Abstract
Electroreduction of nitrite to ammonia has significant promise for economical NH3 electrosynthesis and wastewater treatment. Herein, sulfur vacancies rich Cu─N co‐doped SnS2 nanosheet is designed as a highly active and durable NO2RR catalyst. Benefiting from the Cu─N co‐doped strategy, Cu/N‐SnS2‐x achieves the highest NH3 yield rate of 18.15mg h−1 mgcat −1 at −0.935 V (vs RHE) and excellent Faradaic Efficiency of 95.73% at −0.835 V (vs RHE). In situ FT‐IR and in situ XPS proves that Cu/N‐SnS2‐x has a greater capacity for atomic hydrogen generation, which facilitates the conversion of nitrite to ammonia and maintains excellent structural stability during the NO2RR process. Theoretical calculations reveal that the introduced sulfur vacancies effectively expose the metal atoms inside SnS2 and make them adsorb nitrite efficiently, which effectively accelerates the transformation of nitrite to ammonia. Besides, the introduced Cu and N can form a new electronic structure, which induces Cu in an electron‐deficient state promotes the adsorption of reaction intermediates on Cu, and reduces the reaction energy barrier for nitrite reduction on the Cu/N‐SnS2‐x surface. The current exploration presents fresh prospects for the rational development of an effective electrocatalyst for synthesizing ammonia from nitrite.
Keywords: 2D material, electrocatalyst, nitrite reduction, SnS2
In this work, the co‐introduction of Cu and N efficiently improves the NO2RR performance of pristine‐SnS2. Cu, N co‐doped SnS2 with abundant sulfur vacancies which effectively enhance the conversion of nitrite and achieves a superior NH3 yield of 18.15mg h−1 mgcat −1 and Faradic efficiency of 95.73%.

1. Introduction
Ammonia (NH3), one of the most commonly used industrial products, is in high demand in agriculture and industry due to its fundamental attribute of carbon‐free hydrogen carriers, high‐energy density, and low emissions.[ 1 ] Currently, NH3 is produced industrially by Haber–Bosch process at hightemperatures and pressure, which not only consumes a lot of energy but also produces a lot of CO2.[ 2 ] Electrochemical nitrogen reduction reaction (NRR) is regarded as a green ammonia manufacturing pathway due to its mild reaction conditions and environmental benefits.[ 3 ] Nevertheless, the insufficient N2 conversion as well as the strong nonpolar N2 bond and restricted solubility under ambient conditions limit the development of the NRR process.[ 4 ] Thus, it is critical to discover another promising nitrogen‐containing source to manufacture ammonia, which will play an important role in the future energy system.[ 5 ] By contrast, electrochemical NH3 synthesis via NOx − reduction reaction (NOx −RR) with lower N═O bond energy (204 kJ mol−1), which can be obtained from the atmosphere and sewage, is more conducive to efficient NH3 synthesis.[ 6 ] Furthermore, NOx − is widespread in groundwater, posing a persistent threat to human health.[ 7 ] Thus, NOx − is a suitable N‐source for ammonia electro‐synthesis from an environmental standpoint.[ 8 ] However, a major obstacle to the conversion of NOx − to NH3 is the intricate multi‐electron transfer.[ 9 ] Therefore, it is particularly desirable to use high‐performance electrocatalysts for selective NH3 generation via NOx −RR.[ 10 ]
Nowadays, 2D materials like graphene,[ 11 ] transition metal dichalcogenides (TMDs),[ 12 ] black phosphorus,[ 13 ] and few‐layer MXenes,[ 14 ] have gained significant interest in catalytic, electronics, photonics, and optoelectronics applications due to the specific 2D confinement of electron motion and optical properties.[ 15 ] In contrast to graphene with near zero bandgap and unstable black phosphorus, 2D transition metal dichalcogenides (TMDs) are semiconductors with excellent stability and wide bandgaps that range from 1 to 2.5 eV., which makes TMDs excellent candidates as electrocatalysts.[ 16 ] Amidst TMDs, SnS2 is a semiconductor of the CdI2‐type with layered non noble metal sulfide, exhibiting exceptional electrical activity, a sufficient bandgap, and excellent carrier mobility.[ 17 ] SnS2 exhibits significant stability in oxidation resistance in addition to excellent stability in electrolytes.[ 18 ] However, the intrinsic activity of pristine SnS2 still cannot meet the increasing requirement for highly efficient and reliable electrocatalysts for future energy conversion and storage systems, thus it is urgent to further modify SnS2 to build a highly efficient NOx −RR catalyst.
Doping has been one of the most commonly employed techniques for controlling catalytic activity and selectivity when building heterogeneous catalysts.[ 19 ] The base material coordination environment and electrical configuration can be dramatically changed by adding foreign elements as dopants, which improves the catalytic properties of the material.[ 20 ] Recent reports elucidate that modification of SnS2 by doping with heteroatoms is a viable and effective means of enhancing NOx − reduction capacity of SnS2.[ 21 ] Zhang et al., successfully doped Fe into SnS2 to form sulfur vacancies rich Fe‐SnS2 by hydrothermal method and suggest that the generation of sulfur vacancies greatly enhanced the number of active sites, and the introduction of Fe further adjusted the electronic structure of the metal sites, which effectively lowered the reaction energy barriers of the intermediates in the reduction process of NOx − and facilitated the high speed of NH3 production, demonstrating that heteroatom doping is an effective method to modify SnS2.[ 22 ] Besides, typical nonmetallic elements (N, P, and S) can effectively balance the adsorption and desorption to intermediates for the redistribution of atomic charge around dopants.[ 23 ] Therefore, it is a promising catalyst designing a strategy to further introduce new non‐metallic elements into SnS2 to enhance its NOx − reduction ability.
In line with these requirements, a simple hydrothermal method was applied to introduce Cu and N into the SnS2 structure. Benefiting from the Cu─N co‐doped strategy, Cu/N‐SnS2‐x achieves the highest NH3 yield rate of 18.15mg h−1 mgcat −1 at −0.935 V(vs RHE) and Faradaic Efficiency of 95.73% at −0.835 V(vs RHE), ESR experiments and in situ FT‐IR test prove Cu/N‐SnS2‐x has a greater capacity for atomic hydrogen generation, which facilitates the conversion of nitrite to ammonia. Theoretical calculations revealed the introduced N element could induce Cu in an electron‐deficient state, which promotes the adsorption of Cu on nitrogen‐containing intermediates and reduces the reaction energy barrier for nitrite reduction. Besides, in situ Raman test and long‐term i‐t test prove the excellent stability of Cu/N‐SnS2‐x, suggesting the practicality of industrial applications.
2. Results and Discussion
Cu/N‐SnS2‐x was synthesized by the one‐step hydrothermal method. The Supporting Information presents additional details about the synthesis procedure (Figure 1 ).
Figure 1.

Schematic illustration of the synthesis process of Cu/N‐SnS2‐x.
In order to determine the phase structure and crystallinity of each sample, X‐ray diffraction (XRD) was first applied. As shown in Figure 2a, all sample's peaks have been identified as SnS2 (JCPDS No.23‐0677) in the absence of any noticeable contaminants.[ 17a ] Furthermore, all the peaks of Cu/N‐SnS2‐x, N‐SnS2‐x, and Cu‐SnS2‐x are notably weaker compared to those of pristine SnS2 indicating the lower crystallinity of Cu/N‐SnS2‐x, N‐SnS2‐x, and Cu‐SnS2‐x caused by the doping procedure. The morphology of all generated samples was initially investigated using scanning electron microscopy (SEM). SEM images of SnS2 (Figure S1a, Supporting Information) and Cu/N‐SnS2‐x (Figure 2b) revealed that synthesized samples were made up of ultrathin nanosheets and were arbitrarily coupled to create nanoflowers and specifically, the large gaps between the nanosheets can provide good electrolyte‐Cu/N‐SnS2‐x interaction, leading to the quick conversion of nitrite to ammonia.[ 24 ] Transmission electron microscopy (TEM) images further revealed the nanoflower structure of SnS2 (Figure S1b, Supporting Information) and Cu/N‐SnS2‐x (Figure 2c) with uniform size.
Figure 2.

a) XRD patterns. b) SEM image of Cu/N‐SnS2‐x. c) TEM image of Cu/N‐SnS2‐x. d) AFM image of Cu/N‐SnS2‐x. e) HRTEM image of Cu/N‐SnS2‐x and the corresponding line intensity profiles in A, B, and C regions. f) Element mapping images of Cu/N‐SnS2‐x.
Atomic force microscopy (AFM) analysis was also performed to estimate the thickness Cu/N‐SnS2‐x. As shown in Figure 2d, the topography of the Cu/N‐SnS2‐x reveals a nanosheet morphology with a thickness of ≈4–5 nm which is consistent with the results of SEM and TEM. Besides, the BET result reveals the specific surface area of Cu/N‐SnS2‐x is 320.36 m2 g−1, suggesting Cu/N‐SnS2‐x exhibits a relatively high surface area (Figure S4, Supporting Information). To further investigate the crystal structure and the existence of sulfur vacancy in Cu/N‐SnS2‐x, high‐resolution transmission electron microscopy (HRTEM) was further applied. Figure 2e shows fine lattice fringes with a spacing of 0.599 nm which is assigned to the (001) facet of SnS2, suggesting the successful synthesis of SnS2, this result is also consistent with the DFT calculation results (Figures S5 and S6, Supporting Information). Line intensity profiles generated from noise‐filtered pictures revealed continuously and evenly ordered lattice atoms in Cu/N‐SnS2‐x, indicating the strong crystallinity of Cu/N‐SnS2‐x. In addition, the strategy of doping Cu and N significantly reduced the crystallinity of SnS2, as evidenced by blurry and discontinuous lattice fringes seen in Cu/N‐SnS2‐x (Selected area C in Figure 2e) and the loss of certain lattice atoms directly supporting the creation of sulfur vacancies.[ 25 ] Furthermore, as shown in Figure 2f, element mapping images obtained through energy‐dispersive spectroscopy (EDS) show the even contribution of Cu, N, Sn, and S, which strongly confirms the successful introduction of Cu and N.
Raman spectroscopy was utilized to validate the existence of Cu/N‐SnS2‐x. The signal at 312 cm−1, which corresponds to the A1g mode of SnS2, indicated the presence of SnS2 (Figure 3a).[ 26 ]Besides, the A1g peak intensity was decreased due to the introduction of Cu and N. In this case, the introduction of N element is not obvious for the attenuation of the characteristic Raman peak of SnS2, while the introduction of Cu element plays an obvious attenuation of the characteristic peak, indicating that the introduction of the metal Cu element plays a key role in the attenuation of the SnS2 crystals. The electron spin resonance (ESR) method was further applied to confirm the existence of sulfur vacancies in Cu/N‐SnS2‐x. The ESR spectra (Figure 3b) revealed a detectable signal at a g value of 2.003, indicating unsaturated unpaired electrons caused by the existence of S vacancies. In detail, the ESR spectra of N‐SnS2‐x, Cu‐SnS2‐x, and Cu/N‐SnS2‐x all indicate the existence of S vacancies on their surface. However, N‐SnS2‐x exhibits the lowest S vacancies concentration compared to Cu‐SnS2‐x and Cu/N‐SnS2‐x, whereas the concentration of S vacancies increases dramatically when the metal Cu is introduced, suggesting that the metal element Cu is the key to increase the concentration of sulfur vacancies.[ 27 ] X‐ray photoelectron spectroscopy (XPS) was used to determine the chemical characteristics of prepared materials. First, the XPS survey (Figure S4, Supporting Information) shows the existence of Cu, N, Sn, and S and the corresponding atomic ratios are 2.83at%, 3.72 at%, 21.8at%, and 39.78 at%, respectively. Figure 3c illustrates a detailed inspection of the Cu 2p XPS fine spectra, which verifies the presence of Cu 2p3/2 and Cu 2p1/2 due to the unique peaks found at 932.6 and 952.4 eV, respectively, implying Cu exists in Cu/N‐SnS2‐x.Besides, Auger electron spectroscopy (AES) was further applied to determine the existing state of Cu, the Cu LMM AES spectrum shows a distinct peak at 569 and 570 eV, contributing to the existence of Cu2+ and Cu1+. The ratio of Cu2+ and Cu1+ is 1(33%):2(67%), indicating the main valence state is Cu1+ and further proving the successful doping of Cu.[ 28 ] Besides, as shown in Table S1 (Supporting Information), the ICP‐OES results indicate the percentage of Cu doping is 5.762wt.%. The N 1s XPS spectra and matching peak analyses of Cu/N‐SnS2‐x are displayed in Figure 3d. The emergence of the N─Sn bond at 399.8 eV suggests that partial N atoms have replaced the location of S in SnS2 and heterogeneous N atoms have been successfully induced into SnS2.[ 29 ] Sn4+ levels appear in the XPS spectra for the Sn 3d area for SnS2 and Cu/N‐SnS2‐x at 486.6 eV (Sn3d5/2) and 495.1 eV (Sn3d3/2), respectively (Figure 3e).
Figure 3.

a) Raman patterns. b) ESR patterns. c) XPS Cu2p spectra and Cu LMM AES spectra. d) XPS N 1s spectra. e) XPS Sn3d spectra. f) XPS S2p spectra. g,h) Detailed charge analysis and the corresponding ELF results of SnS2 and Cu/N‐SnS2‐x i) Calculated work functions of SnS2 and Cu/N‐SnS2‐x.
Figure 3f illustrates how the S2p spectra for SnS2 and Cu/N‐SnS2‐x exhibit the S 2p3/2 (161.6 eV) and S 2p1/2 (163 eV) states of S. The Sn 3d and S 2p spectra of Cu/N‐SnS2‐x show a shift to lower binding energies compared to SnS2, which is noteworthy. This shift indicates a reduced valence state and an increased number of electrons in Cu/N‐SnS2‐x due to the presence of sulfur vacancies.[ 27 ]
The electronic structures of SnS2 and Cu/N‐SnS2‐x are further examined by DFT calculations. Detailed charge analysis (Figure 3g(A)–h(A)) reveals the charge exchange after the introduction of Cu and N. Compared to SnS2, Cu/N doping generates sulfur vacancies, which subsequently transfer electrons to neighboring Sn, increasing the charge of Sn. (0.836 |e| vs 0.912 |e| for Sn atom). The electron localization function (ELF) is utilized for assessing electron distribution in SnS2 and Cu/N‐SnS2‐x. As shown in Figure 3g(B)–h(B), Sulfur vacancies cause increased electron localization around the vacancy, resulting in non‐uniform electron distribution and charge transfer around metal atoms.[ 30 ] Besides, the strategy of Cu/N doping can reduce the work function from 6.172 eV of SnS2 to 5.774 eV of Cu/N‐SnS2‐x. As a result, a lower work function of Cu/N‐SnS2‐x could enhance charge transfer from the catalyst surface to the absorbed NO2 − and intermediates, which is favored for the NO2RR process.[ 31 ]
To investigate the electrochemical NO2 − reduction capabilities of Cu/N‐SnS2‐x, electrochemical measurements were tested at room temperature using a typical three‐electrodes system. Before the electrochemical test, cyclic voltammetry (CV) curves were measured until the polarization curves achieved a stable condition. First, electrochemical performance was assessed by linear sweep voltammetry (LSV).[ 32 ] As shown in Figure 4a, the LSV curve of Cu/N‐SnS2‐x in 0.1 m NaOH with 0.1 m NaNO2 shows an obvious increase in current density compared with that without nitrite, indicating that nitrite was involved in the electrochemical reaction.[ 33 ] Furthermore, LSV curves of N‐SnS2‐x and Cu‐SnS2‐x revealed the same trend, but both the current densities were much less than that of Cu/N‐SnS2‐x, which indicates that the co‐doping strategy of Cu and N could synergistically promote nitrite reduction rate. To further reveal the NO2RR enhancement observed in Cu/N‐SnS2‐x, Tafel plots were applied to reveal the catalytic activity of Cu/N‐SnS2‐x, N‐SnS2‐x, and Cu‐SnS2‐x. As shown in Figure 4b, the Tafel slope of Cu/N‐SnS2‐x was ≈358.2 mV dec−1, which was significantly less than 666.7 mV dec−1 for N‐SnS2‐x and 400.6 mV dec−1 for Cu‐SnS2‐x, indicating that Cu/N‐SnS2‐x has relatively rapid kinetics for converting NO2 − to NH3.[ 34 ] Besides, the double‐layer capacitance (Cdl) was measured to determine the electrochemically active surface area (ECSA). As shown in Figure 4c, Cu/N‐SnS2‐x (0.251 mF cm−2) presented a higher Cdl than N‐SnS2‐x(0.122 mF cm−2) and Cu‐SnS2‐x(0.154 mF cm−2), suggesting that Cu/N‐SnS2‐x had more electrochemically active sites derived from the defective structure of Cu/N‐SnS2‐x nanosheets which is favored for NO2RR.[ 35 ]As shown in Figure S5 (Supporting Information), impedance measurements of all four samples indicate the undoped SnS2 exhibits the largest charge transfer resistance, which may be caused by the semiconductor characteristic of SnS2 and its poor conductive properties also contribute to its poor catalytic properties. Whereas, with the introduction of N and Cu elements, the electrical conductivity of SnS2 has been enhanced and Cu/N‐SnS2‐x exhibits a much smaller charge transfer resistance, suggesting Cu/N co‐doping and the introduction of S vacancies can significantly enhance the conductivity of SnS2.
Figure 4.

a) LSV curves b) Tafel plots. c) Cdl values. d) NH3 yields and NH3FEs of Cu/N‐SnS2‐x at different potentials. e) NH3 yields rate and NH3 FE of SnS2, N‐SnS2‐x, Cu‐SnS2‐x, and Cu/N‐SnS2‐x. f) NH3 yields rate and NH3 FE of Cu/N‐SnS2‐x under various nitrite concentrations. g) Blank controls experiment h) 1H‐NMR measurements. i) Comparison NH3 yields of using different detection methods.
To study the NO2RR activity of Cu/N‐SnS2‐x, chronoamperometry tests were performed at various applied potentials and the concentrations of NH3 were further quantified by UV–vis spectroscopy.[ 36 ] As shown in Figure 4d, Cu/N‐SnS2‐x exhibits an outstanding NO2RR performance with an FE of 95.73% at −0.835 V(vs RHE) and NH3 yield of 18.15mg h−1 mgcat −1 at −0.935 V(vs RHE), suggesting the Cu/N‐SnS2‐x has excellent NO2RR performance, which is significantly superior to previous reported materials (Table S3, Supporting Information). Furthermore, the Faradaic Efficiency (FE) of Cu/N‐SnS2‐x first increases and then decreases as the potential decreases, indicating that the FE of ammonia production is related to the applied potential, and this phenomenon can be explained by competition between intermediates containing N and H on the catalyst surface. As a comparison, N‐SnS2‐x and Cu‐SnS2‐x also tested NO2RR performance at the same potentials. As shown in Figure 4e, N‐SnS2‐x and Cu‐SnS2‐x show relatively inferior NH3 yield rates with 7.2 and 18.25 mg h−1 mgcat −1 and the highest FE of N‐SnS2‐x and Cu‐SnS2‐x are 77.13% and 60.32%, respectively, suggesting that the introduction of Cu/N and sulfur vacancy together improvs the NO2RR performance of SnS2. The NO3RR performance of Cu/N‐SnS2‐x was also investigated. As shown in Figure S17c,d (Supporting Information), the NH3 yield rate and FE of Cu/N‐SnS2‐x are significantly lower than NO2RR performance, suggesting NO2 − more suitable as raw material for electrochemical ammonia synthesis. In addition, NO2 − and NO3 − exist in the actual wastewater, thus wastewater simulation experiments are further applied. The composition of simulated wastewater that was selected is 7.1g L−1 Na2SO4; 3.5 g L−1 NaNO3·(40 mm);2.76 g L−1 NaNO2·(40 mm)and 0.7 g L−1 NaCl, and further adjust the initial pH to 13 with 0.1 m NaOH. As shown in Figure S19c (Supporting Information), the maximum ammonia yield in simulated wastewater reaches 5.97 mg h−1 mgcat −1 at the potential of −0.935 V, the ammonia yield gradually increases with the decrease of applied potentials. The highest FE in simulated real wastewater is 67% at −0.835 V (Figure S19d, Supporting Information). The lower FE may be due to the lower concentration gradient on the Cu/N‐SnS2‐x surface due to the relatively low nitrate and nitrite concentration (40 mm), and the wastewater contains other heteroatoms, which limits the mass transfer and adsorption of nitrate and nitrite. To sum up, Cu/N‐SnS2‐x can be used to eliminate excessive nitrate in industrial wastewater, but electrochemical reactor and operating conditions need to be optimized for future practical application.[ 37 ]
To evaluate the adaptability of Cu/N‐SnS2‐x in varied nitrite concentrations, we conducted additional tests utilizing different NO2 − concentration gradients: 0.05m, 0.1 m, and 0.2m NaNO2. Figure 4 shows the LSV curve of Cu/N‐SnS2‐x evaluated at different nitrite concentrations. Cu/N‐SnS2‐x could reduce nitrite at varying nitrite concentrations, as evidenced by the current density's progressive increase with nitrite concentration. As shown in Figure 4f, the NH3 yield rates decrease gradually as the NO2 − concentration decreases and the NH3 yield rates are linearly dependent on the NO2 − concentration, suggesting that the electrochemical reduction of NO2 − to NH3 is a first‐order reaction with respect to the NO2 − concentration. The FEs also demonstrate a downward trend with decreasing NO2 − concentration when the concentration of NO2 − is decreased to 0.05m, Cu/N‐SnS2‐x still delivers a high FE of 74.52% indicating that Cu/N‐SnS2‐x has a potential to be applied to large‐scale industrial production.[ 38 ]
Blank control experiments were further conducted to rule out the possibility of N contamination from the external environment. The extremely low yield of NH3 in the blank electrolyte (Figure 4g) demonstrates that the N of NH3 was derived from NO2 −.[ 39 ] To further verify the N origin of the generated NH3, the 15N isotope labeling experiment combined with the 1H nuclear magnetic resonance (1H‐NMR) technology is undoubtedly the best‐guaranteed method. A set of quantitative 1H‐NMR tests was conducted to prove the authenticity and reliability and according to 1H‐NMR spectra of Figure 4h showing the different concentrations of 14NH4 + and 15NH4 +, the calculated 14NH4 + and 15NH4 + concentrations of Cu/N‐SnS2‐x at −0.935V vs RHE is 180.1 and 180.9µg mL−1, respectively (181.5µg mL−1 using UV–vis) after integrating the obtained peak areas, which further confirming the accuracy of determining NH3 yield rate (Figure 4i). As shown in Figure S18 (Supporting Information), the 1H‐NMR spectra of the electrolyte after electrocatalysis using Na15NO2 as a reactant also showed two peaks corresponding to 15NH4 + and the 1H‐NMR spectrum revealed typical triple peaks corresponding to 14NH4 + while Na14NO2 was used as electrolyte.[ 40 ] This result bears out the fact that the formation of NH3 derives from the NO2 − electroreduction.
Stability is a crucial benchmark to estimate catalysts for potential practical applications. In situ Raman spectroscopy was applied to optimize the structure stability of Cu/N‐SnS2‐x during the reaction. As shown in Figure 5a, when applied potential decreases from −0.535 to −0.935 V, the significant A1g vibration peak of SnS2 remains unchanged at 312 cm−1 during the electrolysis process, indicating the main structure of SnS2 sustains its stability. Besides, in situ XPS was further applied. As shown in Figure 5b,c, the in situ XPS test results of Sn and S show that there is no obvious peak change between Sn and S during the NO2RR process, especially for Sn, there is no existence of Sn2+ and Sn0 during the reaction, which indicates that the main structure of SnS2 is stable. The cyclic stability of Cu/N‐SnS2‐x was shown in Figure 5d under optimal NH3 selectivity reaction conditions. Throughout the recycling trials, the NH3 yield rate and NH3 FE were maintained during the cycling tests, highlighting the exceptional stability of Cu/N‐SnS2‐x in NO2RR applications. Moreover, a continuous electrolysis lasting 72 h i‐t test was performed using an H‐cell reactor as shown in Figure 5e, indicating the remarkable stability of Cu/N‐SnS2‐x. As shown in Figure S27 (Supporting Information), the EIS result of Cu/N‐SnS2‐x after the NO2RR test showed an infinitesimal change compared to the EIS of Cu/N‐SnS2‐x before the NO2RR test, which further proves the excellent stability of Cu/N‐SnS2‐x during the NO2RR process. XRD tests (Figure S30, Supporting Information), TEM image (Figure S31, Supporting Information), HRTEM image(Figure S32, Supporting Information), and XPS results (Figure S33, Supporting Information) of Cu/N‐SnS2‐x after 72h i‐t test show excellent structure stability of Cu/N‐SnS2‐x. Collectively, the post‐test characterization data suggests that Cu/N‐SnS2‐x is chemically stable enough for NO2RR.
Figure 5.

a) In situ Raman test. In situ XPS results of Cu/N‐SnS2‐x under −0.935V b) XPS Sn3d spectra. c) XPS S2p spectra. d)NH3 yields rate and FEs of six‐times recycle test. e) 72 h i‐t test.
In order to further explore the role of a co‐doping strategy for enhanced NO2RR performance, a set of characterizations was applied. First, a cyclic voltammetric test was applied to different samples to evaluate their ability to generate atomic H*, which is an essential component for the following nitrite reduction. The cyclic voltammetric test was applied at the potential range from 0.1 to −1.5V (vs Hg/HgO) in 0.1m NaOH + 0.1m NaNO2, the characteristic peaks of H* appear at 0–−0.15 V (vs Hg/HgO), suggesting the atomic H* was generated during the NO2RR process and involved in the conversion process of nitrite (Figure 6a).[ 41 ] Obviously, Cu/N‐SnS2‐x exhibits a higher intensity of Hads * than Cu‐SnS2‐x, indicating the introduction of N enhanced the ability to generate active hydrogen (Hads *) which is beneficial for nitrite reduction. Furthermore, we conduct ESR measurements using 5,5‐dimethyl1‐pyrroline‐N‐oxide (DMPO) as the Hads * trapping reagent to assess the amounts of Hads * produced or consumed during the NO2RR electrolysis.[ 42 ] As shown in Figure 6b, ESR spectra reveal strong DMPO‐H signals for both Cu/N‐SnS2‐x and Cu ‐SnS2‐x after electrolysis in 0.1m NaOH, implying the strong H2O dissociation capability of Cu/N‐SnS2‐x and Cu‐SnS2‐x to produce abundant *Hads and Cu/N‐SnS2‐x exhibited much stronger ESR intensity than that of Cu‐SnS2‐x, suggesting that the introduction of elemental N further facilitates the promotion of the ability to produce Hads *, which contributes to the successful conduct of the nitrite reduction reaction.[ 30 ] Besides, we used tertiary butanol (t–BuOH) to trap *H, and the NO2RR performance comparison is shown in Figure 6c. When t–BuOH is added, the NO2RR performance of Cu/N‐SnS2‐x is obviously weakened, indicating that the formation of *H can promote the NO2RR process.
Figure 6.

a) Cyclic voltammetry curves of N‐SnS2‐x, Cu‐SnS2‐x, and Cu/N‐SnS2‐x. b) Electron spin resonance spectra of Cu‐SnS2‐x, and Cu/N‐SnS2‐x. c) NH3 yields rate and FEs of Ni‐ Cu/N‐SnS2‐x with and without t–BuOH.d) In situ FT‐IR spectra of Cu ‐SnS2‐x at different potentials for NO2 RR. e) In situ FT‐IR spectra of Cu/N‐SnS2‐x at different potentials for NO2 RR. f) DEMS spectra of Cu/N‐SnS2‐x at different potentials for NO2 RR. d) PDOS of SnS2 e) PDOS of Cu/N‐SnS2‐x f) Adsorption patterns of nitrite on SnS2 and Cu/N‐SnS2‐x surfaces.
In situ attenuated total reflectance surface‐enhanced infrared absorption spectroscopy (ATR‐SEIRAS) was also applied to detect the reaction intermediates adsorbed on Cu‐SnS2‐x (Figure 6d) and Cu/N‐SnS2‐x (Figure 6e) surface during the NO2RR process. When potential decreases from −0.235 to −0.935 V, several peaks appear and increase in intensity in both Cu‐SnS2‐x and Cu/N‐SnS2‐x. Signals were generated at wavenumbers of 1103, 1139, 1202, 1290, 1437, and 1645 cm−1, which respectively represented NH3, NH2, NO2, NH, NH2, and NO adsorbed on the surface of Cu‐SnS2‐x and Cu/N‐SnS2‐x during the reaction, indicating NO2 − effectively transformed to NH3 through a multiple electron transfer process.[ 43 ] However, the signal intensity on the Cu/N‐SnS2‐x surface is much stronger, indicating the Cu─N co‐doping strategy can effectively enhance the process of transformation of NO2 −.In addition, the generation of various H‐containing intermediates indicates that atomic hydrogen (*Hads) generated in Cu/N‐SnS2‐x is further applied to the hydrogenation of NO2 −, which effectively promotes the electrochemical reduction of NO2 − to NH3. Online differential electrochemical mass spectrometry (DEMS) experiments of Cu/N‐SnS2‐x were further applied to detect the intermediates and gas products generated during the NO2RR (Figure 6f). Under the potential of −0.935 V vs RHE, Cu/N‐SnS2‐x produces other gas products in addition to NH3 (17), including m/z signals of NO (30), and NH2 (16) suggesting that the conversion of nitrite to ammonia indeed occurred on Cu/N‐SnS2‐x surface.
To understand the enhanced NO2RR performance of Cu/N‐SnS2‐x caused by dual element doping strategy, density functional theory (DFT) calculations were performed.
We explore the effect of sulfur vacancies and elemental doping on the conductivity of SnS2 by calculating the Projected density of states (PDOS) of the relevant samples. First, as shown in Figure 7a, the PDOS analysis indicates that SnS2 possesses a tangible bandgap indicative of its semiconducting character, suggesting its poor electrical conductivity, which is consistent with the EIS results. In contrast, as S vacancy and Cu─N was introduced, SnS2‐x (Figure S21, Supporting Information) and Cu/N‐SnS2‐x (Figure 7b) exhibit noticeable electronic states crossing the Fermi level, leading to the metallic characteristics of SnS2‐x and Cu/N‐SnS2‐x, thus higher conductivity relative to that of SnS2, which is favorable for the proton‐coupled electron‐transfer process to boost the NO2RR kinetics. Furthermore, we performed the corresponding calculations for the adsorption of nitrite on the SnS2 and Cu/N‐SnS2‐x surfaces. As shown in Figure 7c, NO2 − cannot efficiently adsorb on the SnS2 surface, due to the complete encapsulation of the inner metal sites and the inability of the outer S atoms to efficiently adsorb NO2 −. As for Cu/N‐SnS2‐x, the S vacancies created by Cu/N doping effectively expose the internal metal sites. The exposed Sn sites effectively form an adsorption structure with NO2 −, providing a prerequisite for the subsequent reduction reaction.
Figure 7.

a) PDOS of SnS2 b) PDOS of Cu/N‐SnS2‐x c) Adsorption patterns of nitrite on SnS2 and Cu/N‐SnS2‐x surfaces. d) Calculated free energy changes of nitrite reduction reaction on Cu/N‐SnS2‐x. e) Calculated free energy changes of nitrite reduction reaction on Cu ‐SnS2‐x. In situ XPS results of Cu/N‐SnS2‐x under −0.935V f) XPS Cu2p spectra g) Cu LMM AES spectra. h) XPS N 1s spectra. i,j) Charge density difference of Cu‐SnS2‐x and Cu/N‐SnS2‐x k) Gibbs free energy of hydrogen on different sites of Cu/N‐SnS2‐x.
In order to investigate the reaction pathways for the reduction of nitrite to ammonia, we calculated the Gibbs free energy diagram for the reduction reaction of nitrite on Cu/N‐SnS2‐x (Figure 7d) and Cu‐SnS2‐x (Figure 7e) surfaces, respectively. In detail, nitrite can be successfully transferred into NH3 on Cu‐SnS2‐x and Cu/N‐SnS2‐x surfaces, including the corresponding reaction intermediates (NO2 *, NO*, N*, NH*, NH2 *, NH3 *), suggesting the doping strategy is an effective method to enhance the NO2 − reducing abil of SnS2. From the Gibbs free energy diagram, it is clear that the rate‐limiting step for NO2 − reduction on Cu‐SnS2‐x surface is the formation of N* intermediate, which requires an energy input of 0.88 eV. Besides, the formation of N* intermediate on Cu‐SnS2‐x surface involved the conversion between metal sites, in which Cu atoms effectively adsorb with N and participate in the subsequent reduction reaction, suggesting that Cu is the crucial active site during the NO2RR process. The rate‐limiting step for Cu/N‐SnS2‐x is the formation of the NH2 * intermediate which requires an energy input of 0.65 eV which is lower than the rate‐limiting step of Cu‐SnS2‐x, indicating nitrite is much easier to reduce on Cu/N‐SnS2‐x surface. Besides, due to the further introduction of nitrogen, the Cu site can directly form an adsorption structure with the NO* intermediate in the early stage of the reduction reaction, which participates in the process of the reduction reaction and reduces the reaction energy barrier of the nitrite reduction reaction.
In order to further investigate the role of elemental N doping, the in situ XPS was applied to explore the charge transfer between Cu and N active sites during the NO2RR process. As shown in Figure 7f, Cu XPS results between the applied potential of OCP and −0.935 V vs RHE suggest that Cu2p has not changed significantly and Cu is still 1 + dominant, while the further comparison of the Cu LMM orbitals also reveals that the ratio of Cu2+ is slightly increased to 36%, indicating that Cu will further lose electrons during the NO2RR process, leading to its electron‐deficient state. The XPS results of elemental N show that the overall peak position of N is shifted to the lower binding energy, indicating that N has gained electrons during the reaction process and is in an electron‐rich state, which may be due to its attraction of electrons from the neighboring Cu. Besides, we performed differential charge density calculations for Cu‐SnS2‐x and Cu/N‐SnS2‐x, respectively. As shown in Figure 7i,j, it is clearly found that after N doping, due to the electron‐absorbing property of N, the electrons are further transferred from Cu to N, which makes Cu in an electron‐deficient state. This characteristic makes Cu more favorable to complete the adsorption process of the reaction intermediates, which reduces the corresponding reaction energy barrier and is conducive to the smooth progress of the NO2 − reduction reaction. Furthermore, the hydrogen formation free energy was further investigated on different sites in Cu/N‐SnS2‐x. As shown in Figure 7k, the hydrogen formation free energy on S site is 0.5304 eV, which is much closer to 0 eV compared to Cu sites (1.3483 eV), Sn sites (0.886 eV) and N (−1.772 eV), indicating hydrogen is more likely to adsorb on S sites rather than other active sites on Cu/N‐SnS2‐x.[ 35 ] Besides, the calculation of the adsorption of OH− on different active sites is shown in Figure S35 (Supporting Information), the adsorption energies of t N and S for OH− are both positive, which indicates that these two elements have poor adsorption capacity for OH−, while the adsorption energies of the metallic elements Cu and Sn for OH− are both negative, which indicates that OH− can be adsorbed on the metal active sites. Besides, a specific comparison of the adsorption energies shows that the adsorption capacity of Cu for OH− is stronger than Sn, indicating that OH− will prefer to adsorb on the Cu site. Comparing the adsorption energy of NO2 −, it can be seen that NO2 − is preferentially adsorbed with Sn atoms on the catalyst surface and the adsorption energy is significantly lower than that of OH−, which indicates that Sn also reacts with NO2 − preferentially in the reaction process. This phenomenon facilitates the liberation of metal sites for the preferential adsorption of nitrite and subsequent reactions, further promoting the efficient synthesis of ammonia from nitrite.
Collectively, the enhanced NO2RR performance of Cu/N‐SnS2‐x can be attributed to the following points. First, the S vacancies formed due to the doping process effectively expose the internal metal sites and are further used for NO2 − adsorption and activation. Second, the doped N element can effectively transfer the electrons from Cu to N, make Cu turn into electron‐deficient state and effectively promote the adsorption of Cu to the intermediates of the NO2RR process and reduce the reaction energy barrier. Third, the doped N element effectively enhances the active hydrogen generation capacity of Cu/N‐SnS2‐x, which is favorable to the hydrogenation process with nitrite and enhances its nitrite reduction rate.
3. Conclusion
In summary, sulfur vacancies rich Cu‐N co‐doped SnS2 nanosheet was successfully synthesized by hydrothermal method. Due to the co‐doped strategy, Cu and N were successfully introduced into SnS2 and facilitated the microenvironment in the van der Waals gap which can enhance the adsorption of NO2 − and the generation of Hads. Theoretical calculations revealed the introduced Cu and N could form the unique electron transfer pair leading Cu in the electron‐deficient state promoting the adsorption of nitrogen‐containing intermediates and reducing the energy barrier for nitrite reduction. Benefit from this, Cu─N co‐doped SnS2 achieves the highest NH3 yield rate of 18.15mg h−1 mgcat −1 at −0.935 V(vs RHE) and an excellent Faradaic Efficiency of 95.7% at −0.835 V(vs RHE) which are superior to others Sn‐based electrocatalysts. Our work not only offers a highly active and durable catalyst for NO2RR for NH3 generation but also paves the opportunity for the construction of transition metal sulfide catalysts with high catalytic performance.
Conflict of Interest
The authors declare no conflict of interest.
Supporting information
Supporting Information
Acknowledgements
This work was supported by the National Natural Science Foundation of China (Grant No. 22379112) and the Hebei Province Foundation for the National Natural Science Foundation (Grant Nos. BJ2019056, B2021203016). Subsidy for the Hebei Key Laboratory of Applied Chemistry after Operation Performance (Grant No. 22567616H)
Li H., Wang Y., Wei K., He M., Yan M., Peng F., Gao F., Modifying Microenvironment in Van der Waals Gap by Cu/N Co‐Doping Strategy for Highly Efficient Nitrite Reduction to Ammonia. Adv. Sci. 2025, 12, 2417773. 10.1002/advs.202417773
Data Availability Statement
The data that support the findings of this study are available from the corresponding author upon reasonable request.
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Associated Data
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Supplementary Materials
Supporting Information
Data Availability Statement
The data that support the findings of this study are available from the corresponding author upon reasonable request.
