Open Access Article
Dana Rademakera,
Roy Maasa,
Stefania Tanase
b,
Hongrui Kangc,
Jan P. Hofmann
c and
Dennis G. H. Hetterscheid
*a
aLeiden Institute of Chemistry, Leiden University, 2300 RA Leiden, The Netherlands. E-mail: d.g.h.hetterscheid@chem.leidenuniv.nl
bVan ’t Hoff Institute for Molecular Sciences, Universiteit van Amsterdam, 1098 XH Amsterdam, The Netherlands
cSurface Science Laboratory, Department of Materials and Geosciences, Technical University of Darmstadt, Peter-Grünberg-Straße 4, 64287 Darmstadt, Germany
First published on 10th April 2026
Incorporation of catalytic sites within metal–organic frameworks has been considered advantageous as the amount of catalytic sites per cm2 electrode surface and be greatly expanded, while simultaneously the stability of the catalytic sties can be greatly improved. In contrast to previous studies, it is found that the dPCN-224(Fe) catalyst is extremely sensitive towards reactive oxygen species (ROS) formation during the electrochemical oxygen reduction reaction and deactivates within seconds. Very little is known about deactivation of catalytic sites in MOFs and what the effect could be on the overall catalytic performance of the MOF as a function of time. Herein, the degradation mechanism of dPCN-224(Fe) with ROS is studied in detail and it is shown that a few catalytic sites – presumably positioned at the interface between the MOF and the carbon support – are the specific sites targeted by ROS leading to the complete breakdown of all activity. Therefore, even though the density of active sites is exceptionally high in MOF systems, the catalytic reaction is strongly dependent on only few active sites that are directly positioned at the connection between the MOF and the carbon electrode or support.
Despite the potential of MOFs in catalysis thus far only a single application has made it to the market,10 which is mostly due to an unfavourable ratio between synthetic costs11 and MOF stability during catalytic performance. The stability of MOF-catalysts has predominantly been discussed in terms of the thermodynamics of linker–node interactions.12–14 Particularly high valent metal sites, such as ZrIV or TiIV, in combination with carboxylate functionalized linkers have been reported to be very robust.15 However, the +IV oxidation state in case of titanium and zirconium is very favourable, making these sites unreactive in redox catalysis or electron shuttling.9 Consequently additional redox sites and catalytic sites need to be implemented within such MOFs to mediate electrocatalysis.16–18 Whereas confinement effects to facilitate the activation of reactants is often discussed to improve the activity and/or selectivity of catalytic sites within MOFs,19,20 confinement effects have rarely been discussed as a trigger for catalyst degradation. The local confinement of reagents, pollutants21 and products may for example trigger significant local pH swings,22 or accumulation of other reactive species. To understand how MOF breakdown during electrocatalysis occurs it is important to consider where the catalytic activity takes place during electrocatalysis in MOFs. Where catalysis occurs precisely depends on the diffusion of substrate to the active site, the charge transfer of electrons and ions through the framework, and the intrinsic catalytic rate at these specific active sites.23–25 Depending on the limiting factor during catalysis, the number of active sites that participate in the catalytic reaction may therefore vary (Fig. 1). When the diffusion of the substrate is rate limiting, it is expected that catalysis will predominantly occur at the catalytic sites at the borders of a MOF particle. When the catalytic reaction is limited by charge transfer it is expected that mostly catalytic sites near the interface of the electrode will react. When the catalytic reaction is limited by the intrinsic catalytic rate at an individual site, it is expected that the catalytic reaction will occur more homogeneously throughout the entire MOF particle. Which of these factors is limiting depends on the precise reaction conditions, which includes the concentration of ions, the concentration of substrate, and the applied potential. At the start of the electrolysis the catalytic reaction likely starts at the interface of the MOF crystal and its support, given that the reactant is already loaded within the MOF, and then sweeps through the crystal when the substrate concentration is locally depleted. At these sites where catalysis occurs also damage to the MOF-structure may be expected.
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| Fig. 1 A cartoon of a PCN-224 MOF on an electrode with active sites participating in catalysis shaded in blue with the limiting factor of catalysis being (a) the diffusion of substrate, (b) the conduction of electrons and ions, and (c) the intrinsic catalytic activity of an individual active site. The crystallographic data was obtained from ref. 26. | ||
We recently reported PCN-224(Co) with the cobalt 5,10,15,20-(4-carboxyphenyl)-porphyrin chloride (CoTCPP) as linker as an effective catalyst for the oxygen reduction reaction (ORR) with a high selectivity toward H2O2 of 80%.27 Moreover, the MOF was found to be highly stable upon build-up of H2O2 in the electrolyte solution. This high stability is an interesting finding as H2O2 is a strong oxidant that could lead to deactivation of catalytic sites if they were prone to oxidation by H2O2. The iron porphyrin-based MOFs PCN-224(Fe) and PCN-222(Fe) also showed to be active toward the electrochemical oxygen reduction reaction (ORR) under alkaline aqueous conditions and under acidic aqueous conditions, respectively.28,29 Iron 5,10,15,20-(4-carboxyphenyl)-porphyrin chloride (FeTCPP) is the active site in these porphyrin MOFs and during the ORR with this catalyst, the 2-electron ORR towards H2O2 formation is in competition with the 4-electron reduction towards H2O (Fig. 2).30–32 The H2O2 formed at the iron porphyrin sites can be activated via the Fenton reaction to form reactive oxygen species (ROS).33–40
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| Fig. 2 Mechanism of the ORR and Fenton reaction with iron porphyrin catalysts.30,31 | ||
Here it is found that the catalytic sites in the dPCN-224(Fe) catalyst are extremely sensitive under ORR conditions and deactivate within seconds. With the hypothesis in mind that MOF degradation pathways may be MOF specific due to the confinement of reactants, and local due to the catalytic reaction within the MOF not occurring uniformly (illustrated in Fig. 1) we studied the degradation mechanism of PCN-224(Fe) in the presence of O2 in detail. It is for the first time reported that a few catalytic sites that are presumably positioned at the interface between the MOF and the carbon support are the specific sites that are presumably targeted by ROS leading to the complete breakdown of all ORR activity.
The X-ray powder diffractogram matches the theoretical diffractogram of PCN-224, but lacks the reflections at 3.2 and 5.5° that indicate the presence of ordered PCN-224 superstructure domains in the MOF (Fig. 4).44 Therefore, the PCN-224(Fe) sample made in this work shows the reflections of a crystalline, but disorganized dPCN-224 structure.43,44 The MOF sample is therefore named dPCN-224(Fe). Furthermore, analysis of the N2-isotherm indicated pore sizes of 0.8 and 2.0–2.5 Å, as expected for PCN-224 (Fig. S1).26 Combined, these analytical data for the MOF sample are in good agreement with a dPCN-224 sample of good crystallinity.43
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| Fig. 4 pXRD data of dPCN-224(Fe) synthesized in this work measured at 2° min−1 (black) and the theoretical diffractogram of PCN-224 (grey) that is based on the crystal structure of PCN-224 obtained by Zhou et al.30 | ||
The ORR activity of dPCN-224(Fe) is compared to the activity of FeTCPP to investigate the role of the porous environment of dPCN-224(Fe) on the ORR activity, selectivity, and stability of the catalyst under ORR conditions. Rotating disk electrode (RDE) measurements are carried out in which the glassy carbon working electrode is modified with a dropcast containing the catalyst, carbon black (CB) as an electron conducting additive, and Nafion as an adhesive binder to maintain the physical intactness of the layer. This ink was dropcasted onto a glassy carbon electrode and allowed to dry in air. The ORR activity was assessed with RDE cyclic voltammograms (RDE CVs) in an aqueous solution containing 0.15 M HNO3 and 0.15 M NaNO3 under an oxygen atmosphere.
It is important to note that other electrolytes were used as well, including acetate buffer (pH 4.7), phosphate buffer (pH 7), and borate buffer (pH 8.5) and non-buffered Na2SO4 (pH 5), NaNO3 (pH 7), and NaOH (pH 14) electrolytes (SI 3). However, with all these electrolyte systems, the dPCN-224(Fe) MOF leached from the electrode during the first CV scan or directly when inserted into the electrolyte (Fig. S2). The dPCN-224(Fe) dropcast only remained intact in acidic electrolytes of HNO3, H2SO4 or HClO4. Whereas other PCN-224(Fe) materials have been described to show good ORR activity in alkaline 0.1 M electrolyte solutions,28 the cubic PCN-224(Fe) crystals obtained in this study are not stable in alkaline media and dissolve immediately.
RDE CV measurements of dPCN-224(Fe) and FeTCPP show that in the first scan both catalysts are active for the ORR resulting in large peak-shaped curves (Fig. 5 and SI 4). The shapes of these curves are unusual for RDE experiments and indicate that an irreversible event is occurring during the ORR that is not mass transport limited in oxygen. Moreover, for dPCN-224(Fe) the current collapses upon the continuation of the CV experiment and after nine scans, the ORR activity is completely lost (Fig. 5b). This behavior was also found for a sample of phase-pure PCN-224(Fe) in acidic aqueous electrolyte, which indicates that the absence of the long-range superstructure in dPCN-224(Fe) is not the cause of the decreasing ORR current (Fig. S6). For FeTCPP, the change in the CV upon prolonged scanning is more gradual. The maximum current decreases while the catalytic wave shifts cathodically (Fig. 5c). This RDE CV shows a plateau current with a cathodic peak at 0.25 V vs. RHE on top of the plateau. This additional cathodic peak might be indicative of a mismatch between the elementary steps during ORR catalysis.45–47 If the first activation of the Fe superoxide intermediate via a proton and electron transfer is limiting catalysis, the Fe superoxide species might accumulate before it reacts toward the Fe hydroperoxo intermediate at a higher overpotential. If the activation of this Fe hydroperoxo species is limiting, H2O2 might form locally which is further reduced to H2O at a higher potential.
During the ORR, the iron species is reduced from FeIII to FeII before oxygen binds (Fig. 2). This redox couple can be visualized by measuring a differential pulse voltammetry (DPV) experiment in the absence of oxygen. Therefore, a DPV measurement was carried out under argon atmosphere with a fresh dropcast containing dPCN-224(Fe) (Fig. 6). In the DPV trace two redox couples can be distinguished at 0.65 V vs. RHE and at 0.17 V vs. RHE. The peak at 0.65 V vs. RHE was also observed for PCN-224(H2), which is the same MOF without the iron center coordinated in the porphyrin pocket (Fig. S7). Broad peaks at around 0.6–0.7 V vs. NHE have previously been associated with proton-coupled electron transfers of quinone functionalities on a carbon support.48,49 Therefore, this peak is not expected to be related to the iron porphyrin complex. The peak at 0.17 V vs. RHE is assigned to the FeII/FeIII couple.50 After measuring DPV under argon atmosphere, the dPCN-224(Fe) sample was subjected to an RDE CV measurement of nine scans under oxygen atmosphere, after which DPV was recorded again under argon atmosphere (Fig. 6). The DPV after electrocatalysis reveals that the redox couple at 0.17 V vs. RHE is no longer present.
From reports about photooxidation with dPCN-224(Fe) it is known that H2O2 and reactive oxygen species (ROS) can induce degradation of the catalyst.33–37 To verify if H2O2 also plays a role in the irreversible diminishing of the ORR current for dPCN-224(Fe), the ORR selectivity is investigated. During the ORR, the two-electron oxygen reduction reaction (E° = 0.695 V vs. NHE) towards H2O2 is in competition with the four-electron oxygen reduction reaction towards H2O (E° = 1.23 V vs. NHE). The faradaic efficiency of the ORR towards H2O2 (% H2O2) with dPCN-224(Fe) or FeTCPP is investigated with rotating rink disk electrode linear sweep voltammetry (RRDE LSV) experiments (SI 7). To determine % H2O2 the average of three measurements was used. dPCN-224(Fe) shows a % H2O2 of ∼19 ± 5% over the whole potential range, while FeTCPP shows a % H2O2 of ∼32 ± 7% at 0.4 V vs. RHE and ∼8 ± 2% at 0.15 V vs. RHE. These results indicate that during the ORR with dPCN-224(Fe) and FeTCPP H2O2 is indeed being formed.
Reactive oxygen species (ROS) such as the hydroxyl radical can be formed by the Fenton reaction catalyzed by an iron species:51
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| Fe2+ + H2O2 → Fe3+ + HO˙ + OH− | (2) |
The possibility of an iron species to carry out the Fenton reaction depends on the nature of the iron species and the electrolyte.52 An extensive study was carried out by Yang et al. in which the Fenton reaction catalyzed by FeTCPP was investigated.53 The FeTCPP catalyst was used to degrade the organic molecule bisphenol A in the pH range of 4–12. Via 5,5-dimethyl-1-pyrroline N-oxide (DMPO) trapping experiments, hydroxide radicals could be found in the reaction mixture. This indicates that the porphyrin site FeTCPP that is present in dPCN-224(Fe) is capable of Fenton chemistry. The ability of dPCN-224(Fe) to generate hydroxyl radicals from H2O2 was tested by combining the MOF with H2O2 and the organic dye methylene blue in 0.15 M HNO3 and 0.15 M NaNO3. Methylene blue (MB) is an organic dye that is specifically degraded by hydroxide radicals as shown by radical trapping experiments with DMPO in previous reports.54–56 The degradation of the MB dye can be monitored with UV-vis spectroscopy. The UV-vis signal of MB was found to be stable after addition of H2O2 to the acidic MB solution (Fig. 7a), which indicates that H2O2 itself cannot degrade MB. Combining the dPCN-224(Fe) MOF with the acidic MB solution resulted in 57% loss of MB signal after 24 h (Fig. 7b). This loss of the UV-vis signal of MB can be explained by absorption of the organic dye in the pores of the MOF, which was also observed with PCN-224(Co) (Fig. S10) and the iron-based MOF NH2-MIL-88B(Fe).56 Upon addition of both the dPCN-224(Fe) and H2O2 to the acidic MB solution, a more rapid decrease of the MB signal is seen and 95% of the UV-vis signal at 665 nm is lost after 24 h (Fig. 7c and d). This large decrease of the UV-vis signal of MB indicates that dPCN-224(Fe) can indeed generate hydroxyl radicals from H2O2 that degrade the MB dye. Moreover, upon addition of H2O2 to dPCN-224(Fe) the formation of bubbles was observed, which indicates that the MOF can also catalyse the disproportionation of H2O2 to water and oxygen (Fig. S11). The activation of H2O2 by dPCN-224(Fe) is an interesting finding, since iron mostly has a Fe(III) oxidation state in this MOF, while it is Fe(II) that is expected to mostly accelerate Fenton chemistry via the reductive pathway. This leads to a slow activation of H2O2 in the UV-vis experiment. During the electrochemical ORR, the iron sites are expected to be reduced to Fe(II) by the electrode material, which makes the iron sites more active for the Fenton reaction and fast decomposition of H2O2 to hydroxide radicals is expected.
It was shown that dPCN-224(Fe) produces H2O2 during the electrochemical ORR and that dPCN-224(Fe) can degrade H2O2 into hydroxyl radicals. Therefore, the degradation of dPCN-224(Fe) might be caused by interactions of these radical species with the porphyrin linkers of the MOF. The interactions of ROS with iron porphyrins have been investigated previously.58,60–64 In nature, iron porphyrins of peroxidases are often damaged by the reaction of the heme with H2O2.60 In this peroxidase, porphyrin degradation was found to proceed via ring-cleavage oxidation at the meso-position of the porphyrin. This porphyrin degradation mechanism via ring-opening with loss of iron ions was also found for dPCN-224(Fe) upon H2O2 treatment under UV-light irradiation (Fig. 8).39 Furthermore, degradation of an iron porphyrin in pyridine solution was found to occur due to attack by ROS and a degradation pathway in which the meso-position is oxidized with retention of the N4-binding pocket of the porphyrin was identified (Fig. 8).57,58 This pathway was also reported as possible degradation pathway of heme in nature, in which meso-hydroxyheme is formed upon interaction with hydrogen peroxide.59 To understand what happens to dPCN-224(Fe) during the ORR, the structure and chemistry of dPCN-224(Fe) before and after catalysis was assessed with SEM, pXRD, inductively coupled plasma mass spectrometry (ICP-MS), X-ray photoelectron spectroscopy (XPS), solid state UV-vis, and Fourier-transform infrared spectroscopy (FTIR) measurements.
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| Fig. 8 Reported degradation pathways of an iron porphyrin of the dPCN-224(Fe) MOF upon contact with a reactive oxygen species being either H2O2 or a radical species.39,57–59 | ||
To evaluate the morphology of the dPCN-224(Fe) particles before and after ORR catalysis, a fluorine doped tin oxide (FTO) electrode was covered with the catalyst ink solution and used for twenty CV cycles under oxygen atmosphere. During these 20 CV scans the activity was completely lost (Fig. S12). After drying of the electrode, SEM images were collected of a fresh dropcast sample and a sample that was subjected to catalysis (Fig. S13). The size and shape of the cubic particles are retained after catalysis. Moreover, elemental mapping with SEM-EDX (EDX = energy dispersive X-ray) measurements were carried out to identify the FTO background with Sn and the MOF particles with Zr and Fe contents (Fig. 9). The elemental mapping indicates the presence of Zr and Fe at the position of the MOF particles before and after catalysis as well as Sn at the places without MOF particles. This indicates that the iron is not removed from the framework during catalysis. This was confirmed with ICP-MS analysis of dPCN-224(Fe) by dissolving a fresh dropcast of an FTO electrode and a dropcast of an FTO electrode used for catalysis in HNO3 solution. In the fresh sample 2.09 ± 0.01 Fe ions per Zr6 node were found, while the used samples showed 2.02 ± 0.10 Fe centers per node (SI 11). Moreover, XPS analysis of the dPCN-224(Fe) samples before and after catalysis illustrate that the MOF is retained during catalysis. Substantial amounts of Zr can be detected in samples before and after catalysis. However, Fe, due to its low surface concentration, could not be detected before and after catalysis. Also, the nitrogen content was too low to make a conclusive statement on the state of N from the N 1s spectra. This may suggest that the outside of the MOF particles predominantly consist of Zr-nodes. pXRD measurements were carried out with the FTO electrode covered with the dPCN-224(Fe) ink to investigate the porosity of the framework after catalysis (Fig. 10a). An FTO electrode was covered with 50 µL ink and used for 20 CV cycles under oxygen atmosphere (Fig. S15). pXRD was measured of a fresh FTO electrode with dPCN-224(Fe) ink on it and of an FTO electrode used for electrocatalysis (Fig. 10a). To obtain a dry sample after catalysis, the FTO plate with dropcast was soaked in water to remove electrolyte ions and in DCM to remove the water molecules and allow for drying. During these soaking cycles, some of the dropcast detached from the FTO electrode. Therefore, there are less MOF particles after catalysis than in a fresh dropcast, which leads to lower intensity signals in characterization methods used herein. Nevertheless, the pXRD indicates faint reflections at 4.6° for both FTO electrodes, which indicates the porosity is maintained after catalysis (Fig. 10a).
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| Fig. 9 SEM-EDX of dPCN-224(Fe) (a) before and (b) after 20 CV cycles. Elemental mapping is given for Sn (red), Zr (teal) and Fe (green). | ||
Solid state UV-vis was carried out to investigate the porphyrin UV-vis absorbance of dPCN-224(Fe) before and after catalysis on an FTO electrode (Fig. 10b). A dPCN-224(Fe) ink was made without CB, because the carbon would absorb all the light. The FTO electrode was used for 20 CV cycles under oxygen atmosphere (Fig. S18). A bare FTO electrode, fresh dropcast on FTO and the dropcast used for electrocatalysis were investigated with solid state UV-vis spectroscopy. The fresh dropcast shows two absorbance peaks at 399 and 473 nm that are not present for the bare FTO sample and originate from the porphyrin structure in dPCN-224(Fe). For FeTCPP a Soret band at 419 nm and a Q-band at 535 nm have been documented previously.65,66 Therefore, for dPCN-224(Fe) the absorption peaks are assigned to a Soret band at 399 nm and a Q-band at 473 nm, which is blue-shifted compared to FeTCPP itself. These absorption peaks are still present in the dropcast after catalysis, which indicates that the porphyrin structure remains intact.
FTIR was carried out with the same FTO electrodes without CB to investigate the bonds present in the dPCN-224(Fe) framework before and after electrocatalysis (Fig. 10c). All peaks of the fresh sample are found back in the sample after catalysis and are assigned in Table S3. Moreover, the vibration at 999 cm−1 of Fe–N is present in both spectra, which is indicative of the retention of Fe in the N4-pocket of the porphyrin (Fig. 10d).35 Based on the SEM-EDX, ICP-MS, XPS, pXRD, solid-state UV-vis, and FTIR measurements, it can be concluded that no significant change of the porphyrin and Zr node content has taken place after ORR catalysis with dPCN-224(Fe).
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| Fig. 11 Schematic overview of electron conduction in dPCN-224(Fe) when intact or when the porphyrin site near the glassy carbon (GC) working electrode is inactive due to degradation. | ||
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