to its initial value, ∼0.5 Ω cm² (Figure 1B: 158–266 h, and Figure 3C: 158–266 h), which indicates the recovery of the electrochemical performance of the LSM|YSZ cell. DRT plots in Figures 4C,D show the same trend for the restoration. The signals (P1–P3), which were increased in the presence of SO₂, are reduced in the absence of SO₂ and returned to their original levels. As with the first cyclic test, the electrochemical performance, secondarily degraded by sulfur poisoning (Figure 3D: 266–353 h), is restored again in airflow (Figure 3E: 353–474 h). The observations confirm that, for sulfur-poisoned LSM, the performance recovery is almost reversible. The original and recovered impedance plots (58 and 266 h) are displayed in Supplementary Figure 2A for comparison. It appears that the high-frequency x-intercept (R_Ω) is shifted by 0.23 Ω cm² (from 1.51 to 1.74 Ω cm²) whereas the impedance arc diameter (R_p) is rarely changed (from 0.27 to 0.34 Ω cm²). The R_Ω increase could be attributed to the formation of poorly conductive secondary phases such as SrSO₄ on the LSM surface and La₂Zr₂O₇ at the electrode/electrolyte interface (Mitterdorfer and Gauckler, 1998; Chen et al., 2009, 2010). It is also observed that a very small impedance arc in the low-frequency range (10⁰–10¹ Hz) was formed, which is likely to contribute to the R_p increase (Supplementary Figure 2A). As the low-frequency impedance is related to oxygen adsorption and diffusion near the surface, the LSM surface modified by sulfur poisoning may affect the slight increase in R_p. The above predictions from EIS results will be verified by post-test characterization in the following section.

Structural Modification of LSCF and LSM in Cyclic Conditions

Figure 5 shows SEM images of the cross section of LSCF|GDC cell exposed to alternating atmospheres of air and 4 ppm SO_2(g) for ∼360 h during the electrochemical test. The nanostructure of LSCF appears to change significantly. The LSCF particle surface has numerous nano-bumps indicative of Sr exsolution (Figure 5A), which was not initially present (Figure 6B). The nano-bumps are likely to be sulfur compounds such as SrSO₄, based on previous research (Hong et al., 2019). Correspondingly, as can be seen in Figure 5B, the EDS spectrum from the LSCF particle with the surface nanoparticles (Region 2), shows a higher sulfur concentration than that from the LSCF particle core (Region 1). The SrSO₄ formation can lead to Co/Fe exsolution, for example, CoFe₂O₄ formation (Wang et al., 2013; De Vero et al., 2018; Budiman et al., 2019). Indeed, the Raman analysis identifies a characteristic peak for the Co₃O₄ phase (Na et al., 2012), from a LSCF specimen that was exposed to alternating atmospheres of air and 1 ppm SO₄ (Figure 7B), further discussion of which will be presented below. Such structural changes are well agreed with the electrochemical performance degradation shown in Figures 1, 2. Therefore, it is indicated that the LSCF structure, once modified by sulfur poisoning, cannot be structurally recovered in air flow.

FIGURE 5

Figure 5. (A) SEM image of the cross section of the LSCF/GDC cell exposed to an alternating atmosphere of air and 4 ppm SO_{2 (g)} for ∼360 h at 700°C during the electrochemical test. (B) Elemental composition (La, Sr, Co, Fe, and S) of LSCF particles measured by EDS (on the core and surface).

FIGURE 6

Figure 6. SEM images of (A) LSM and (B) LSCF particles exposed to an alternating atmosphere of air and 1 ppm SO₂ (air balance) for 400 h at 700°C.

FIGURE 7

Figure 7. Raman spectra of (A) LSM and (B) LSCF exposed to an alternating atmosphere of air and 1 ppm SO₂ (air balance) for 400 h at 700°C.

Figure 8 shows the morphology of the fractured cross section of LSM|YSZ cell, which was exposed to alternating atmospheres of air and 4 ppm SO_2(g) for ∼530 h during the electrochemical test. The LSM particles appear to have smooth surfaces with no evidence of Sr exsolution and SrSO₄ formation (Figure 8A). It should be noted that in our previous study (Hong et al., 2019), an LSM|YSZ cell, exposed to 4 ppm SO₂ for 120 h but without subsequent exposure to air flow, has sulfur-enriched nanoparticles (regarded as SrSO₄) protruding on the surface. It is thus indicated that, in the subsequent air flow, the sulfur physi/chemisorbed on the LSM surface is released while the strontium is partially dissolved back into LSM. This result corresponds to the electrochemical performance restoration of the LSM|YSZ cell (Figure 3). Even after the recovery process, however, a few particles appear to have a different morphology such as cylindrical columns (Figure 8B), which contain a higher concentration of sulfur than the granular particles (see the elemental compositions of three selected regions of the LSM electrode, tabulated in the inset of Figure 8B). Such irreversible morphology change could be the cause of the incomplete recovery of the electrochemical performance of LSM (Supplementary Figure 2A). When the partial pressure of SO₂ is as low as 75 ppb [in ambient air; primary standard (National Ambient Air Quality Standards by US Environmental Protection Agency, 2010)], though, the sulfur poisoning and recovery might be a completely reversible process.

FIGURE 8

Figure 8. (A) SEM image of the cross section of the LSM/YSZ cell exposed to an alternating atmosphere of air and 4 ppm SO_{2 (g)} for ∼530 h at 700°C during the electrochemical test. (B) Elemental composition (La, Sr, Mn, and S) of LSM particles measured by EDS (on the core and surface).

To further understand the restoration of the electrochemical performance of sulfur-contaminated LSM and LSCF electrodes, the structural evolution of LSM and LSCF, exposed to alternating atmospheres of 1 ppm SO₂ (air balance) and air at 700°C, is investigated using the SEM, XRD, and Raman spectroscopy. Figure 6 shows the nanostructure changes of LSM and LSCF during the exposure. As for LSM, nanoparticles have formed on the surface in SO₂ flow, possibly due to Sr exsolution forming SrSO₄ (Figure 6A: as-prepared, and 0–100 h). In the subsequent air flow, the number and size of the nanoparticles decreased a little but they still exist, indicating the partial dissolution of exsolved-Sr back into LSM releasing SO₂ (Figure 6A: 100–200 h). After the second exposure to SO₂, the nanoparticle size is enlarged, indicating further Sr exsolution (Figure 6A: 200–300 h). In the subsequent air flow, the particle size appears decreased but slightly bigger than that of the first cycle (Figure 6A: 300–400 h). However, any structural change is not found by the XRD and Raman spectroscopy as shown in Figures 7A, 9A, implying that the structural change of LSM by sulfur poisoning is confined to the very surface.

FIGURE 9

Figure 9. X-ray diffraction patterns of (A) LSM and (B) LSCF exposed to an alternating atmosphere of air and 1 ppm SO₂ (air balance) for 400 h at 700°C, where YSZ was used as a substrate to support the thin LSM and LSCF layers.

In the case of LSCF, the nanostructure change associated with sulfur poisoning is more significant. In SO₂ flow, the initially smooth surface becomes rough and covered with numerous exsolved nanoparticles and angular particles [possibly SrSO₄ (Wang et al., 2014, 2015)], marked by arrows in Figure 6B: as-prepared, and 0–100 h. After subsequent exposure to air, most of the angular particles disappeared, but the surface remains still rough (Figure 6B: 100–200 h). It is indicated that the surface SrSO₄ could be partially decomposed in air flow while the strontium dissolves into LSCF. When the LSCF is again exposed to the alternating atmosphere, the same changes occur in the nanostructure (Figure 6B: 200–300 and 300–400 h). However, the structural change for sulfur poisoning and recovery in LSCF is not a reversible process, based on the electrochemical test results in Figures 1A, 2. The irreversible process could be due to the phase separation of LSCF, for instance, Co/Fe exsolution subsequent to SrSO₄ formation (Cai et al., 2012; Wang et al., 2013). Raman spectroscopy identifies a characteristic peak at ∼685 cm^–1 (Figure 7B) corresponding to an octahedral vibration mode (A_1g) of Co₃O₄ phase (Na et al., 2012), indicative of Co(Fe) exsolution. In the case of Co₃O₄ phase in LSCF, similar to other studies (Upasen et al., 2015; Li et al., 2018), only the signal for A_1g mode is distinctive over the other four Raman modes at 190.8 (F_2g), 478.6 (E_g), 519.2 (F_2g), and 616.6 (F_2g) of Co₃O₄, which may be attributed to a spinel-type Co/Fe oxide formation (Benson et al., 1999; Diallo et al., 2015). Correspondingly, the doublet peaks at around 40°, 58°, and 68° for perovskite LSCF in the XRD patterns are slightly modified in the intensity over time (Figure 9B). This is indicative of Sr/Co/Fe exsolution because a decreasing strontium content can cause [Co(Fe)O₆] octahedra distortion and lattice structure transformation from pseudo-cubic to rhombohedral (Deganello et al., 2007; Guo et al., 2021).

Discussion

The experimental findings show two different behaviors of the electrochemical performance degradation and recovery of LSCF and LSM electrodes in the alternating atmospheres of air and SO₂-air at 700°C. Particularly for LSM, the performance degradation due to sulfur poisoning was almost completely restored in the subsequent air flow, whereas the performance deterioration of LSCF partially recovered, indicating the high stability of LSM to SO₂ contaminant. Electrochemical and post-test characterizations elucidate the sulfur poisoning and recovery process.

Figures 10A–C illustrates a schematic diagram of the process of sulfur poisoning and recovery for the LSCF electrode. Basically, for LSCF at high temperatures (>500°C), strontium tends to exsolve from the A-site of perovskite LSCF, forming SrO on the surface (Figure 10A; Lee et al., 2013; Koo et al., 2018). Because of the high affinity of SrO with SO_2(g), the SrO on the surface absorbs and reacts with airborne SO₂, forming SrSO₄ (Figure 10B). The SrSO₄ covering the LSCF surface interferes with oxygen reduction reaction at the surface, increasing polarization resistance (R_p). The SrSO₄ formation leads to the loss of Sr in (La,Sr)(Co,Fe)O₃ perovskite and thereby the segregation of Co and Fe, such as the exsolution of Co₃O₄ (Figure 7B) and CoFe₂O₄ (Wang et al., 2013; De Vero et al., 2018; Budiman et al., 2019). This phase separation of LSCF (LSCF→LSCF + SrSO₄ + CoFe₂O₄) could reduce the electric conductivity and/or increase the length of oxygen diffusion path, thereby increasing the ohmic resistance (R_Ω) as well as the polarization resistance (R_p) (Figure 10C). When the sulfur-contaminated LSCF is subsequently exposed to air flow, the SO₂ absorbed on the LSCF and incorporated in SrSO₄ could be partially released out, whereas the exsolved Co and Fe in each LSCF particle is unlikely to be dissolved back into LSCF at the relatively low operating temperature (700°C), resulting in the incomplete performance recovery for LSCF. In conclusion, the recovery of the structural change and degradation by sulfur poisoning for LSCF cannot be sufficiently achieved as the sulfur poisoning significantly transforms the LSCF structure.

FIGURE 10

Figure 10. Schematic diagram of the sulfur poisoning and recovery process of the LSCF and LSM electrodes under the presence and absence of SO_{2 (g)}: (A) SO₂ absorption at SrO present on the LSCF particle surface, (B) SrSO₄ formation and Co-Fe exsolution over LSCF, (C) SO₂ desorption and partial dissolution of SrSO₄ and (Co,Fe)O_x onto LSCF under SO₂-free air flow, (D) SO₂ absorption on the Sr-terminated LSM particle surface, (E) SrSO₄ island formation on the LSM surface leaving a Sr-deficient LSM, and (F) SO₂ desorption and partial dissolution of SrSO₄ onto LSM under SO₂-free air flow.

The process of sulfur poisoning and recovery for LSM is displayed in Figures 10D–F. Unlike LSCF, LSM is thermally stable without A-site cation (i.e., Sr) exsolution at high temperatures (>500°C). However, in the presence of SO₂, Sr-terminated LSM surface is likely to interact with and absorb SO₂ forming SrSO₄ on the top surface of the LSM particles (Figure 10D), which hinders the oxygen reduction reaction. Nevertheless, the Sr exsolution accompanied by SrSO₄ formation is localized at the surface, yielding a Sr-deficient LSM in the vicinity of the surface, but which does not cause additional structural changes of LSM (Figure 10E). Correspondingly, the polarization resistance (R_p) increased, whereas the ohmic resistance (R_Ω) remains as it is (Figure 3). When the sulfur-contaminated LSM is subsequently exposed to air, the strontium of SrSO₄ partially dissolves back into LSM, releasing SO₂ (including physically adsorbed SO₂) to air (Figure 10F). Thus, the performance degradation (mainly R_p increase) of LSM mostly recovers, although the ohmic resistance slightly increases after the poisoning and recovery process. The minor increase in the ohmic resistance could be due to the formation of a poorly conductive SrSO₄ on the surface and to SrZrO₃/La₂Zr₂O₇ formation by interdiffusion of La/Sr and Zr at the electrode/electrolyte interface where the latter is a natural aging process in air (Mitterdorfer and Gauckler, 1998; Chen et al., 2009, 2010; Wang C.C. et al., 2016). Considering that the SO₂ concentration (4 ppm) used in this work is much higher than the actual concentration in ambient air (75 ppb), the reversible recovery of sulfur poisoning for LSM would be achievable in general cases.

Conclusion

The reversibility of sulfur poisoning and recovery of the LSCF and LSM air-electrodes have been investigated. It is proposed that, for Sr-containing perovskite air-electrodes, the chemical activity of Sr is a major factor that determines the structural stability and the reversibility of the recovery of sulfur poisoning. In the presence of SO₂, the catalytic activity of the electrodes for ORR decreases along with the polarization resistance increase in low-frequency regions. For LSCF, the SrO, segregated on the LSCF surface, has a tendency to absorb and react with SO₂. Thus, LSCF electrode particles absorb airborne SO₂ forming SrSO₄ followed by the exsolution of Co and Fe. In the subsequent exposure to air, the electrochemical performance of LSCF does not recover as the LSCF particles predominantly remain covered with SrSO₄ and Co/Fe oxides (e.g., Co₃O₄) nanoparticles. In contrast, for LSM, the absorption of SO₂ is limited to the Sr-rich areas of LSM, including the active reaction sites near the TPBs, leading to a sparse Sr exsolution with SrSO₄ formation and Sr-deficient LSM formation. Immediately after the subsequent exposure to air, the SO₂, loosely adsorbed on the LSM surface, is easily swept away while SrSO₄ is partially decomposed, releasing SO₂, and dissolving Sr into the bulk LSM, by which the electrochemical performance is mostly restored. Although minor, the ohmic resistance slightly increased because of Sr-deficiency in LSM and the presence of a poorly conductive SrSO₄. Considering the high SO₂ concentration (4 ppm) used in this work, the reversible recovery of sulfur poisoning is achievable for LSM in ambient air. The result also shows the potential application of LSM for a sulfur sensor available in high-temperature harsh conditions.

Data Availability Statement

The original contributions presented in the study are included in the article/Supplementary Material. Further inquiries can be directed to the corresponding author.

Author Contributions

The results presented here are based on part of the author JH’s doctoral dissertation. All authors extensively discussed the results, reviewed the manuscript, and approved the final version of the manuscript to be published.

Funding

This work was financially supported by a federal grant (DE-FE 0023385) from the United States Department of Energy (DOE) and National Energy Technology Laboratory (NETL).

Conflict of Interest

The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

Supplementary Material

The Supplementary Material for this article can be found online at: https://www.frontiersin.org/articles/10.3389/fenrg.2021.643431/full#supplementary-material

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