Open Access Article
You Wu†
a,
Yangpeng Zhang†
a,
Hao Zhao†a,
Yang Penga,
Hailing Maa,
Fangyuan Kang
b,
Zhonghua Li
*a,
Yang Liu*c and
Qichun Zhang
*bd
aSchool of Chemistry and Chemical Engineering, Harbin Institute of Technology, Harbin 150001, P. R. China
bDepartment of Materials Science and Engineering, City University of Hong Kong, Hong Kong SAR 999077, P. R. China
cSchool of Computer Science and Technology, Harbin Institute of Technology, Harbin 150001, P. R. China
dDepartment of Chemistry, Center of Super-Diamond and Advanced Films (COSDAF), Hong Kong Institute of Clean Energy (HKICE), City University of Hong Kong, Hong Kong SAR 999077, P. R. China
First published on 6th January 2026
The electrocatalytic reduction of nitrate (NO3RR) to ammonia presents a viable solution for addressing nitrate pollution and offers an environmentally-friendly, energy-efficient alternative for industrial ammonia synthesis. However, the absence of efficient electrocatalysts impedes its industrial application. In this study, we constructed a porphyrin organic cage (PB-2) through the covalent-bonded self-assembly. Subsequently, metalized porphyrin organic cages, PB-M (M = Co, Ni, Cu), were synthesized via post-modification of PB-2. These PB-M catalysts were utilized to elucidate the reaction pathway and intrinsic structure–performance relationship of the NO3RR. Experimental results indicate that PB-Co exhibits the highest activity and ammonia selectivity (FENH3 = 95.8 ± 1.06%, NH3 yield rate = 995.5 ± 28.4 µmol h−1 mgcat−1). Theoretical calculations reveal that the d–p orbital hybridization between the Co 3d orbital in PB-Co and the NO3− 2p orbital is the strongest one. PB-Co possesses a high d-band center of −0.97 eV and high adsorption energies for NO3− and H2O, promoting charge transfer and the production of active hydrogen, thereby reducing the activation energy barrier of NO3−. This research illuminates the intrinsic structure–activity relationship of metalized PB-M for the NO3RR, potentially providing valuable insights for the design of efficient electrocatalysts.
The electrocatalytic reduction of nitrate (NO3RR) provides an environmentally friendly, energy-saving, and potentially scalable solution to address nitrate pollution. The NO3RR employs renewable and clean electrical energy to drive the reduction reaction, thereby effectively decoupling ammonia synthesis from fossil fuels. This innovative technology not only reduces greenhouse gas emissions but also addresses the critical challenge of nitrate contamination in water bodies.22–24 Due to the complexity of the NO3RR process and intermediate products, the development of highly efficient and selective electrocatalysts poses a significant challenge.25–27 Efficient NO3RR requires highly active, selective, and stable electrocatalysts. Porphyrin serves as the active center in numerous biological enzymes and acts as a significant biomimetic catalyst, possessing high catalytic efficiency and selectivity during the catalytic reaction process.28,29 The utilization of porphyrin molecules in the NO3RR has been extensively documented over the years.30–32 However, the low density of active sites and the tendency to aggregate have hindered the practical application of porphyrin molecule catalysts. The integration of porphyrins into porous materials, such as covalent organic frameworks (COFs), metal–organic frameworks (MOFs) and porous organic cages (POCs) has become a trend.33–38 POCs are an emerging sub-class of crystalline porous materials that have garnered significant attention in recent years due to their exceptional properties. In 2015, Kim et al. synthesized two porphyrin boxes (PB-1 and PB-2) through dynamic imine condensation reactions.39 These two porphyrin boxes are covalent organic cages with a rhombic cuboctahedral geometry, constructed from six porphyrin units and eight triamine linkers. The hollow characteristics of octahedral porphyrin boxes and the excellent chemical properties of porphyrin units have enabled Kim et al. to apply them in the fields such as electrocatalysis and photocatalysis.40–43 Due to the open intrinsic and inter-cage pores of porphyrin organic cages, when metal ions coordinate with porphyrin, small molecules can readily diffuse to the metal ion sites, thereby facilitating the occurrence of catalytic reactions. The porphyrin organic cages have the structural characteristics of enzyme catalysts, providing valuable insights for the study of supramolecular catalysts and potential avenues for the research of biomimetic catalysts.
In this study, we successfully synthesized a porphyrin porous organic cage (PB-2), which can be utilized as a support for Single Metal Atoms (SACs). The incorporation of metal atoms into PB-2 significantly enhances its electrocatalytic activity for the NO3RR. Specifically, PB-Co demonstrates excellent electrocatalysis efficiency for the NO3RR with a FENH3 of 95.8 ± 1.06% and a corresponding NH3 yield of 995.5 ± 28.4 µmol h−1 mgcat−1. The d-band center of PB-Co is −0.97 eV, which is closer to the Fermi level. DFT analysis shows that the d–p orbital hybridization between the Co 3d orbital in PB-Co and the NO3− 2p orbital is the most robust. The experimental and theoretical results also suggest that PB-Co adsorbs H2O more easily and produces active hydrogen (*H). Furthermore, PB-Co exhibits the lowest reaction barrier, thereby facilitating the reduction of NO3−.
N) for PB-2 (Fig. S2).44 Then, the metal atom (Co, Ni, and Cu) was incorporated into PB-2 by refluxing the mixture of PB-2 and corresponding metal salts. The successful metallization of PB-2 in the presence of different metal salts was verified using MALDI-TOF mass spectrometry (Fig. S1). Powder X-ray diffraction was employed to characterize the crystal structure of PB-2 and PB-M (Fig. S3). The similar characteristic peaks of PB-2 and PB-M were observed, indicating that the crystal structure of PB-2 was not destroyed by chelating metals. Fourier transform infrared (FT-IR) spectroscopy of PB-2 and PB-M (M = Co, Ni, Cu) was also studied (Fig. 1a). Specifically, the peak at 1640 cm−1 can be assigned to the C
N bond, the disappeared peak at 3332 cm−1 corresponds to the stretching of N–H on the porphyrin ring and the newly appeared peak at 1000 cm−1 (M–N–C) confirm the successful metallization of PB-2.45 The UV-vis spectra of PB-2 displayed a strong Soret band around 420 nm and four Q bands between 500 and 670 nm (Fig. 1b). The Soret band arises from the a1u(π) → eg(π*) transition, whereas the Q bands correspond to a2u(π) → eg(π*) transition, respectively. The reduction in the number of Q bands in PB-Co, PB-Ni, and PB-Cu is attributed to the increased symmetry of the porphyrin upon coordination of metal ions, indicating the coordination of metal ions within PB-2.46
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| Scheme 1 Synthesis of PB-2 and PB-M (M = Co, Ni, Cu). (i) TFA, o-dichlorohenzene, 80 °C, 5d; (ii) THF, Co2+/Ni2+/Cu2+ salt, 70 °C, 24 h. | ||
X-ray photoelectron spectroscopy (XPS) tests were conducted to investigate the surface chemical states as well as the elemental composition of these samples. The C 1s XPS spectrum of PB-2 revealed four distinct peaks at 284.8, 285.6, 286.7 eV, and 289.4 eV, which can be attributed to C–C, C–N, C
O, and N–C
O bonds, respectively (Fig. S4). In the N 1s XPS spectra of PB-M (Fig. 1c), three distinct peaks were observed, attributable to imine nitrogen, metal-coordinated nitrogen and pyrrolic N, respectively.47 PB-Co exhibited characteristic Co2+ signatures in its 2p spectrum with satellite peaks (Fig. 1d). PB-Ni showed analogous divalent characteristics (Fig. S5). In the case of PB-Cu, peaks for both divalent and monovalent copper were observed, and the ratio of Cu+/(Cu2++Cu+) in the PB-Cu samples is 30.9%.48 The loading amount of metal atoms was determined by inductively coupled plasma optical emission spectrometry (ICP-OES) analysis, with Co, Ni, and Cu contents of 6.04%, 6.27%, and 7.18%, respectively (Table S1).
Due to the relatively weak adsorption capacity of cages for N2 at 77 K, the porosity of cage is mostly estimated by CO2 adsorption at 195 K, which is common in porous molecular materials. As shown in Fig. 1e and S6, all of these samples exhibited typical type IV sorption isotherm curves, a characteristic evidence for mesoporous structures. The Brunauer–Emmett–Teller (BET) surface areas were calculated to be 242.8 m2 g−1, 48.1 m2 g−1, 51.6 m2 g−1, and 59.4 m2 g−1 for PB-2, PB-Co, PB-Ni, and PB-Cu, respectively. The pore-size distributions of PB-M showed a main peak centered at around 3.4 nm. The microstructure of these samples was characterized using Scanning Electron Microscopy (SEM) and Transmission Electron Microscopy (TEM). SEM (Fig. S7) and TEM (Fig. S8) images revealed that PB-2 and PB-M (M = Co, Ni, Cu) have similar morphological characteristics. The element mapping image shows the uniform distribution of Co, C, and N in PB-Co (Fig. 1f). Additionally, the morphology and element distribution of PB-2, PB-Ni, and PB-Cu are displayed in Fig. S9–S11, respectively.
In order to evaluate the electrochemical performance of PB-2 and PB-M (M = Co, Ni, Cu), these samples were dropcast onto a 1 × 1.5 cm2 carbon paper (CP) with a mass loading of 0.5 mg cm−2 and tested in a H-type electrolytic cell with a three-electrode system. Fig. 2a depicts the linear sweep voltammetry (LSV) curves of the samples in Ar–saturated 0.5 M K2SO4 with and without 0.1 M KNO3.
In 0.5 M K2SO4 electrolyte, only the hydrogen evolution reaction (HER) occurs on the catalyst surface, and the current density of the PB-Co catalyst does not significantly increase until the voltage is lower than −0.25 V (vs. RHE, the same hereinafter). The addition of KNO3 significantly increased the current density of PB-2 and PB-M (M = Co, Ni, Cu) in the electrolyte. For PB-Co catalysts, the current density starts to take off at −0.25 V and increases to 200 mA cm−2 at −1.35 V. In contrast, the maximum current density of the PB-2 catalyst within the test voltage range is less than 100 mA cm−2, which is the proof of the great NO3RR activity for PB-Co. As illustrated in Fig. 2b, the Tafel slope of PB-Co (105.6 mV dec−1) is notably smaller than those of PB-2 (426.2 mV dec−1), PB-Ni (294.1 mV dec−1), and PB-Cu (182.5 mV dec−1). This indicates that PB-Co exhibits the fastest reaction kinetics. The analysis results indicate that both PB and PB-M catalysts have potential ability toward the NO3RR. Compared with the PB-2 catalyst, all metalized PB-2 catalysts showed enhanced catalytic performance.
Quantification of NH3 yields was performed by UV-vis spectrophotometry using the indophenol blue method. The NH3 yield and corresponding faradaic efficiency (FE) at different potentials are calculated and shown in Fig. 2c and d. Notably, PB-Co exhibited the highest FE toward NH3 within the −0.70 to −1.10 V range, achieving a peak faradaic efficiency (95.8 ± 1.06%) at −0.9 V, with a corresponding NH3 yield of 995.5 ± 28.4 µmol h−1 mgcat−1. We compared the NH3 yield rates between molecular cobalt porphyrin (Co-TPP) and PB-Co, found that the NH3 yield rate of PB-Co was approximately 4 times higher than that of Co-TPP (Fig. S14). Therefore, integrating Co into a porpyhrin organic cage can effectively enhance the catalytic performance. Interestingly, although the PB-Cu catalyst shows a relatively high current density in the LSV curve, it exhibited the lowest faraday efficiency and NH3 yield among the PB-M catalysts. Therefore, we calculated the yield rate and FE of NO2−, a significant byproduct of nitrate reduction (Fig. 2e and S15). The PB-Cu catalyst showed the highest yield rate of NO2−. At −0.7 V, the yield rate and FE of NO2− were 393.8 ± 36.3 µmol h−1 mgcat−1 and 11.8 ± 0.07%, respectively. As the potential decreased, the FE of NO2− also showed a downward trend. In order to visually display the dominant product after the reaction, the yield rate ratio of NH3 to NO2− in the product was defined as [NH3]/[NO2−]. As shown in Fig. 2f and S15, for the PB-2 catalyst, the values of [NH3]/[NO2−] were less than 1, indicating that NO2− is the main product, with low selectivity for NH3. As for PB-Co and PB-Ni, the values of [NH3]/[NO2−] were much greater than 1.0, indicating high selectivity for NH3. As for PB-Cu, within the test potential range, the values of [NH3]/[NO2−] were much smaller than 1.0, indicating that NO2− is the main product. The reason for this phenomenon is that *NO2− is easy to desorb on PB-Cu. The theoretical calculation show that the desorption free energy of NO2− on PB-Cu is a negative value, indicating that the desorption of NO2− on PB-Cu is a spontaneous process, resulting in the selectivity of ammonia synthesis on PB-Cu being lower than that of PB-Ni and PB-Co (Fig. S16).49
To elucidate the primary active centers and mechanism of PB-M in the NO3RR, systematic KSCN poisoning experiments were implemented. This approach leverages the strong affinity of SCN− for metal sites, thereby blocking nitrate adsorption through competitive binding.50,51 When introduced into the combined electrolyte system (0.5 M K2SO4 + 0.1 M KNO3), the KSCN additive induced a marked decrease in current densities compared to the KSCN-free control, as evidenced by electrochemical characterization (Fig. 2g and S17). Notably, the suppressed current levels fell below those observed under nitrate-free conditions, confirming the predominant role of metal centers in PB-M (M = Co, Ni, Cu) for the NO3RR. The NO3RR is a process involving the transfer of nine protons, so active hydrogen (*H) plays an important role in the NO3RR. In order to study the ability of different metals to produce *H, 0.5 M tert-butanol (TBA) was added to the electrolyte, where TBA acts as a scavenger for *H. The integral area of current density change after the addition of TBA for PB-Co (68.38) is larger than that of PB-Ni (42.64) and PB-Cu (19.51) (Fig. 2h and S18), indicating that PB-Co can produce more *H. We compared the performance of PB-Co with other recently reported electrocatalysts for the NO3RR, and the NH3 yield rate and FENH3 of PB-Co exceed those of the majority of catalysts reported in previous literature (Fig. 2i and Table S2).
The stability of catalysts is a crucial factor in assessing their potential for industrial applications. Seven cycles of electrolysis with a PB-Co electrode were carried out at −0.9 V, each cycle lasting 1 hour (Fig. 3a). It is clear that the FE and yield rate for NH3 slightly decreased, indicating excellent catalytic stability of PB-Co. Post-electrolysis characterization of PB-Co through FT-IR (Fig. S20), XPS (Fig. S21), and SEM (Fig. S22) analyses demonstrated minor structural alterations, conclusively verifying the exceptional stability of the catalyst under operational conditions. MALDI-TOF analysis also demonstrated that the molecular structure of PB-Co remained intact (Fig. S23). ICP-MS analysis of the electrolyte (after electrocatalysis for 4 h) indicated that the leached Co, Ni, and Cu concentrations were below the detectable limit (0.1 µg L−1). Therefore, PB-M has great stability during the electrolysis. To corroborate the source of produced ammonia, the NO3RR performance of carbon paper (CP) was evaluated by the NH3 yield (Fig. 3b). As expected, CP exhibits low NO3RR activity. PB-Co was used as the working electrode in 0.1 M K2SO4 electrolyte, no NH3 production was detected. Similarly, with PB-Co as the working electrode and 0.5 M K2SO4 + 0.1 M KNO3 as the electrolyte, no ammonia was detected in the electrolyte under open circuit voltage (OCP). Isotope labeling experiments using K14NO3 or K15NO3 as a nitrogen source, followed by product identification via 1H-NMR, were performed. As shown in Fig. 3c, three peaks are observed in the 1H-NMR spectrum after 2 h of electrolysis when using K14NO3 as the electrolyte, corresponding to 14NH4+. Only double peaks corresponding to 15NH4+ are identified in the 1H-NMR spectrum when using K15NO3 as the electrolyte, suggesting that the produced ammonia totally originates from the electrochemical NO3RR.
To evaluate the true catalytic performance of samples, it is necessary to obtain electrochemically active surface areas (ECSAs); however, we cannot directly calculate the ECSAs. Due to the relationship between double-layer capacitance (Cdl) and ECSA, we can roughly calculate the ECSA by calculating the Cdl.52,53 Cyclic voltammetry measurements were conducted (Fig. S24), and by fitting the current density Δj at different scanning rates (20 to 100 mV s−1), the Cdl values of PB-2 and PB-M were obtained (Fig. 3d and e). The results revealed that the Cdl value for PB-Co is 9.12 mF cm−2, which is notably higher than that for PB-Ni (8.02 mF cm−2), PB-Cu (6.72 mF cm−2), and PB-2 (4.18 mF cm−2). The observed enhancement in NO3RR performance of PB-M compared to PB-2 reveals a correlation with its enhanced ECSAs. To systematically evaluate catalytic efficacy, we conducted electrochemical impedance spectroscopy (EIS) analysis to probe interfacial charge-transfer characteristics (Fig. 3f). PB-Co and PB-Cu demonstrated substantially reduced semicircle diameters relative to PB-2 and PB-Ni, correlating with lower Rct values. This charge-transport optimization mechanism effectively enhances the nitrate-to-ammonia conversion kinetics in cobalt-modified systems.
In situ FT-IR spectrometry was conducted to explore the reaction mechanism of PB-M for the NO3RR. As shown in Fig. 4a, the band at ∼1335 cm−1 was attributed to the N–O asymmetric stretching vibration of adsorbed NO3−. The bands located at ∼1100 cm−1 and ∼1269 cm−1 were assigned to the intermediates *NO and *NO2−, respectively. The band located at ∼1465 cm−1 belonged to N–H bending vibration of *NH4+, indicating the conversion of NO3− to NH3 on the catalyst surface under applied potentials. More importantly, we monitored the characteristic peaks of the adsorbed *NH2OH species at ∼1178 cm−1.54–56 According to the above results, the NO3RR on PB-Co satisfies the NHO pathway (*NO3− → *NO2− → *NO → *NHO → *NHOH → *NH2OH → *NH2 → *NH3).
Density functional theory (DFT) calculation was carried out to get deep insight into the great NO3RR performance of PB-Co. The electronic configuration of metal d orbitals is an important factor affecting catalytic activity. The projected density of states (PDOS) of PB-Co, PB-Ni, and PB-Cu are plotted in Fig. 4b. It was found that the DOS for spin-up and spin-down states is more asymmetric for PB-Co than for PB-Ni and PB-Cu, indicates that PB-Co has the largest spin density. The calculated d-band centers (εd) for PB-Co, PB-Ni, and PB-Cu are −0.971 eV, −1.176 eV, and −2.656 eV, respectively. Previous studies have shown that the more positive the d-band center, the stronger the adsorption energy of NO3−; therefore, the adsorption of NO3− on PB-Co is the strongest.57 The interaction between metal d orbitals and NO3− 2p orbitals can be explained by the acceptance–donation mechanism:58,59 on the one hand, the occupied d orbitals of metal atoms transfer electrons to the empty π* orbitals of NO3−, on the other hand, the unoccupied d orbitals of metal atoms accept electrons from NO3−. To further probe the mechanism, the Bader charge and charge density differences were calculated. The Bader charge analysis of PB-M indicates that the Co atom in PB-Co has a more positive charge, which is beneficial to the adsorption of NO3− molecules (Fig. S25). Based on the Bader charge and charge density difference of *NO3−, PB-Co and PB-Ni transferred 0.53 e and 0.56 e to NO3−, respectively, which are higher than that of PB-Cu (Fig. S26). In order to investigate the orbital interactions between *NO3− and metal atoms, we calculated the DOS (Fig. S27) and Crystal Orbital Hamilton Populations (COHP) (Fig. 4c and S28). Analysis of the PDOS between the 2p orbital of *NO3− and the metal d orbital of PB-M (M = Co, Ni, Cu) shows that the overlap between the Co d orbital in PB-Co and the *NO3− 2p orbital is the largest, which effectively forms strongly chemical bonds of Co–O and then boosts the electrons transfer from Co to NO3−.60,61 The strong adsorption of *NO3− on PB-Co is thus validated by COHP, as fewer anti-bonding states are below EF when NO3− is adsorbed on PB-Co. Furthermore, we calculated the ICOHP values between metal atoms and O atoms, and a more negative ICOHP value for the Co–O bond in PB-Co was observed. Therefore, the adsorption of NO3− on PB-Co is stronger than that on PB-Ni and PB-Cu.62–64 As shown in Fig. 4d, the closer the d-band center is to the Fermi level, the stronger the adsorption energy for NO3− and the d–p orbital hybridization, and the better the NO3RR activity. To get deep insight into the superior NO3RR performance of PB-Co, the DFT calculation was carried out to investigate the reaction pathways for the NO3RR on PB-2 and PB-M. The calculated Gibbs free energy changes along with the related intermediates and reaction pathway are shown in Fig. 4e. The first step involves the adsorption of NO3− onto the catalysts, and the stable adsorption of nitrate molecules on catalysts is the key to determining whether the NO3RR can occur. The calculated adsorption free energies of PB-2, PB-Co, PB-Ni, and PB-Cu are 1.91, 0.89, 1.53, and 1.83 eV, respectively, indicating that metal atoms can promote the adsorption of NO3−. There are two typical reaction pathways in the NO3RR:65 the NOH pathway (*NO3 → *NO2 → *NO → *NOH → *N → *NH → *NH2→ *NH3) and the NHO pathway (*NO3 → *NO2 → *NO → *NHO → *NHOH → *NH2OH → *NH2 → *NH3), and it was found that the NHO pathway is energetically more favorable. The results of theoretical calculation showed that ΔG(NO3−–*NO3−) was the rate-determining step for both PB-2 and PB-M. The energy barrier of NO3− required for PB-Co is 0.89 eV, which is the lowest energy barrier. Therefore, PB-Co exhibits the best NO3RR activity and selectivity for NH3. NO is an important intermediate in the NO3RR, and the degree of activation of NO determines whether subsequent reactions can proceed smoothly. Therefore, we calculated the N–O bond lengths of NO on different catalysts, which were 1.187 Å (PB-Co), 1.175 Å (PB-Ni), and 1.173 Å (PB-Cu), respectively. The maximum elongation of the N–O bond on PB-Co is due to the activation effect of the Co atom on *NO, which is beneficial for the subsequent hydrogenation reaction. To further explore the mechanism of PB-M decomposing water to produce active hydrogen, we also calculated the free energy diagram of water decomposition, as shown in Fig. 4f, Compared with PB-Ni and PB-Cu, H2O is more easily adsorbed on PB-Co and more easily decomposed to produce active hydrogen. Therefore, PB-Co exhibits excellent NO3RR activity by promoting the adsorption of NO3− and H2O and producing a large amount of *H.
Footnote |
| † Y. W., Y. Z. and H. Z. contributed equally to this work. |
| This journal is © The Royal Society of Chemistry 2026 |