US20260176774A1
2026-06-25
19/412,903
2025-12-09
Smart Summary: An electrochemical nitrate reduction system helps reduce nitrate levels in water. It uses a special liquid solution that is acidic and contains a high concentration of nitrate. An electrode is part of the system, which is a key component for the process. By applying a specific electrical potential to the electrode, the system prevents unwanted hydrogen gas from forming. This allows the nitrate to be effectively reduced, making the water cleaner. π TL;DR
Disclosed are an electrochemical nitrate reduction system and a method of inducing reduction of nitrate. The electrochemical nitrate reduction system includes an electrolyte including an acidic aqueous solvent and nitrate having a concentration of greater than or equal to about 6 m, and an electrode. The method of inducing electrochemical reduction of nitrate includes preparing an electrochemical device, which includes an electrolyte solution including an acidic aqueous solvent and a nitrate having a concentration of greater than or equal to about 6 m, and an electrode, and applying a potential to the electrode to suppress a hydrogen evolution reaction and induce reduction of the nitrate.
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C25B1/50 » CPC main
Electrolytic production of inorganic compounds or non-metals Processes
C25B1/27 » CPC further
Electrolytic production of inorganic compounds or non-metals; Products Ammonia
C25B11/046 » CPC further
Electrodes; Manufacture thereof not otherwise provided for characterised by the material; Electrodes formed of a single material Alloys
This application claims priority to and the benefit of Korean Patent Application No. 10-2024-0193090 filed with the Korean Intellectual Property Office on Dec. 20, 2024, and Korean Patent Application No. 10-2025-0112657 filed with the Korean Intellectual Property Office on Aug. 13, 2025, the entire contents of which are incorporated herein by reference.
This relates to an electrochemical nitrate reduction system and a method of inducing electrochemical reduction of nitrate.
Research on highly efficient methods of reducing nitrates due to the growing demand for ammonia (NH3 or NH4+), which is used as a fertilizer feedstock and a hydrogen carrier, as well as efforts to remove a nitrate (NO3β), which is a toxic chemical, from various wastewaters is actively underway. Among them, an electrochemical reduction of the nitrates, which may be processed in a short period of operation without requiring a large installation area, is economical.
The electrochemical nitrate reduction reaction involves several hydrogenation and deoxygenation steps, wherein each step competes with a hydrogen evolution reaction (HER). Due to this competition, the nitrate reduction becomes very inefficient. In order to increase the efficiency of the nitrate reduction, an alkali or neutral aqueous solvent may be suggested but has problems of rather lowering the efficiency due to the slow H2O dissociation rate, which limits hydrogen transfer.
An electrochemical nitrate reduction system capable of reducing nitrate with high efficiency and a reduction method are provided, and their operating principles are presented.
In an embodiment, an electrochemical nitrate reduction system includes an electrolyte solution including an acidic aqueous solvent and a nitrate having a concentration of greater than or equal to about 6 m, and an electrode.
In another embodiment, a method of inducing electrochemical reduction of nitrate includes preparing an electrochemical device, which includes an electrolyte solution including nitrate having a concentration of greater than or equal to about 6 m and an acidic aqueous solvent and an electrode, applying a potential to the electrode to suppress a hydrogen evolution reaction and induce reduction of nitrate.
The electrolyte solution according to an embodiment may enable an electrochemical reduction reaction of the nitrate, suppress a hydrogen evolution reaction that is a competitive reaction, and maximize the efficiency of nitrate reduction.
FIG. 1 is a cyclic voltammetry (CV) graph from a tip and substrate electrode associated with the H+/H2 redox reaction at a scan rate of 0.02 V/s in the electrolyte of Comparative Example 1 through the tip generation/substrate collection (TG/SC) mode of a scanning electrochemical microscope (SECM) with a substrate voltage (Es) of 0 V. In the cyclic voltammetry graph, the horizontal axis is the potential (ET) of the tip electrode and the vertical axis is the current (i).
FIG. 2 is a cyclic voltammetry graph associated with the H+/H2 redox reaction at a scan rate of 0.02 V/s in the electrolyte of Example 1 through the TG/SC mode of SECM with Es=0 V.
FIG. 3 is a cyclic voltammetry graph associated with the H+/H2 redox reaction at a scan rate of 0.02 V/s in the electrolyte of Example 2 through the TG/SC mode of SECM with Es=0 V.
FIG. 4 is an UV-vis absorption spectrum of nitrite (NO2β) and ammonia (NH3) from the aliquots after potentiostatic electrolysis through the nitrate reduction reaction from the electrochemical cell using the electrolyte solution of Example 2 as a catholyte.
FIG. 5 is a cyclic voltammetry graph associated with H+/H2 redox reaction in the electrolyte solution of Example 2 at 0.001 V/s through the TG/SC mode of SECM.
FIG. 6 is a cyclic voltammetry graph (CVNO3-) showing the voltage current of nitrate reduction in the electrolyte solution of Example 2 with a scan rate of 0.02 V/s is.
FIG. 7 is a graph showing the ratio (iT,min/iT,max) of the tip electrode minimum current to the tip electrode maximum current according to the concentration of LiNO3 and the ratio (iT,min/iT,max) according to the concentration of LiTFSI.
FIG. 8 is a ΞRct plot showing the change in estimated charge transfer resistance (Rct) according to the concentration of LiNO3 and ΞRct plot according to the concentration of LiTFSI.
FIG. 9 is a graph showing the faradaic efficiency (FE) of NO2β and NH3 according to the concentration of LiNO3.
FIG. 10 is a graph showing ΞRct according to the concentration of NaNO3.
FIG. 11 is a fractional diagram showing the peak area ratios in infrared (IR) spectroscopy of network water, intermediate water, and multimer water according to the concentration of LiTFSI.
FIG. 12 is a fractional diagram showing the IR peak area ratio of network water, intermediate water, and multimer water according to the concentration of LiNO3.
FIG. 13 is a graph showing the radial distribution functions (RDFs) of Li+ to H2O at various concentrations of LiNO3.
FIG. 14 is a graph showing the RDFs of Li+ to H3O+ at various concentrations of LiNO3.
FIG. 15 is a molecular dynamics snapshot representing the solvation structure of 9 m LiNO3 acid electrolyte solution.
FIG. 16 is a graph showing the coordination numbers of Li+ with H3O+ as a function of the concentration of LiNO3.
FIG. 17 is a schematic illustrations of the electrical double layer during H+ reduction occurs on a Pt electrode in an acidic LiNO3-based hydronium-in-salt electrolyte (HISE).
FIG. 18 is a graph showing the average collection efficiency (Neff, iS/iT) according to the tip electrode potential (ET) when HNO3 was added as an acidic raw material to the electrolyte solution of Example 2.
FIG. 19 is a graph showing Neff according to ET for the case where HNO3 was not added to the electrolyte solution of Example 2.
Hereinafter, embodiments of the present invention are described in detail so that those of ordinary skill in the art can easily implement the present invention. However, this disclosure may be embodied in many different forms and is not construed as limited to the example embodiments set forth herein.
Hereinafter, βcombination thereofβ refers to a mixture, a laminate, a composite, a copolymer, an alloy, a blend, or a reaction product of constituents.
Herein, it should be understood that terms such as βcomprises,β βincludes,β or βhaveβ are intended to designate the presence of an embodied feature, number, step, element, or a combination thereof, and it does not preclude the possibility of the presence or addition of one or more other features, number, step, element, or a combination thereof.
Herein, βorβ is not to be construed as an exclusive meaning, for example, βA or Bβ is construed to include A, B, A+B, and the like.
In an embodiment, a electrochemical nitrate reduction system includes an electrolyte solution including an acidic aqueous solvent and a nitrate having a concentration of greater than or equal to about 6 m, and an electrode.
The nitrate concentration in the electrolyte solution means the number of moles of the nitrate per weight of the acidic aqueous solvent, and the unit, m, means a molal concentration. When an electrolyte solution satisfying the nitrate concentration of greater than or equal to about 6 m is applied, the competing reaction, the hydrogen evolution reaction (2H++2eβ>H2), may be suppressed, while inducing the electrochemical nitrate reduction reaction with efficiency.
The nitrate concentration in the electrolyte solution may be, for example, greater than or equal to about 6 m about 9 m, for example, about 6 m to about 9 m, about 6.5 m to about 8.5 m, about 6 m to about 8 m, about 6 m to about 7 m, about 7 m to about 9 m, or about 7 m to about 8 m but is not limited thereto. If the electrolyte concentration is less than about 6 m, the efficiency of the nitrate reduction reaction may sharply drop. In addition, if the electrolyte concentration is greater than about 9 m, hydronium ions (H3O+) may not be dissolved in the solvent, thereby not forming an acidic aqueous solvent, which may resultantly fail in inducing the nitrate reduction reaction or deteriorate the efficiency
Types of the nitrates are not particularly limited but may include LiNO3, NaNO3, or a combination thereof, for example, LiNO3.
In the acidic aqueous solvent, the hydronium ions (H3O+) may be at a concentration of about 5 mM to about 100 mM, for example, about 5 mM to about 80 mM, about 5 mM to about 60 mM, about 5 mM to about 50 mM, or about 10 mM to about 100 mM. A unit of mM stands for millimolar concentration. If the concentration of the hydronium ions in the solvent is within the ranges, the nitrate reduction reaction may proceed with high efficiency.
A source of the hydronium ions in the acidic aqueous solvent is not particularly limited but may be, for example, HNO3. In other words, the acidic aqueous solvent may include HNO3.
The electrode is not particularly limited but may include Ag, Co, Cu, Fe, Ni, Pt, Ti, or a combination thereof. For example, the electrode may include Pt. The Pt electrode is an electrode that is advantageous for the hydrogen evolution reaction but disadvantageous for the nitrate reduction reaction, and if applying the electrolyte solution according to an embodiment, even when the Pt electrode is used, the nitrate reduction reaction may be induced with high efficiency.
According to the analysis described below, the electrolyte solution forms not a water-in-salt but a hydronium-in-salt as a solvation structure, which may suppress the hydrogen evolution reaction but effectively proceed the nitrate reduction reaction.
The hydronium-in-salt may be formed by a strong interaction of H3O+ and Li+NO3β (or Na+NO3β). The hydronium-in-salt may include H3O+-in-Li+NO3β or H3O+-in-Na+NO3β.
The reduction of nitrate according to an embodiment may include the following Chemical Equation 1 and/or Chemical Equation 2.
NO3β+2H++2eββNO2β+H2Oββ[Chemical Equation 1]
NO3β+9H++8eββNH3+3H2Oββ[Chemical Equation 2]
According to an embodiment, nitrite (NO2β) and/or ammonia (NH3) are produced by the reduction reaction of nitrate.
In another embodiment, an electrochemical method includes preparing an electrochemical device, which includes an electrolyte solution including nitrate having a concentration of greater than or equal to about 6 m and an acidic aqueous solvent and an electrode, applying a potential to the electrode to suppress a hydrogen evolution reaction and induce reduction of nitrate.
The applying of the potential may be referred to as potentiostatic bulk electrolysis.
The potential may be a negative potential range in which a hydrogen evolution reaction (HER) occurs at the applied electrode, for example, about β0.1 V to about β2.0 V, or about β0.2 V to about β1.5 V, or about β0.4 V to about β1.2 V relative to the point of zero charge (PZC).
Hereinafter, specific examples according to an embodiment are described.
An electrolyte solution according to Comparative Example 1 was prepared by dissolving 5 mM of HNO3 and 0.1 m of LiNO3 in distilled water.
After adjusting a distance between the tip and Pt substrate ultra-microelectrodes (UMEs; dT-S) to 3.5 ΞΌm in a scanning electrochemical microscope (SECM), the electrolyte solution of Comparative Example 1 was injected thereinto to perform a cyclic voltammetry (CV) analysis by setting a substrate potential (Es) to 0 V and scanning a tip potential (ET) from 0 V to β0.8 V at a scan rate of 0.02 V/s in a tip generation (TG)/substrate collection (SC) mode, and the results are shown in FIG. 1.
Referring to a cyclic current-voltage graph of FIG. 1, no side reactions occurred as H+/H2 redox cycles progressed, and no current decrease due to H2 bubbles was observed. Accordingly, this confirmed that LiNO3 was electrically inactive at low concentrations.
An electrolyte solution according to Example 1 was prepared by dissolving 15 mM of HNO3 and 6 m of LiNO3 in distilled water. The electrolyte solution of Example 1 was subjected to the cyclic current voltammetry analysis in the same manner as in Comparative Example 1, and the results are shown in FIG. 2.
An electrolyte solution according to Example 2 was prepared by dissolving 5 mM of HNO3 and 9 m of LiNO3 in distilled water. The electrolyte solution of Example 2 was subjected to the cyclic current voltammetry analysis in the same manner as in Comparative Example 1, and the results are shown in FIG. 3.
Referring to FIGS. 2 and 3, the electrolyte solutions at greater than or equal to about 6 m of LiNO3 exhibited voltage and current drops in both forward and backward directions. Accordingly, in Examples 1 and 2, H+ hopping was expected to be significantly interrupted.
For comparison, an electrolyte solution according to Comparative Example 2 was prepared by dissolving 5 mM of HClO4 and 9 m of LiTFSI in distilled water and then, subjected to the cyclic current voltammetry analysis in the same manner as in Comparative Example 1. However, in this case, no voltage and current drops occurred. An electrolyte solution according to Comparative Example 3 was prepared by dissolving 1 mM of [Fe(CN)6]3β and 9 m of LiNO3 in distilled water and then, subjected to the cyclic current voltammetry analysis according to [Fe(CN)6]3β/[Fe(CN)6]4β redox reaction in the same manner as in Comparative Example 1. However, in this case, no graphs like FIGS. 2 and 3 appeared.
It was confirmed that the voltage and current drops as shown in FIGS. 2 and 3 appeared only in the acidic electrolyte solutions having a nitrate concentration of greater than or equal to about 6 m. It was understood that a hydrogen evolution reaction was suppressed by irreversibly generated by-products. Herein, an electrochemical nitrate reduction was understood to be the most likely side reaction. Hereinafter, this is explained through UV-vis spectroscopic titration.
A three electrode cell was manufactured by using Pt as an operation electrode | the electrolyte solution of Example 2β₯ the electrolyte solution of Example 2 as a catholyte | a carbon felt as a counter electrode. This cell was subjected to potentiostatic bulk electrolysis at an operation electrode potential of β0.7 V to obtain a reduction potential of 2 C, inducing nitrate reduction. Subsequently, a catholyte sample was collected therefrom and then, mixed with colorants respectively detecting NO2β and NH3 to perform the UV-vis spectral analysis, and the results are shown in FIG. 4.
Referring to FIG. 4, it was confirmed that nitrite (NO2β) and ammonia (NH3) were formed by the nitrate reduction reaction. When measured from the UV-vis absorption peaks, NO2β was at a concentration of 13.1%, NH3 was at a concentration of 50.7%, and in addition, NO2β exhibited faradaic efficiency of Β±2.1%, and NH3 exhibited faradaic efficiency of Β±5.9%.
In the previous SCEM, the electrolyte solution of Example 2 was subjected to CVs at the scan rate of 0.02 V/s, but this time, the CVs was performed at a scan rate of 0.001 V/s, and the results are shown in FIG. 5. Referring to FIG. 5, as the tip potential (ET) shifted toward a negative direction from the forward direction by greater than or equal to β0.4 V, significant voltage and current drops occurred. These voltage and current drops were induced by the nitrate reduction reaction, which was understood to be controlled by an adsorption process on the tip electrode surface.
A current (iT,NO3-RR) due to the nitrate reduction reaction may be calculated by subtracting a current (iT,HER) due to the hydrogen evolution reaction from a total current (iT). However, a current (iS) in the substrate, which is a flux of H2 generated at the tip electrode, and the current (iT,HER) in the hydrogen evolution reaction have the same absolute value. Accordingly, an absolute value of a current (iT,NO3-RR) due to the nitrate reduction reaction may be obtained by subtracting the substrate current (iS) from the absolute value of the tip current (iT), wherein the absolute value of the current (iT,NO3-RR) was used to derive a voltage current CVNO3- of the nitrate reduction at the 0.02 V/s, as shown in FIG. 6.
Referring to FIG. 6, NO3β started to be electrically reduced at about β0.3 V and stopped at β0.4 V, where the voltage and current drops started. This indicates that the hydrogen evolution reaction was significantly suppressed, while the nitrate reduction reaction was maximized.
Subsequently, the effect of nitrate concentrations was analyzed.
In addition to Comparative Example 1 and Examples 1 and 2, the electrolyte solution of Comparative Example 4 was prepared by dissolving 5 mM of HNO3 and 3 m of LiNO3 in distilled water, the electrolyte solution of Example 3 was prepared by dissolving 5 mM of HNO3 and 7 m of LiNO3 in distilled water, and the electrolyte solution of Example 4 was prepared by dissolving 5 mM of HNO3 and 8 m of LiNO3 in distilled water. Comparative Example 1 was at a nitrate concentration of 0.1 m, Comparative Example 4 was at a nitrate concentration of 3 m, Example 1 was at a nitrate concentration of 6 m, Example 3 was at a nitrate concentration of 7 m, Example 4 was at a nitrate concentration of 8 m, and Example 2 was at a nitrate concentration of 9 m.
Comparative Examples 1 and 4 and Examples 1 to 4 at different nitrate concentration were subjected to TG/SC mode SCEM at a speed of 0.02 V/s to measure CVs. The CVs results were used to derive a ratio (iT,min/iT,max) of a minimum current at a tip electrode to a maximum current at the tip electrode, and the iT,min/iT,max ratios according to the nitrate concentrations are shown in FIG. 7.
For comparison, each electrolyte solution was prepared by dissolving 5 mM of HClO4 in distilled water and LiTFSI at different concentrations of 0.1 m, 3 m, 6 m, 7 m, 8 m, and 9 m and then, measured with respect to CVs, and iT,min/iT,max ratios according to the LiTFSI concentrations are shown in FIG. 7.
Referring to FIG. 7, the acidic LiTFSI electrolyte solutions exhibited no iT,min/iT,max difference according to the concentrations, but the acidic nitrate electrolyte solutions clearly exhibited iT,min/iT,max differences according to the concentrations based on the concentration of 6 m. In the case of the nitrate, the slope was β0.025 mβ1 until the concentration reached 6 m but sharply decreased slope to β0.11 mβ1 after the concentration reached 6 m. It was confirmed that within the range of the nitrate concentration of greater than or equal to about 6 m, reactivity of NO3β significantly increased.
Subsequently, electrochemical impedance spectroscopy (EIS) was performed to measure estimated charge transfer resistance (Rct) of Comparative Examples 1 and 4 and Examples 1 to 4, which was used to calculate a Rct difference (ΞRct) between where a potential of β0.8 V was applied for 9 minutes and where not applied, and then, ΞRct according to nitrate concentrations was shown in FIG. 8. For comparison, ΞRct according to LiTFSI concentrations was shown in FIG. 8.
Referring to FIG. 8, LiTFSI exhibited no ΞRct change according to the concentrations, but nitrate exhibited sharply increasing ΞRct from the concentration of greater than or equal to about 6 m.
Comparative Examples 1 and 4 and Examples 1 to 4 having different nitrate concentrations were subjected to potentiostatic bulk electrolysis in the aforementioned method to calculate each faradaic efficiency of NO2β and NH3, nitrate reduction products, and the results are shown in FIG. 9.
The faradaic efficiency was calculated according to Equations 1 and 2.
FENO2-=2FVCNO2-/Qtotββ[Equation 1]
FENH3=8FVCNH3/Qtot[Equation 2]
In Equations 1 and 2, FENO2- is faradaic efficiency of NO2β, FENH3 is faradaic efficiency of NH3, F is a faraday constant, V is an electrolyte solution volume, CNO2- is a concentration of NO2β in an electrolyte solution after electrolysis, CNH3 is a concentration of NH3 in the electrolyte solution after the electrolysis, and Qtot is a total charge of the electrolysis.
Referring to FIG. 9, when nitrate was at a concentration of 0.1 m, less than 2% of charges were involved in the nitrate reduction reaction, which confirmed that the hydrogen evolution reaction was dominant. Even if the nitrate concentration was increased to 3 m, total faradaic efficiency only increased to 8% or so. On the other hand, when the nitrate concentration was greater than or equal to about 6 m, total faradaic efficiency sharply increased even to 64% at the nitrate concentration of 9 m.
Referring to the SCEM, EIS analysis, and UV-vis absorption spectroscopy titration results as functions of nitrate concentrations, the nitrate concentration of greater than or equal to about 6 m had a critical significance in the acidic nitrate electrolyte solutions. It was understood that solvation structural changes in the acidic electrolyte solution activated the nitrate reduction reaction but suppressed the hydrogen evolution reaction.
NaNO3 instead of LiNO3 was used at various concentrations of 0.1 m, 3 m, 6 m, and 9 m to prepare electrolyte solutions, which were subjected to SECM CVs, EIS, and UV-vis appropriate analysis in the same methods as above. Among them, ΞRct changes according to the NaNO3 concentrations are shown in FIG. 10. In the overall analysis including FIG. 10, NaNO3, like LiNO3, exhibited that the nitrate reduction reaction was rapidly activated at the concentration of greater than or equal to about 6 m, but the hydrogen evolution reaction was suppressed. In the case of KNO3, which had solubility of about 4 in water at 25Β° C., it was difficult to directly compare.
Hereinafter, in order to determine a solvation structure that enables the nitrate reduction reaction at the concentration of greater than or equal to about 6 m, a water network was analyzed through hydrogen bonding in the electrolyte solutions.
Electrolyte solutions were prepared by dissolving 5 mM of HClO4 in distilled water and also, LiTFSI at each concentration of 0.1 m, 3 m, 6 m, 7 m, 8 m, and 9 m and then, subjected to infrared (IR) spectroscopy to analyze an OH stretching mode of H2O. In the IR spectra, peaks appeared at 3300 cmβ1, 3471 cmβ1, and 3593 cmβ1, which corresponded to network water, intermediate water, and multimer water in order. In the network water, H2O had a coordination number of less than or equal to 4, but as the network water changed into the multimer water, a hydrogen bond between water molecules became significantly weaker. The three peaks were separated to calculate a ratio of each peak to a total area of the three peaks, and each peak area ratio according to the LiTFSI concentrations is shown in FIG. 11.
Referring to FIG. 11, H2O largely existed as the network water at 0.1 m, which means that water molecules smoothly interact through the hydrogen bond. On the other hand, at 9 m, as the peak area ratio of the network water significantly decreased, but the ratio of the multimer water increased. Accordingly, the 9 m LiTFSI acidic electrolyte solution, in which the hydrogen bond between water molecules were significantly disrupted, was confirmed to be converted from conventional salt-in-water electrolyte (SIWE) to water-in-salt electrolyte (WISE).
Subsequently, other electrolyte solutions prepared by dissolving 5 mM of HNO3 in distilled water and also, LiNO3 at different concentrations of 0.1 m, 3 m, 6 m, 7 m, 8 m, and 9 m were prepared and then, subjected to IR spectroscopy analysis. In their IR spectra, peaks of network water (3300 cmβ1), intermediate water (3471 cmβ1), and multimer water (3593 cmβ1) were separated to calculate a ratio of each peak area to a total area of the three peaks, which is shown as a peak area ratio according to the nitrate concentrations in FIG. 12.
Referring to FIG. 12, unlike FIG. 11, as the nitrate concentration was increased, the ratio of the network water was slightly decreased, while the intermediate water was slightly decreased, but the multimer water exhibited a low ratio at all the concentrations. This shows that even when the nitrate concentration was increased to 9 m in the acidic aqueous solution, the hydrogen bond between the water molecules was not weakened, which means that WISE was not formed.
Hereinafter, formation of hydronium-in-salt electrolyte (HISE) is explained through molecule dynamic simulation.
Electrolyte solutions were prepared by dissolving 5 mM of HNO3 in distilled water and also, LiNO3 at different concentrations of 0.1 m, 3 m, 6 m, 7 m, 8 m, and 9 m to analyze a radial distribution function (RDFs) between Li+ and other types (H2O, NO3β, Li+, and H3O+). FIG. 13 is a graph showing RDFs of Li+ and H2O according to the nitrate concentrations, and FIG. 14 is a graph showing RDFs of Li+ and H3O+ according to the nitrate concentrations.
Referring to FIG. 13, even when the nitrate concentration was increased, H2O with a distance of less than about 2 β« with Lit exhibited almost no change in density, which indicates that H2O and Lit had weak the interactions even at the high concentrations. Referring to FIG. 14, the higher density of H3O+ with a distance of about 4 β« or less or about 6 β« with Lit, the higher nitrate concentration. The higher nitrate concentration, the higher density of H3O+, which was understood that H3O+ had more interactions with Lit as well as NO3β.
FIG. 15 is a molecule dynamic snapshot showing the solvation structure of the 9 m LiNO3 acidic electrolyte solution. In FIG. 15, each type represents H2O (red), NO3β (yellow), Li+ (pink), and H3O+ (green). Referring to FIG. 15, the lower density of H2O, the higher density of NO3β increased in a solvation shell of H3O+, and also, Li+ appeared. Accordingly, in the acidic high-concentration nitrate electrolyte, H3O+ was solvated by Li+NO3β to form HISE.
FIG. 16 is a graph showing a coordination number of H3O+ to Lit according to the nitrate concentrations. Referring to FIG. 16, the coordination number sharply increased, as the concentration was increased from 0.1 m to 6 m, but then, stopped increasing at the 6 m. This result indicates that as the nitrate concentration was increased, the solvation structure changed from SIWE to HISE, and the change was almost completed at about 6 m. This is consistent with the experimental results described above, which shows that the concentration of greater than or equal to about 6 m has a critical significance in the nitrate reduction reaction.
Hereinafter, mechanism of the nitrate reduction reaction in HISE is explained.
FIG. 17 is a schematic view showing an electrical double layer where nitrate reduction may occur competitively with H+ on the Pt electrode surface in HISE of acidic LiNO3. In HISE, ions are not individually hydrated but form a complex solvation structure. Within the ion cluster of HISE, a distance between H3O+ and NO3β is reduced, lowering an activation barrier of proton-coupled electron transfers (PCETs) from H3O+ to NO3β, which may result in generating reactivity intermediates. This is distinct from SIWE, where H3O+ and NO3β are completely separated by a thick hydration shell. The ion cluster of HISE may access to IHP due to the overall charge cancellation by the cation-anion bond structure. In other words, the ion cluster composed of [Li++H3O++NO3β] may be adsorbed on IHP, and the nitrate reduction reaction may occur through PCET.
In order to check a difference in the nitrate reduction reaction depending on the presence or absence of acidity, each electrolyte solution was prepared by adding or not adding 5 mM of HNO3 to a 9 m LiNO3 aqueous solution. These two electrolyte solutions were subjected to cyclic voltammetry analysis to β1.2 V at a scan rate of 1 V/s in SECM TG/SC mode. FIG. 18 is a graph showing collection efficiency (Neffβ², iS/iT) according to a tip electrode potential (ET) when HNO3 was added. FIG. 19 is a graph showing Neff according to ET when HNO3 was not added. Referring to FIG. 19, Neff was about 80%, which was more than twice of that in FIG. 18, indicating that a hydrogen evolution reaction was dominant. This result indicates that when there is no H+ (e.g., H3O+ near a Pt electrode) in an electrolyte solution, even if the high nitrate concentration was high, the nitrate reduction reaction did not occur effectively because the hydrogen evolution reaction was not suppressed.
While this invention has been described in connection with what is presently considered to be practical example embodiments, it is to be understood that the invention is not limited to the disclosed embodiments. On the contrary, it is intended to cover various modifications and equivalent arrangements included within the spirit and scope of the appended claims.
1. An electrochemical nitrate reduction system, comprising
an electrolyte solution including an acidic aqueous solvent and a nitrate having a concentration of greater than or equal to about 6 m (molality), and
an electrode.
2. The electrochemical nitrate reduction system of claim 1, wherein a concentration of the nitrate in the electrolyte solution is 6 m to 9 m.
3. The electrochemical nitrate reduction system of claim 1, wherein the nitrate includes LiNO3, NaNO3, or a combination thereof.
4. The electrochemical nitrate reduction system of claim 1, wherein a concentration of H3O+ in the acidic aqueous solvent is 5 mM to 100 mM.
5. The electrochemical nitrate reduction system of claim 1, wherein the acidic aqueous solvent includes HNO3.
6. The electrochemical nitrate reduction system of claim 1, wherein the electrode includes Ag, Co, Cu, Fe, Ni, Pt, Ti, or a combination thereof.
7. The electrochemical nitrate reduction system of claim 6, wherein the electrode includes Pt.
8. The electrochemical nitrate reduction system of claim 1, wherein the electrolyte solution includes a hydronium-in-salt.
9. The electrochemical nitrate reduction system of claim 8, wherein the hydronium-in-salt includes H3O+-in-Li+NO3β or H3O+-in-Na+NO3β.
10. The electrochemical nitrate reduction system of claim 8, wherein the electrolyte solution does not include a water-in-salt.
11. The electrochemical nitrate reduction system of claim 1, wherein a hydrogen evolution reaction, which is a competitive reaction of the nitrate reduction reaction, is suppressed.
12. The electrochemical nitrate reduction system of claim 1, wherein
the nitrate reduction includes Chemical Equation 1 and/or Chemical Equation 2:
NO3β+2H++2eββNO2β+H2Oββ[Chemical Equation 1]
NO3β+9H++8eββNH3+3H2O.ββ[Chemical Equation 2]
13. The electrochemical nitrate reduction system of claim 1, wherein NO2β and/or NH3 are produced by the reduction reaction of nitrate.
14. A method of inducing electrochemical reduction of nitrate, comprising
preparing an electrochemical device, which includes an electrolyte solution including an acidic aqueous solvent and a nitrate having a concentration of greater than or equal to about 6 m, and an electrode, and
applying a potential to the electrode to suppress a hydrogen evolution reaction and induce reduction of the nitrate.
15. The method of claim 14, wherein
the potential is about β0.1 V to about β2.0 V relative to the point of zero charge (PZC).