Amrutanshu Praharaj‡
ab,
Manjunatha Kempasiddaiah‡ab,
Biplab Kumar Mannaab,
Rajib Samantaab,
Ravi Kumar Trivedicd,
Tushar Khairwalab and
Sudip Barman
*ab
aSchool of Chemical Sciences, National Institute of Science Education and Research (NISER), Bhubaneswar-752050, Orissa, India. E-mail: sbarman@niser.ac.in
bHomi Bhabha National Institute, Training School Complex, Anushakti Nagar, Mumbai – 400094, India
cDepartment of Physics, Karpagam Academy of Higher Education, Coimbatore 641021, Tamil Nadu, India
dCentre for Computational Physics, Karpagam Academy of Higher Education, Coimbatore 641021, Tamil Nadu, India
First published on 6th August 2025
Excess nitrate (NO3−) accumulation occurs due to an imbalanced nitrogen cycle, primarily driven by artificial nitrogen fixation. In the meantime, environmental NO3− buildup has a substantial adverse effect on human health and the ecosystem. The electrocatalytic nitrate reduction reaction (NO3RR), which yields value-added compounds like ammonia (NH3), has lately attracted attention as a viable technique for addressing environmental and energy-related concerns. The NO3RR meets the urgent need to remove NO3− and produce NH3 through an alluring electrocatalytic pathway. Thus, this paper will discuss the preparation of novel 2D [Co(btbH)2(dpe)2]·DMF metal–organic frameworks, which crystallize in the triclinic crystal system belonging to the P space group, using a solvothermal method. Among the nanocatalysts used, metallic cobalt nanoparticles supported on nitrogen-doped carbon (CoNPs/NC-600), facilely prepared through the thermal decomposition of Co-MOFs, have been shown to be highly efficient electrocatalysts for NH3 production from the NO3RR. The CoNPs/NC-600 nanocomposites exhibit a maximum partial current density (PCD) of −66.03 mA cm−2 for NH3 production, achieving a faradaic efficiency (FE) of 72.25% at −0.5 V vs. RHE. Additionally, the highest yield rate of ammonia reached a notable value of 30.79 mmol h−2 cm−2. Furthermore, density functional theory (DFT) calculations revealed that the Co[111] surface facilitates active nitrate reduction surpassing water dissociation over the Co3O4[311] surface. Hence, this work provides a new design strategy for developing high-performance MOF-derived electrocatalysts for the nitrate reduction reaction (NO3RR) aimed at NH3 production.
Currently, ammonia (NH3) is one of the most widely used industrial compounds.5 To help feed the growing global population, the production of NH3 is now estimated to be around 175 million tonnes annually and is predicted to rise by 3–5% annually for the next few years.6 Today, NH3-based fertilisers account for 50% of all agricultural production worldwide, with 85% of the NH3 produced going towards fertiliser production.7 Therefore, ammonia will continue to play a dominant role in the agricultural sector, supported by existing distribution and transportation networks. Additionally, it is also being explored as a potential energy carrier. The main factor boosting NH3's potential as an energy carrier is its high volumetric energy density (15.6 MJ L−1), which is more than three times higher than that of Li-ion batteries (1.73 MJ L−1) and compressed H2 (5.5 MJ L−1 at 70 MPa).8 It might also develop into an energy carrier in the future.9 The storage and transportation of hydrogen is quite complex, making ammonia a promising hydrogen carrier.10 Unlike liquid hydrogen, which requires extreme conditions, ammonia can be easily liquefied by increasing pressure.11
To date, we know the Haber–Bosch process as the only way for the mass production of ammonia from a reaction between N2 and H2 at high temperature (∼500 °C) and pressure (∼300 bar).12 However, the process is energy-intensive and requires the use of fossil fuels to generate H2, which results in high operating costs, and as a byproduct, it also emits CO2. Currently, the world relies on the Haber–Bosch (HB) process for the production of NH3. It emits more than 450 million metric tonnes of CO2 (−2.9 tCO2 per tNH3) annually and uses over 5.5 EJ of energy (38 GJ per tNH3).13,14 The nitrogen reduction reaction (NRR), a promising ambient electrochemical pathway, has the potential to serve as an alternative to the energy-intensive Haber–Bosch process.15–18 However, the NRR usually experiences a significantly poor NH3 yield as well as FE due to the extremely low solubility of N2, highly stable NN bond with a bond energy of 941 kJ mol−1 (ref. 19) at room temperature, and the intensely competitive hydrogen evolution reaction (HER), which occurs at almost the same potential.6 Thus, an alternative approach for the selective production of ammonia is essential.
In nitrate (NO3−), the NO bond has a low dissociation energy of 204 kJ mol−1 (ref. 20 and 21) and is highly soluble in water. As a result, NO3− electroreduction to NH3 (NO3RR) is more energetically advantageous for NH3 production than the NRR.22–25 In the meantime, NO3−, a frequent and hazardous environmental pollutant, is present in large amounts in industrial and sanitary wastewater.26 Consequently, the NO3RR offers a potential path toward simultaneously achieving ammonia production and environmental remediation. Instead of requiring an abundance of H2 or other reducing agents, the NO3RR employs electricity to reduce protons in the aqueous phase of nitrate, converting them into products like N2, NH3, etc.27 Therefore, the NO3RR may offer a viable substitute for the HB process while also offering a way to address the world nitrogen cycle's imbalance.28 In the NO3RR, electrocatalysts and their effectiveness are frequently assessed using three parameters: durability, selectivity, and catalytic activity. The cost of the electrocatalysts and the FE of the NO3RR are also essential considerations for scale-up, as they raise the energy consumption and construction costs of electrochemical systems. Also, the NO3RR is strongly impacted by the competitive hydrogen evolution reaction (HER). Thus, finding catalyst materials that satisfy all of these requirements is still tricky.29
Metal ions or clusters linked by organic ligands are known as metal–organic frameworks (MOFs). MOFs have a vast surface area and pore structure, making them functional materials for various applications, including catalysis, gas sensing, and energy storage.30–33 Generally, MOFs can exhibit ultra-high porosity and surface areas beyond 6000 m2 g−1.34 Porous MOFs exhibit microporous characteristics (<2 nm), but they could be typically adjusted to tune the pore diameters from several angstroms to several nanometres by varying the organic linkers.35 At the same time, metal–organic frameworks with cobalt metal precursors have shown great promise as nitrate reduction materials because of their distinct structural characteristics and catalytic properties.36 Because of their high electrostatic interaction with NO3− ions and the oxidation states (such as Co, Co+, Co2+, and Co3+) Co catalysts are favourable for the adsorption and activation of NO3−.14,37 Usually, cobalt ions are paired with organic ligands to create porous structures with large surface areas in these MOFs. The MOF's cobalt active sites allow effective nitrate reduction via electrochemical processes. The capacity of cobalt sites to adsorb nitrate molecules and aid in their conversion to nitrogen gas or ammonia is supposed to be responsible for their catalytic activity. Furthermore, the increased mass transfer of reactants and products made possible by the porous structure of cobalt-derived MOFs improves their catalytic efficacy. The worth of cobalt-derived MOFs for nitrate reduction in aqueous environments has been shown in several investigations, underscoring their potential for environmental remediation and long-term nitrate control.38–40
In this work, we synthesized a new 2D Co[(btbH)2(dpe)2]·DMF MOF via a simple solvothermal method, which was then converted into CoNPs/NC-600 composites through CVD pyrolysis. These composites outperformed bare CoNPs and Co3O4/NC-500 in nitrate reduction to ammonia. The CoNPs/NC-600 achieved a notable partial current density (PCD) of −66.03 mA cm−2 and a faradaic efficiency (FE) of 72.25% at −0.5 V (vs. RHE), significantly enhancing NO3− to NH3 reduction while minimizing H2 production. Also, the composite showed excellent stability over 12 hours. This improvement is attributed to higher active site exposure, better NO3− adsorption, and the composite's crystalline nature, electrochemical surface area, and porous structure. Furthermore, DFT calculations also revealed that Co[111] promotes hydrogenation more efficiently than Co3O4[311], with a lower energy barrier for *NH2 to *NH3 conversion. Hence, this work underscores the potential of Co-based MOF derivatives for advancing sustainable ammonia synthesis.
ERHE = EAg/AgCl + 0.059 × pH + 0.1976 | (1) |
![]() | (2) |
The faradaic efficiency (FE) is the ratio of electrons consumed during the NO3− reduction to NH3 to the electrons consumed to produce a specific product. The following formula is used to calculate the FE for the formation of NH3:
![]() | (3) |
![]() | (4) |
The following equation was used to calculate the formation rate of NH3 (mmol h−1 cm−2) from the NO3RR:
![]() | (5) |
Assuming that every Co atom on the electrode is a catalytically active site, the TOF is computed using the following equation:
![]() | (6) |
The overall packing arrangement of the 2D layered structure is illustrated in Fig. 1f, where the framework exhibits a rectangular motif. Each rectangle comprises two cobalt centres positioned at the corners, linked by double-walled dpe ligands and a single btb ligand. The spatial organization and intermolecular interactions within the crystal suggest potential implications for porosity and host–guest interactions in related MOF architectures. The crystal data and structure refinement parameters and the corresponding bond lengths and bond angles of [Co(btbH)2(dpe)2]·DMF are shown in Tables S1–S3,† respectively.
X-ray photoelectron spectroscopy (XPS) was used to further examine the surface chemical state and composition of the [Co(btbH)2(dpe)2]·DMF MOF, as illustrated in Fig. 3a and b. The presence of Co, C, N, and O in the MOF is evident from the XPS survey scan (Fig. 3a). The Co(II) 2p3/2 and Co(II) 2p1/2 states are represented by the two distinctive peaks in the Co 2p core XPS spectrum, which are located at 780.8 eV and 796.6 eV, respectively. Further proof of the existence of divalent Co(II) ions in the Co-MOF is also provided by the emergence of shake-up satellite peaks in the binding energy range of 775 to 810 eV (Fig. 3b). Furthermore, the results of powder X-ray diffraction pattern matched the simulated XRD data and displayed a good agreement with all the diffraction peaks (Fig. 3c). Also, through the stretching and bending vibrations at 1706, 1666, 1607, 1403, 1016, 768, and 554 cm−1, ATR-IR further verifies the structure of the [Co(btbH)2(dpe)2]·DMF MOF (Fig. S2†). All these results confirm that the produced [Co(btbH)2(dpe)2]·DMF MOF was highly pure and had outstanding crystallinity.
Using powder XRD patterns, the composition and crystalline nature were carefully investigated (Fig. 3d and Fig. S3a†). At first, Fig. 3d shows the p-XRD pattern of CoNPs/NC-600 composites with the distinctive peaks of Co nanoparticles (COD Number: 9008466), which agrees well with the HR-TEM results of the CoNPs/NC-600 composites. These p-XRD patterns demonstrate different peaks at different 2θ values of 44.3°, 51.7°, and 76°, respectively, which correspond to the crystallographic planes (−1−1−1), (−200), and (−2−20) of Co nanoparticles. Additionally, the crystal plane of Co(−1−1−1) exhibits a strong and highly powerful Braggs reflection at 2θ of 44.3°, confirming the face-centered cubic structure of Co nanoparticles. Hence, all the above HR-TEM and p-XRD data show that the porous N-doped carbon frameworks were successfully decorated with Co nanoparticles. Also, the p-XRD pattern of the Co3O4/NC-500 composite (COD Number: 1538531, Fig. S3a†) displays characteristic peaks corresponding to Co3O4, thereby confirming the formation of the Co3O4/NC-500 composites.
Additionally, to determine the pore size distribution, nitrogen (N2) adsorption and desorption isotherms of the CoNPs/NC-600 composites were examined (Fig. S3b and c†). Initially, the pore size distribution study using density functional theory showed a pore radius of 1.56 nm, confirming the presence of micropores in the prepared material. The surface area of the composite was also calculated using the Brunauer–Emmett–Teller (BET) method. The CoNPs/NC-600 composite's computed specific surface area was found to be 217.7 m2 g−1. These results suggest that the composite has a porous structure that allows ions and electrolytes to pass through. By facilitating the effective transport of ions and electrolytes within the material, these pathways are essential for improving electrocatalytic kinetics and supporting the material's electrocatalytic performance.
To gain a systematic understanding of the composites's surface elemental composition, electronic characteristics, and element valence states, an additional study using X-ray photoelectron spectroscopy was carried out. Co, C, O, and N were clearly verified using the XPS survey scan of the CoNPs/NC-600 composite (Fig. 4a), which is compatible with the elemental mapping analysis results. Two prominent peaks at binding energies of 779.1 eV (2p3/2) and 795.1 eV (2p1/2) in the deconvoluted high-resolution XPS spectra of Co 2p were mostly associated with the metallic Co (Fig. 4b).41 The combined results of the HR-TEM and p-XRD data determine that most of the composite materials were metallic Co.
![]() | ||
Fig. 4 X-ray photoelectron spectroscopy (a) survey scan; high-resolution (b) Co 2p, (c) C 1s, and (d) O 1s spectra of the CoNPs/NC-600 composite. |
However, peaks corresponding to Co(II) formation were also observed at the binding energies of 781.11 eV and 796.8 eV (Fig. 4b). Five distinct peaks were identified by further fitting the C 1s XPS spectra, as shown in Fig. 4c. These peaks were recognised as Co–C (283.7 eV), sp2 C (284.25 eV), sp3 C (285.1 eV), C–N/CO (286.22 eV), and O
C–O (288.05 eV), respectively.42 The O 1s spectrum is deconvoluted into three main components in Fig. 4d. Binding energies of 529.5, 530.22, and 531.57 eV were attributed to oxygen bonded with Co (O–Co), C
O, and C–O/C–N bonds, respectively.43 The ICP-OES data were also obtained for CoNPs/NC-600 composites to quantify the active metal content present. From the results, it is evident that CoNPs/NC-600 composites contain 33% of Co. The higher metal content could explain the better NO3RR activity of the CoNPs/NC-600 composite.
Subsequently, electrochemical impedance spectroscopy (EIS) was performed to obtain Nyquist plots for bare CoNPs, Co3O4/NC-500 and CoNPs/NC-600 composites (Fig. 5c). The EIS was conducted at a particular potential of −0.5 V vs. RHE to analyse the electron transfer process in NO3− ion saturated 1 M KOH aqueous electrolyte. An equivalent circuit was used in the analysis to fit the Nyquist curves of the impedance spectra (Fig. S4†), where factors such as electrolyte resistance and polarisation resistance are symbolized as Rs and Rct, respectively. Table S4† shows that all composites have nearly equal ohmic resistance (Rohm), with an average value of 4.45 ± 0.07 Ω due to similar electrolytes and reactor conditions. The semicircle radius is proportional to the charge transfer resistance; a smaller arc radius suggests quicker interfacial electron transport. The Nyquist plots show that the CoNPs/NC-600 composite synthesized in an inert environment had a substantial effect on the electrode's electrochemical characteristics. The arc radius of the CoNPs/NC-600 composite had the smallest Rct value of 1.10 Ω, which is 5.31 and 1.2 times lower than those of CoNPs and Co3O4/NC-500 composites, respectively. The CoNPs/NC-600 composite demonstrates low charge-transfer resistance, implying that the composites can improve quicker charge transfer or reaction kinetics at the reaction surfaces, which is beneficial for NO3− reduction.
To study the kinetics of the reaction with and without the presence of NO3− ions, Tafel slope values were calculated using the applied potential (V vs. RHE) and logarithm of current density log(J (mA cm−2)). Fig. 5d depicts the Tafel slope of the CoNPs/NC-600 composite for both the NO3RR and HER processes. The Tafel slope of the CoNPs/NC-600 composite for the HER (without NO3− ions) is about 387 mV dec−1, while it is 170 mV dec−1 for the NO3− reduction reaction. The lower slope in the case of the NO3RR corresponds to a lower Rct value and higher reaction kinetics. Thus, the CoNPs/NC-600 composite significantly promotes the production of ammonia (NH3) over H2 generation.
Right after observing the interesting catalytic behaviour of the bare CoNPs, Co3O4/NC-500 and CoNPs/NC-600 composites from the LSV curves, and to evaluate the corresponding faradaic efficiency of the NO3RR, bulk electrolysis was performed sequentially in an H-type cell at constant potentials ranging from −0.3 to −0.6 V vs. RHE in 1.0 M KOH with 0.1–0.025 M KNO3 electrolyte. Following 30 minutes of bulk electrolysis, NH3 was detected and measured using the 1H-NMR technique (see section 2.3.3 for specifics), and the results are plotted in Fig. 6 and 7.
Remarkably, NH3 was reliably detected at a potential as low as −0.3 V vs. RHE, and its identification was constant and reproducible. The small deterioration of the catalytic performance at more negative potentials (>−0.6 V vs. RHE) could be attributed to the competing HER process. Following the chronoamperometry studies, the electrode made of CoNPs/NC-600 composites displayed a volcano-shaped curve in faradaic efficiency, peaking at −0.3 V at 63.43% (Fig. 6a). Nonetheless, CoNPs/NC-600 composites exhibit the highest faradaic efficiency for NH3 (FEammonia) than bare CoNPs and Co3O4/NC-500 composites at nearly all studied potentials, which hinders the generation of H2 (Fig. 6a). More specifically, the CoNPs/NC-600 composite had a higher faradaic efficiency and NH3 production rate of 72.25% and 30.79 mmol h−1 cm−2 (0.075 M KNO3), respectively, which were significantly greater than those of the Co3O4/NC-500 composite (52.5% FE) and bare CoNPs (48.75% FE) (Fig. 6b). The 1H-NMR spectra of the electrolyte following the NO3RR are shown in Fig. 6c. These spectra clearly demonstrate the generation of NH3 through electrochemical reduction of NO3− ions at various applied potentials in 0.1 M KNO3 electrolyte, with their peak intensity rising as the applied potential increases. Furthermore, many control studies were also conducted to verify the nitrogen source involved in the artificial ammonia formation. First, the amount of generated NH3 was observed under an open circuit, i.e., no current passing through the cell and in the presence of 0.1 M KNO3 solution. This experiment shows negligible formation of ammonia after 30 minutes of electrolysis (Fig. 6d and e). Similarly, without adding NO3− ions to the electrolyte solution, we did not observe any visible NH3 generation under an applied potential of −0.5 V vs. RHE, which was again confirmed by the 1H-NMR technique (Fig. 6d and e). All things considered, our findings support the idea that NH3 production and the level of NO3− ions in electrolyte are directly correlated. These findings also supported the idea that the sole nitrogen source for ammonia's electrochemical production is the presence of NO3− in the solution. To assess the stability of the electrocatalyst, chronoamperometry (CA) was performed under essential conditions (1.0 M KOH) for 12 hours at −0.3 V, following the addition of 1.0 M KNO3. As shown in the graph (Fig. 6f), the initial current density was −22 mA cm−2, which decreased to −19 mA cm−2 after 12 hours. This indicates that the prepared catalyst retains 86.6% of its initial current density even after 12 hours of electrolysis. The after-stability characterization of the material was also carried out by ex situ XPS, and TEM analyses. The Co 2p XPS analysis of the CoNPs/NC-600 composite confirmed the same oxidation states of Co even after electrolysis (Fig. S5a†). Moreover, the TEM image of the post-electrolysis CoNPs/NC-600 composite demonstrated that its morphology remained nearly identical to that of the fresh catalyst (Fig. S5b†). These observations are strongly supported by the HR-TEM and SAED results (Fig. S5(c and d)†), providing compelling evidence for the presence of these components.
Ultimately, the impact of the nitrate concentration on the performance was evaluated, and the electrolyte containing 0.075 M KNO3 yielded the optimal FE for the formation of NH3 (Fig. 7a). In this instance, we assessed the CoNPs/NC-600 composite's catalytic performance at a range of KNO3 concentrations, which varied from 0.025 to 0.1 M. The FE for NH3 synthesis was somewhat reduced as the NO3− concentration declined, which is most likely due to the increasing contribution of the competing HER. Additionally, we found that raising the KNO3 concentration from 0.025 to 0.075 M significantly increased the NH3 faradaic efficiency. At 0.025, 0.05, and 0.075 M concentrations of KNO3, the maximum FEs for NO3− to NH3 conversion were 69.14, 72.1, and 72.25%, respectively. It is interesting to note that as the NO3− concentration increased to 0.1 M, the FE of ammonia generation reduced even more. Herein, we speculate that the high concentration of NH3 generated in this instance may not be quickly detached from the catalyst surface in a timely manner, which would cause the NO3RR active site deactivation. In a 1.0 M KOH electrolyte containing 0.075 M KNO3, the maximal FE of the CoNPs/NC-600 composite for the NO3RR is 72.25%. Hence, these findings show that the CoNPs/NC-600 composite performs well in basic electrolytes in terms of the NO3RR, which is encouraging for sustainable environmental applications (Fig. 7a). In parallel, NH3 yield rates were computed for each NO3RR conversion. It is evident from the plot of the NH3 yield rate vs. applied potential (Fig. 7b) that a higher potential led to a higher NH3 yield. Compared to other bare CoNPs and Co3O4/NC-500 composites, the product yield rate of the CoNPs/NC-600 composite was considerably higher. However, as the potential increased, the yield rate of NH3 improved dramatically, reaching its peak performance at −0.5 V vs. RHE up to 30.79 mmol h−1 cm−2 (Fig. 7b). Considering the wide range of applied potentials over which the FE of NH3 is still high, Fig. 7c shows the partial current density (PCD) of each sample. According to Fig. 7c, which shows the plot of PCD against the studied potentials, the PCD for NH3 (jammonia) increased due to a rise in overpotential. Compared to other composites like bare CoNPs and Co3O4/NC-500 composites, the PCD of the CoNPs/NC-600 composite exhibits significantly greater jammonia values. Interestingly, the jammonia values of CoNPs/NC-600 (in 0.075 M KNO3) and Co3O4/NC-500 (in 0.1 M KNO3) composites are nearly identical when the potential is more positive than −0.5 V. However, when the potential is more negative from −0.5 V, the jammonia of CoNPs/NC-600 surpasses that of the Co3O4/NC-500 composite. This is clearly due to the larger potential window of CoNPs/NC-600 for the high selectivity of NH3 production. In 0.075 M KNO3, as shown in Fig. 7c, the maximum values of the partial current density of the CoNPs/NC-600 composite for NH3 is −66.03 mAcm−2 at −0.6 V.
In comparison, the jammonia of bare CoNPs and Co3O4/NC-500 composites are −60.95 mA cm−2 (at −0.6 V, 0.1 M KNO3) and −66 mA cm−2 (at −0.5 V, 0.1 M KNO3), respectively. We also computed the turnover frequency (TOF) using the obtained FE, which is plotted against applied potentials in Fig. 7d. With a higher TOF value of 0.75 s−1 at −0.5 V vs. RHE, the CoNPs/NC-600 composite performs much better than other composites such as bare CoNPs and Co3O4/NC-500, assuming that all the Co atoms on the electrode surfaces are catalytically active.
Factors responsible for high catalytic activity:
(a) From Brunauer–Emmett–Teller (BET) analysis (Fig. S3b and c†), it is confirmed that the CoNPs/NC-600 composite has a porous structure with a high specific surface area of 217.72 m2 g−1. The electrolyte can move through it more easily because of its porous structure. This phenomenon will facilitate the transfer of mass and charge since reactants will be supplied to the cathodic surfaces rapidly, and the formed product will be released easily. Consequently, there is an increase in catalytic performance.
(b) The presence of a nitrogen-doped carbon framework could be another key reason for increased catalytic activity and thus the formation of NH3. As we can see, the CoNPs/NC-600 composite exhibits better current density and faradaic efficiency than bare CoNPs. Herein, the N-doped porous carbon skeleton improves the conductivity of the CoNPs/NC-600 composite while also maintaining structural integrity, shortening ion-diffusion paths, and increasing stability.
(c) The strong catalytic activity observed may be attributed to its large electrochemically active surface area (ECSA). The catalysts’ ECSA was calculated using double-layered capacitance (Cdl). It is commonly recognized that the catalyst's ECSA and Cdl are intimately correlated. Consequently, we measured the Cdl by cyclic voltammetry of the catalysts in 1.0 M KOH in the non-faradaic region within the 20–100 mV s−1 scan speed range. The plot of current density vs. scan rate for each composite is displayed in Fig. S6.† According to Fig. S6,† the Cdl values for the CoNPs/NC-600, Co3O4/NC-500, and bare CoNPs were 0.24, 0.22, and 0.25 mF cm−2, respectively. The CoNPs/NC-600 composite exhibits the highest ECSA value of 0.24 mF cm−2 than Co3O4/NC-500, implying more active sites for the electrochemical conversion of NO3− to NH3 and a greater electrochemical active surface area.
These findings imply that the outstanding NO3RR activity of the CoNPs/NC-600 composite is due to its unique structure, porous carbon nature, and higher surface area, indicating that this is a promising way to achieve an effective and highly selective NO3RR. Also, the porous carbon skeleton improves the conductivity as well as the stability of CoNPs/NC-600 while also maintaining structural integrity.
To perform DFT simulations, the Co [111] and Co3O4 [311] surfaces, as suggested by experimental XRD and HR-TEM investigation, are chosen as theoretical models. The NO3RR to NH3 on Co [111] and Co3O4 [311] follows multiple reaction pathways, as shown in Fig. 8. The entire optimized minimum energy configuration is displayed in ESI Fig. S7–S9.† The zero point energy and entropy correction for the Co[111] surface are shown in Table S5.†
There are generally two pathways reported in the literature.27,45–47 The NO3RR in the present study proceeds through NO3− – *NO3 – *NO2 – *NO – *N deoxygenation steps, followed by the *NH – *NH2 – *NH3 – NH3 (g) hydrogenation steps. The rate determining step (RDS) in our present study, as shown in Fig. 8, is the conversion of *N to *NH (deoxygenation step) with a free energy (ΔG) 0.89 eV on the Co [111] surface, while the ΔG of *N to *NH for the Co3O4 [311] surface is 1.33 eV. For the Co3O4 [311] surface, the RDS is *NH3 to NH3 with a change in the Gibbs free energy of 1.72 eV.48,49 It shows that the ΔG value of 0.89 eV for Co [111] in the RDS is smaller than the ΔG value of 1.72 eV for the Co3O4 [311] surface, which is consistent with the experimental phenomenon and thus highlights the critical role of Co in facilitating the kinetics of the NO3−RR. Furthermore, to get more insight into the theoretical mechanism for the change of free energy, we consider the N–H hydrogenation reaction as shown in Fig. 9a. It can be observed that the water dissociation energy barrier is around 1.18 eV, as shown in Fig. 9b, which is very high compared to the energy of 0.15 eV required for the “*NH2 + *H2O = *NH3 + *OH” process. It is proposed that the hydrogenation occurs concurrently on the Co [111] surface and activates the NO3RR process easily rather than on the Co3O4[311] surface.
![]() | ||
Fig. 9 (a) Reaction free energy plot for water dissociation and *N, *NH, and *NH2 hydrogenation. (b) Reaction free energy on Co[111] and Co3O4[311] towards the HER (hydrogen evolution reaction). |
Footnotes |
† Electronic supplementary information (ESI) available: Instruments and analysis; table of crystal data and structure refinement parameters; table of bond lengths of [Co(btbH)2(dpe)2]·DMF; table of bond angles of [Co(btbH)2(dpe)2]·DMF; ATR-IR spectra of the 2D [Co(btbH)2(dpe)2]·DMF MOF; p-XRD data of Co3O4/NC-500, BET data of the CoNPs/NC-600 composite; fitting equivalent circuit and table of fitting data of the impedance spectra for bare CoNPs, Co3O4/NC-500 and CoNPs/NC-600 composites; after stability characterization; ECSA analysis; computational details. CCDC 2364117. For ESI and crystallographic data in CIF or other electronic format see DOI: https://doi.org/10.1039/d5nr02589c |
‡ These authors contributed equally. |
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