Degradation indicators for the PEMs, CLs, and GDLs in the MEAs
The degradation of PEMs and CLs can be detected by an electrochemical reaction; PEMs and CLs are indexed by their open-circuit voltage (OCV) and electrochemically active surface area (ECSA) values, respectively. In contrast, GDL degradation is generally difficult to assess separately based on the electrochemical properties. This study identifies the degradation rate of GDLs via water saturation using operando synchrotron X-ray radiography29. Operando cells equipped with resin-impregnated graphite block separators30 are typically used for rib/channel identification for radiographic measurements. In this study, metal separators were designed because carbon separators are not suitable for research involving carbon corrosion. The rib/channel geometry of the metal separator was not identified because of insufficient X-ray transmission, and only the morphology of the MEA sandwiched between the separators was visualized (Fig. 1a). The rib/channel positions were determined by referring to the markers placed on the metal separator. The liquid water in the MEAs could be visualized during power generation by recording the difference between the wet and dry states (Fig. 1b). Figures 1c and 1d show the transmitted X-ray intensity profiles along the x- and y-axes shown in Figs. 1a and 1b, respectively. The transmitted X-rays in the GDL exhibited a relatively high intensity and intensity differences within the GDL, including the components of the carbon fiber, interfacial layer, and MPL (Fig. 1c). The interfacial layer is defined as an MPL intrusion layer in the carbon fiber, which is typically formed during the coating process31. The transmitted X-rays in the GDL, except for the MPL, are attenuated at the cathode by the water produced during power generation. Therefore, the water thickness in the GDL can be quantified during power generation. In contrast, the incident X-rays were attenuated in the metal separator, CL, and PEM (Fig. 1c). The water saturation in the CL and the swelling ratio of the PEM were difficult to quantify because of insufficient X-ray transmittance. Recently, a carbon separator with a super-shortened X-ray path length was proposed for water visualization in the PEM and cathode CL32; however, metal separators with low X-ray transmittance could not be applied. The transmitted X-rays under the ribs were attenuated by the produced water (Fig. 1d); these results are consistent with those widely reported in previous studies30,32–36. The obtained water thickness in the GDL was converted to water saturation using the GDL porosity (0.61) calculated by considering the compression state37 (compressed to 130 µm from the initial thickness of 215 µm from the transmission image) from the initial porosity (0.7731). To simplify the discussion, the water saturation in the cathode GDL under the ribs was calculated by averaging over three components (carbon fiber, interfacial layer, and MPL) and was used as the degradation indicator.
Load cycle AST
AST simulating load cycles was recorded by applying rectangular potential cycles between 0.6 and 0.95 V (Fig. 2a). Figures 2b and 2c show the cyclic voltammograms (CVs) during the AST and the I–V curves at the beginning-of-life (BOL) and end-of-life (EOL), respectively. The OCV, ECSA, current (0.2 V), and water saturation in the cathode GDL (under the ribs) normalized by their maximum values are shown in Fig. 2d. The OCV was almost constant throughout the measurements, and the PEM did not degrade under these conditions. The CVs curves showed typical butterfly shapes with hydrogen adsorption/desorption peaks (below 0.35 V) and Pt redox peaks (above 0.55 V), as shown in Fig. 2b. The ECSA, determined from the hydrogen adsorption peaks, decreased by 26% during the AST (Fig. 2d). In general, this parameter is affected by three phenomena: electrochemical Ostwald ripening, which is explained by the dissolution of Pt nanoparticles during oxidation and their redeposition on larger particles during reduction; particle coalescence induced by particle migration on the surface of the carbon support; and particle detachment from the carbon support38,39. For carbon-supported Pt nanoparticles, particle detachment is caused by the potential-driven oxidation of the carbon support. In the potential range of the AST (0.6–0.95 V), hydroxyl groups are adsorbed onto the surfaces of Pt at the cathode CL, producing carbon dioxide via carbon defects40.
C + H2O ↔ C–Oad + 2H+ + 2e– (1)
Pt + H2O ↔ Pt–OHad + H+ + e– (2)
C–Oad + Pt–OHad → CO2 + Pt + 2H+ + 2e– (3)
Along with a reduction in the ECSA, the I–V performance deteriorated at low current densities, which is related to the catalytic activity (Fig. 2c). In contrast, the deterioration of the I–V performance at high current densities was only 5.8% at 0.2 V (Figs. 2c and 2d). However, water saturation in the cathode GDL increased as the number of potential cycles increased (Fig. 2d), even though the current decreased (i.e., the amount of water produced decreased). Recently, Zenyuk et al. investigated the effect of the GDL on the CL durability41,42. They claimed that a higher liquid water flux due to the presence of MPL cracks in the GDL resulted in a more direct loss of dissolved Pt ions from the cathode CL during the durability test. The observed increase in water saturation did not have a significant negative impact on the I–V performance at high current densities; however, this water accumulation tendency may indirectly adversely affect water-mediated CL degradation.
Start-stop cycle AST
The durability of MEAs under high-potential conditions was tested by sweeping the potential between 1.0 and 1.5 V under an inert gas condition (Fig. 3a). Figures 3b and 3c show the CVs during the AST and the I–V curves at the BOL and EOL, respectively. The ECSA, OCV, current (0.2 V), and water saturation in the cathode GDL (under the ribs) normalized by their maximum values are shown in Fig. 3d. A decrease in the ECSA was observed up to 54% till 6,000 potential cycles (Fig. 3c). In addition, the electrical double layer was compressed during the AST. This is because of carbon corrosion occurring at the cathode CL. Depending on the type of carbon support, both the compression and expansion of the electrical double layer have been reported40,43. In many cases, the nonporous carbon black (Vulcan) (used in this study) reduces the electrical double layer under high-potential conditions owing to carbon corrosion. In the potential range of the AST (1.0–1.5 V), carbon corrosion was primarily caused by the chemical reaction with water at the cathode:
C + 2H2O → CO2 + 4H+ + 4e– (4)
After 7,000 potential cycles, the CVs were not properly recorded because of hydrogen leakage to the cathode through the PEM. The stability of the OCV was also affected by the leakage (Fig. 3d). A significant deterioration in I–V performance at both low and high current densities was observed after 10,000 potential cycles (Fig. 3c). Water saturation in the cathode GDL decreased as the number of potential cycles increased. This trend originated from the deteriorated I–V performance (i.e., less produced water). Eller et al.34 have reported that the current and water saturation in GDLs exhibit a linear relationship in the low-current-density region up to 2.25 A cm–2. The rate of decrease in water saturation was low compared to that in current (Fig. 3d), indicating that the produced water was more likely to accumulate in the cathode GDL during the AST, which in turn can be attributed to the reduced hydrophobicity of the aged GDL. The hydrophobicity loss in GDLs is closely associated with the loss of both carbon materials and PTFE in GDLs under oxidizing conditions25, chemically aged conditions26,27, and after real-time operations using a prototype vehicle28.
To verify the above assumption that higher liquid water saturation in the cathode GDL is derived from the loss of hydrophobicity, time-resolved liquid water distribution images are shown in Fig. 4. Sequential images captured at the BOL and EOL are shown in the Movies (Movies 1 and 2: load cycle AST at the BOL and EOL, respectively; Movies 3 and 4: start-stop cycle AST at the BOL and EOL, respectively). During the start-stop cycle AST, the absolute amount of water at the EOL was lower than that at the BOL because of the lower current value owing to degradation (Figs. 3d and 4a). In contrast, the dynamic behavior of the water clusters wetted in the cathode MPL, as indicated by the arrows in Fig. 4b, was observed at the EOL. During the operation of PEFCs, water produced and condensed at the cathode CL migrates to the carbon fiber through large pores or cracks in the hydrophobic MPL33–35. Water forms spherical droplets in carbon fibers44 and MPLs45 with a hydrophobic nature, wetted clusters46 in MPLs with hydrophilic additives, and a widespread wetted region47 in carbon fibers with a lower amount of PTFE. The wetted water clusters oscillated inside the cathode MPL with the hydrophobicity loss because of the reduced ability of the capillary force24 to discharge water from the MPL into the carbon fiber and eventually into the channels of the metal separator.
Water accumulation in the anode GDL under the ribs was also observed during the start-stop cycle AST (Fig. 4b, Movie 4). However, this trend was not observed during the load cycle AST (Movie 2). The loss of hydrophobicity in the aged anode GDL may have resulted in the retention of water under the ribs. During the operation of PEFCs, water produces at the cathode and a concentration difference occurs between the cathode and anode, causing the water back-diffusion from the cathode to the anode36,48. Yang et al.49 have reported that insufficient water management of the anode GDL leads to water accumulation at the anode, which inhibits hydrogen transport to the catalyst (hydrogen starvation), thereby causing carbon corrosion at the anode (Eq. 4)50. Water accumulation in the aged anode GDL has the potential risk of carbon corrosion, leading to loss of elasticity, which is an important function of anode GDLs in PEFCs51.
In conclusion, we presented a diagnostic method for simultaneously evaluating the degradation rates of MEA components in PEFCs using operando synchrotron X-ray radiography. The proposed method was applied to degradation studies via two different ASTs: load cycling with rectangular potential cycles between 0.6 and 0.95 V and start-stop cycling with linear sweep potential cycles between 1.0 and 1.5 V. During the load cycle AST, the cathode CL degraded the most in the MEA components, with a 26% reduction in the ECSA after 10,000 cycles; no degradation was observed in the PEM, whereas the cathode GDL showed a 10% increase in water saturation, indicating a decrease in hydrophobicity due to degradation. During the start-stop cycle AST, all the MEA components deteriorated at the same timescale. The PEM caused hydrogen cross-leakage after 7,000 cycles. The cathode CL exhibited significant carbon corrosion and catalyst degradation. The cathode GDL exhibited increased water saturation relative to the amount of water produced, and wetting behavior was observed in the cathode MPL. Furthermore, water accumulation was also observed in the anode GDL. Considering the cost of fuel cell stacks, GDLs comprising carbon without precious metals are by far the least expensive components of the MEAs. This indicates that stack replacement owing to GDL degradation is unacceptable. Our findings indicate the importance of GDL degradation studies vis-à-vis the current trend of focusing on PEM and CL degradation studies for PEFCs.