Tamilselvi Gurusamy†
a,
Thomas D. Pope†
a,
Samuel F. Wenzel
a,
He Zhang
a,
Heekwon Lee
a and
Hang Ren
*abc
aDepartment of Chemistry, The University of Texas at Austin, Austin, TX 78712, USA. E-mail: hren@utexas.edu
bTexas Materials Institute, The University of Texas at Austin, Austin, TX 78712, USA
cCenter for Electrochemistry, The University of Texas at Austin, Austin, TX 78712, USA
First published on 14th October 2025
Electrochemical nitrate reduction is an attractive pathway to synthesize ammonia from abundant nitrate sources. Copper (Cu) is an active catalyst for this transformation; however, its stability is often compromised by oxidation and leaching during electrocatalysis. Herein, we investigated the encapsulation of Cu nanoparticles inside carbon nanotubes (Cu-in-CNT), which significantly enhances both their structural and electrochemical stability compared to Cu nanoparticles supported on the outer surface (Cu-on-CNT). Encapsulation provides a protective environment that preserves the structure of the catalyst. Post-catalysis analysis reveals that Cu-in-CNT retains its metallic state, whereas Cu-on-CNT undergoes transformation to and CuO to Cu and Cu2O. After 12 hours of continuous nitrate reduction, Cu-in-CNT exhibits much less Cu leaching (5.3 wt%) compared to Cu-on-CNT (20.5 wt%). Furthermore, Cu-in-CNT maintains a stable faradaic efficiency for nitrite and ammonia combined (∼80%), in contrast to significant declined observed for Cu-on-CNT (∼40%).
Electrochemical nitrate reduction is an alternative pathway for ammonia synthesis.9–12 Unlike N2, nitrate (NO3−) and other NOx intermediates can be activated under much milder conditions, and exhibit high solubility in aqueous solutions. Moreover, nitrate is abundantly available, including the widespread accumulation of reactive nitrogen compounds in the environment from agricultural runoff and fossil fuel combustion. Therefore, electrochemical reduction of nitrate to ammonia presents a sustainable and dual-benefit solution for (i) pollution mitigation through the removal of harmful nitrates from water, and (ii) the sustainable production of ammonia from an abundant waste stream.13
Despite its promise, the practical application of electrochemical nitrate reduction is limited by sluggish kinetics arising from the multi-step proton–electron transfer processes, which generate undesired byproducts and compromise catalyst selectivity. Among various candidates, Cu-based catalysts have shown notable potential due to their favorable binding energies toward nitrate and key nitrogen intermediates, facilitating stepwise reduction to ammonia.14–18 However, Cu catalysts, especially Cu nanoparticles, suffer from significant stability issues because they are prone to oxidation, aggregation, and structural degradation during extended operation. For example, electrodeposited Cu can quickly form surface oxides upon air and electrolyte exposure, which affect the selectivity and yield of ammonia even when they can be reduced back during nitrate reduction.19–22 Furthermore, Cu+ states, which are essential for stabilizing intermediates, are often over-reduced, thereby undermining catalyst integrity.23,24 Metallic Cu nanoparticles are also susceptible to coalescence and dissolution, leading to active surface area loss and performance decay. Prior studies have shown that Cu nanoparticles, despite their high activity, are vulnerable to dynamic morphological changes that compromise long-term stability.25–31
To address these challenges, we hypothesize that confining Cu nanoparticles in a microenvironment can create a barrier that limits their aggregation and degradation during nitrate reduction, stabilizing the catalyst. Herein, we test this hypothesis by encapsulating Cu nanoparticles inside carbon nanotubes (CNTs). Encapsulation provides a physical barrier that limits particle–particle contact, which is necessary for aggregation. The isolation of Cu nanoparticles between different CNTs also impedes Ostwald ripening, which is another pathway for the degradation of nanoparticle catalyst. By comparing the catalyst morphology and selectivity of electrochemical nitrate reduction for Cu nanoparticles on CNTs vs. encapsulated inside the CNTs, the effectiveness of the strategy is directly demonstrated.
To synthesize Cu-confined CNTs catalysts (denoted Cu-in-CNT), 35 mg of acid-treated CNTs were impregnated with 1 mL of 0.8 M Cu(NO3)2 in acetonitrile. The mixture was sonicated and stirred for 30 min, followed by the dropwise addition of 0.5 mL deionized water. After an additional 30 min of sonication, the resulting material was dried at 100 °C for 10 h. To remove any Cu species attached to the external surface, the dried sample was washed with 1 M HCl, then dried again at 80 °C for 14 h. Finally, the material was calcined at 400 °C under an Ar atmosphere for 3 h to yield the Cu-in-CNT catalyst. Controlling the presence of Cu particles within CNTs was challenging due to the washing step, so their content was quantified using ICP-OES analysis post-synthesis. The maximum loading achieved for Cu-in-CNT was 2 wt%, beyond this, Cu particles attached to the CNT's exterior surface as well.
To prepare Cu-attached CNTs (denoted Cu-on-CNT), the CNTs were first refluxed at 35% HNO3 to close the tube ends, following a previously reported method.32,33 The end-closed CNTs were then impregnated with Cu(NO3)2·3H2O solution using the incipient wetness impregnation method (water was used as the solvent instead of acetonitrile). The same drying, washing, and calcination procedure as described for Cu-in-CNT was applied to yield the Cu-on-CNT catalyst except washing with 1 M HCl.
A schematic illustration of Cu-in-CNT and Cu-on-CNT is shown in Fig. 1a. TEM provides direct structural evidence supporting the selective positioning of Cu nanoparticles in/on CNTs, thereby confirming the successful synthesis of the two distinct samples. The TEM image for the Cu-in-CNT in Fig. 1b clearly shows that Cu nanoparticles are placed inside the hollow cores of the CNTs. These confined particles exhibit an average particle size of ∼8.7 nm, indicating controlled nucleation and growth. The TEM image for the Cu-on-CNT reveals that Cu nanoparticles of comparable size (∼9.5 nm) are distributed on the outer surface of the CNTs. The particle size distributions for both samples are shown in Fig. S1. The slight difference in particle size between the encapsulated and surface-attached Cu nanoparticles suggests that spatial confinement within the CNTs limits particle growth. The Cu loadings were quantified by ICP-OES to be 2.0 wt% for Cu-in-CNT and 12.7 wt% for Cu-on-CNT.
Cu/CNT with varying Cu loadings were also synthesized, and annular dark-field scanning transmission electron microscopy (ADF-STEM) images were acquired (Fig. S2 and S3). In ADF-STEM, heavier elements such as Cu exhibit brighter contrast, enabling clear visualization of Cu nanoparticles inside the hollow channels of CNTs. These images reveal that at Cu loadings up to 2 wt%, the nanoparticles are effectively encapsulated within the CNTs, with no detectable Cu on the outer surfaces. At 3.5 wt% loading, Cu nanoparticles start to show up at the exterior of the CNTs in addition to the interior, confirming controlled encapsulation at lower loadings. Further structural analysis was conducted on the HR-TEM image of Cu-in-CNT (shown in Fig. S4), which shows the crystalline nature of the Cu nanoparticles. The symmetry and spacing of the spots in the Fourier-transformed image correspond to metallic Cu. The lattice fringes observed in the HRTEM image exhibit a d-spacing of approximately 0.21 nm, which is indexed to the (111) plane of metallic Cu. In contrast, the Cu-on-CNT sample exhibits a less symmetric FFT pattern, along with lattice fringes showing an interplanar spacing of approximately 0.21 nm and 0.25 nm, which can be attributed to the (111) planes of metallic Cu and CuO, respectively.
To further characterize the structure of the catalysts, Cu-in-CNT and Cu-on-CNT samples were analyzed using XRD. As shown in Fig. 1c, a prominent peak at ∼26° is observed in both cases, corresponding to the (002) of graphitic carbon, confirming the presence and structural integrity of the CNT framework. For the Cu-on-CNT sample, well-defined diffraction peaks at 43.3° and 50.4° are observed, which are assigned to the (111) and (200) planes of metallic Cu, respectively. Additional peaks at 35.4° and 38.6° correspond to the (002) and (111) planes of CuO, indicating partial oxidation of the Cu nanoparticles. The presence of CuO is likely due to surface oxidation upon exposure to air during handling or storage. The XRD pattern of the Cu-in-CNT sample also shows peaks for the (111) and (200) planes of metallic Cu. However, these peaks exhibit slight shifts in position, which is likely due to lattice strain experienced by the Cu nanoparticles confined within the CNTs channels. In contrast, no CuO peaks are detected in the Cu-in-CNT sample, strongly suggesting that encapsulation within the CNTs provides a protective environment that inhibits the oxidation of Cu nanoparticles.
XPS analysis was also performed on both Cu-in-CNT and Cu-on-CNT catalysts to examine their initial oxidation states. For as-synthesized Cu-in-CNT, two prominent peaks at 952.2 and 932.4 eV were observed, corresponding to Cu 2p1/2 and Cu 2p3/2 spin–orbit couplings, respectively. The absence of satellite peaks confirmed that Cu-in-CNT primarily contained Cu(I) and/or Cu(0), with no detectable Cu(II) (Fig. 1d). In contrast, the as-synthesized Cu-on-CNT sample exhibited Cu 2p1/2 and Cu 2p3/2 at 952.4 and 942 eV, respectively, along with distinct satellite peaks around 962.2 and 942 eV, indicating the presence of Cu(II) (Fig. 1d). To further differentiate between Cu(I) and Cu(0), since their Cu 2p binding energies overlap, Auger LMM spectra were recorded. The Auger kinetic energy analysis (Cu(0) at 918.6 eV, Cu(I) at 916.7 eV, Cu(II) at 917.8 eV) revealed that the Cu-in-CNT catalyst predominantly contained metallic Cu(0), while Cu-on-CNT displayed a broad feature spanning the Cu(II) to Cu(0) region (Fig. S5).
To investigate the redox behavior of Cu in different environments, cyclic voltammetry (CV) was performed. As shown in Fig. 2a, a pair of redox peaks with a half-wave potential near −0.2 V (vs. Ag/AgCl) was observed, corresponding to the redox of Cu. The Cu-on-CNT sample showed sharper, better-defined peaks with smaller peak-to-peak separation (0.14 V), indicating more reversible electrode kinetics. In contrast, Cu-in-CNT exhibited broader peaks with a larger separation (0.21 V), suggesting a more sluggish redox process, likely due to the limited accessibility of the confined Cu sites. The voltammograms of CNTs without Cu were also recorded, revealing redox peaks centered around −0.12 V superimposed on a capacitive background (Fig. S6). These peaks were attributed to the redox-active functional groups in the CNTs. Baseline correction using these voltammograms enabled accurate determination of the charge associated with Cu (Fig. S7 and S8).
Fig. 2b shows the linear sweep voltammograms of Cu modified CNTs in 0.1 M phosphate buffer, normalized to the mass of electrochemically accessible Cu. In the absence of nitrate, both Cu-in-CNT and Cu-on-CNT showed negligible electrocatalytic activity; however, Cu-in-CNT displayed slightly higher non-faradaic current due to mass normalization. For both catalysts, current began to increase around −1.05 V, attributed to the onset of the hydrogen evolution reaction (HER). Upon addition of KNO3, a significant enhancement in current was observed for both catalysts, with an earlier onset of reduction. Nevertheless, Cu-in-CNT consistently delivered higher current densities across the entire potential range, indicating superior catalytic activity, potentially due to enhanced nitrate-Cu interactions within the confined environment. Notably, for Cu-in-CNT, nitrate can diffuse into the nanochannels from the opening ends of CNT and access the encapsulated Cu. Although the voltammogram of CNTs alone (65% HNO3 treated) confirmed some catalytic activity toward nitrate reduction from CNT, Cu-in-CNT and Cu-on-CNT far outperformed bare CNTs under identical loadings (Fig. S9). Specifically, Cu-in-CNT decreased the overpotential for nitrate reduction by approximately 300 mV (from −1.1 V to −0.8 V) and achieved a current density ∼10× higher than bare CNTs at −1.5 V, underscoring the important catalytic role of Cu nanoparticles.
To evaluate the products of electrochemical nitrate reduction using Cu-in-CNT and Cu-on-CNT, chronoamperometry was performed at various potentials for 2 hours. Following electrolysis, the electrolyte was collected and analyzed to quantify the major water-soluble products, ammonia and nitrite, using the indophenol method and the Griess assay, respectively. Detailed procedures regarding product quantification are provided in the SI Section S1. Calibration curves and corresponding UV-visible spectra for the ammonia and nitrite are shown in Fig. S10. For Cu-in-CNT (Fig. 3a), the faradaic efficiency showed a clear dependence on the applied potential. At a less negative potential, nitrite was the dominant product, indicating its role as an intermediate in the reduction pathway. As the potential became more negative, nitrite formation decreased while ammonia formation increased, reaching a maximum faradaic efficiency of approximately 70 ± 6% at −1.2 V vs. Ag/AgCl. Beyond this potential, ammonia formation remained relatively constant, while nitrite continued to decrease, suggesting the onset of competing hydrogen evolution without further improvement in ammonia formation. For Cu-on-CNT (Fig. 3b), nitrite remains the dominant product at potentials more positive than −1.2 V. However, at −1.3 V and more negative potentials, ammonia formation increased significantly, peaking at around 65 ± 6%. At even more negative potentials, the production of nitrogen-containing products is overtaken by HER. The slightly lower ammonia selectivity for Cu-on-CNT (65% vs. 70% for Cu-in-CNT) suggests that the confinement in Cu-in-CNT may offer a slight advantage in ammonia selectivity. As a control, 65% HNO3-treated CNTs was subjected to chronoamperometry at various potentials for the nitrate reduction reaction (Fig. S11). For bare CNTs, nitrite is the predominant product in the potential range of −1.2 to −1.4 V (∼50%). In contrast, the presence of Cu nanoparticles shifts the selectivity towards ammonia, making it the main product within this potential window (−1.2 to −1.5 V). These observations suggest that Cu might be the active sites that allow further reduction of the intermediate nitrite, which is accessible via the opening at the CNT tips. A maximum faradaic efficiency of ∼56% toward ammonia was observed at −1.5 V for bare CNTs, confirming the significant role of Cu in enhancing the nitrate reduction kinetics at less negative potentials (∼70% at −1.2 V).
After confirming the product distribution across various potentials, we investigated the effect of Cu loading on selectivity first for Cu-in-CNT. A maximum Cu loading of 2 wt% was achieved, as higher loadings (e.g., 3.5 wt%) resulted in additional Cu attachment to the exterior CNTs as verified by ADF-STEM (Fig. S2). As shown in Fig. S12a, both ammonia selectivity and overall nitrate conversion efficiency increase with Cu loading, reaching ∼70% and ∼100%, respectively, at 2 wt% Cu. At 3.5 wt% loading (which contains additional Cu outside CNT), although the overall nitrate reduction was 100%, the selectivity for ammonia is lower, which is likely due to the contribution of exterior Cu nanoparticles. We also attempted to study the effect of Cu loading for Cu-on-CNT, and the results are summarized in Fig. S12b.
We subsequently evaluated the stability of the catalysts for electrochemical nitrate reduction. Chronoamperometry was conducted at the most optimized potential for each catalyst over 12 hours. As shown in Fig. 4a, Cu-in-CNT maintains a high total Faradaic efficiency, close to 100% at 2 h, and gradually decreases to ∼80% after 12 h. Notably, ammonia selectivity decreases from ∼70% to ∼30%, while nitrite increases from ∼30% to ∼50%, indicating a shift in product distribution (from ammonia to nitrite) while sustaining the overall selectivity of ∼80%. Cu-on-CNT (Fig. 4b) shows a significant performance drop, with the total Faradaic efficiency decreasing from ∼100% at 2 h to ∼40% at 12 h. Both ammonia and nitrite production decline considerably, with ammonia dropping from ∼65% to ∼15% and nitrite from ∼35% to ∼25%. ICP-OES analysis was also performed, which revealed that Cu-on-CNT experienced substantial leaching, with 20.5 wt% of its Cu content lost to the solution, whereas Cu-in-CNT showed only 5.3 wt% Cu loss. This analysis supports our hypothesis that confining Cu nanoparticles inside CNTs significantly enhances their electrochemical stability compared to Cu-on-CNT.
The structure and phase stability of the catalysts after electrochemical nitrate reduction were evaluated using TEM and XRD, respectively. Fig. 5 shows the TEM image of Cu-in-CNT, revealing that the Cu nanoparticles largely retained their encapsulated structure within the CNTs, with an average size of ∼8.0 nm (see also Fig. S13a). This observation confirms that the confinement of Cu nanoparticles within CNTs effectively prevents their agglomeration or loss during the reaction. However, some particles still migrated within the CNTs. In contrast, the TEM image of Cu-on-CNT shows particles with a broader size distribution, with particles as large as ∼15–20 nm, and others that have broken down to ∼3 nm (Fig. S13b). To further investigate phase changes, XRD analysis was performed on both catalysts after the reaction. For Cu-in-CNT (Fig. 5b), the XRD pattern confirmed the presence of metallic Cu, indicating no noticeable phase transformation. In contrast, the XRD pattern of Cu on CNTs revealed a complete disappearance of CuO peaks and the appearance of Cu2O peaks, while metallic Cu remained detectable. This shift in phase signifies a notable change in the oxidation state of Cu during the reaction. From these studies, we support that Cu-in-CNT maintains its structural and phase integrity due to the protective role of CNTs confinement.
The post-electrolysis XPS shows that the Cu in Cu-in-CNT maintained its oxidation state, confirming the stability of the metallic Cu species (Fig. 5c). In contrast, Cu-on-CNT exhibited a significant decrease in the Cu(II) component, accompanied by an increase in Cu(I)/Cu(0) signals, suggesting partial reduction of Cu(II) during the reaction (Fig. 5c). Auger spectra further confirmed this transformation: while Cu-in-CNT remained dominated by metallic Cu(0), Cu-on-CNT displayed a pronounced metallic Cu(0) feature alongside residual Cu(II) (Fig. S14). These findings collectively indicate that Cu-in-CNT maintains its metallic state throughout the process, whereas Cu-on-CNT undergoes reduction from Cu(II) to Cu(0).
Footnote |
† Equal contribution. |
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