Open Access Article
Haldrian Iriawan†
*a,
Jedidian Adjei†
bc,
Danae A. Chipoco Haro†
d,
Dayana Donneys Victoriac,
Asa G. Ashleye,
Andrew J. Medford
*f,
Marta C. Hatzell
*g,
Gerardine G. Botte
*bc and
Yang Shao-Horn
*aehi
aDepartment of Materials Science & Engineering, Massachusetts Institute of Technology, Cambridge, MA 02139, USA. E-mail: haldrian@mit.edu
bDepartment of Chemical Engineering, Texas Tech University, Lubbock, TX 79409, USA
cInstitute for Sustainability & Circular Economy, Texas Tech University, Lubbock, TX 79409, USA
dSchool of Materials Science and Engineering, Georgia Institute of Technology, Atlanta, GA 30332, USA
eResearch Laboratory of Electronics, Massachusetts Institute of Technology, Cambridge, MA 02139, USA
fSchool of Chemical & Biomolecular Engineering, Georgia Institute of Technology, Atlanta, GA 30332, USA
gGeorge W. Woodruff School of Mechanical Engineering, Georgia Institute of Technology, 770 Ferst Ave, Atlanta, GA 30309, USA
hDepartment of Mechanical Engineering, Massachusetts Institute of Technology, Cambridge, MA 02139, USA
iDepartment of Chemistry, Massachusetts Institute of Technology, Cambridge, MA, 02139, USA
First published on 7th May 2026
Electrochemical conversion of nitrogen-containing organics in sludge offers a route for ammonia recovery but is challenged by compositional complexity. Glycine, abundant in municipal wastewater and structurally simple, provides a model system to benchmark nitrogen and carbon product distributions and electrode stability. Here, we report a coordinated cross-institutional study to elucidate glycine electro-oxidation pathways to ammonia. In alkaline electrolyte, ammonia was produced preferentially under oxidative potentials (>1.60 VRHE), rather than reductive conditions (<−0.40 VRHE), with Ni exhibiting lower overpotentials than Au and Pt. At 2.00 VRHE, ammonia was the dominant nitrogen product (∼70%), but with moderate Faradaic efficiency (23.5 ± 2.5%), accompanied by NO2−/NO3− (∼24%), Ni dissolution (∼12%), and O2 evolution (∼40%), collectively closing the charge balance. Carbon analysis using HPLC, IC, and 13C NMR revealed a mix of glycolate, glyoxylate, formaldehyde, cyanide, and formate (∼20% carbon, 6% Faradaic efficiency), with the remainder as CO2, indicating concurrent C–N and C–C cleavage pathways. These data, combined with thermodynamic analysis, inform a unified reaction framework and reveal C–N cleavage as the rate-limiting step. Furthermore, the ammonia-dominated production and coupled Ni2+ dissolution are correlated across different amino acids, highlighting Ni-complexation as a possible underlying mechanism favoring ammonia production. This work establishes a product-resolved framework and assesses experimental parameters (stirring, cell geometry, potential pulsing) to improve reproducibility and advance mechanistic understanding of ammonia recovery from organic nitrogen electrolysis.
Broader contextElectrified nutrient recovery from municipal waste streams is emerging as a promising strategy to transform wastewater treatment infrastructure into distributed platforms for circular fertilizer production. However, the complex and variable composition of these waste streams presents major challenges for catalyst evaluation, mechanistic understanding, and reliable product quantification. Amino acids are the key building blocks of proteins and dominant nitrogen-containing components of waste sludge. Yet even for the simplest amino acids, such as glycine, fundamental knowledge of nitrogen and carbon product distributions, selectivity, and catalyst stability remains limited. In this work, we establish a reproducible experimental framework across laboratories to examine the electrolysis of glycine and other amino acids, and uncover unexpected ammonia formation as the dominant N product under strongly oxidative conditions, despite the strong thermodynamic driving force to form oxidized products. Comprehensive characterization of reaction byproducts and systematic experimental evaluation provide key mechanistic insights into C–N bond cleavage and hydrogenation steps governing ammonia formation, while highlighting the critical influence of reaction environment and operating parameters on catalyst stability and selectivity. These findings lay the foundation for scalable electrochemical strategies to recover ammonia from organic waste streams, advancing circular nitrogen management and electrified waste treatment. |
Electrochemical approaches offer an attractive route in which chemical transformations are driven directly by applied potential and powered by electricity, enabling flexible operational control and coupling to renewables.6,7 Compared to thermal routes for sludge conversion (e.g., pyrolysis/gasification), which typically operate at ∼300–1000 °C and demand centralized heat integration and solid-handling infrastructure,8,9 or plasma-assisted routes which rely on specialized reactors and high-energy excitation,10 electrolysis can operate near ambient conditions and allows modular, decentralized deployment at wastewater treatment facilities.11 Jafari and Botte demonstrate that the electrochemical treatment of waste-activated sludge can produce ammonia (NH3) alongside short-chain fatty acids using electrodes including Ni, Cu, and stainless steel at low potentials (∼1.35 V versus Hg/HgO) in alkaline media (0.2 M NaOH), or ∼2.2 V versus reversible hydrogen electrode, VRHE, assuming pH = 13.12 Notably, Ni electrodes are reported to yield 250 mg L−1 of ammonia after 2 h of pulsed electrolysis.12 Technoeconomic analyses of electrically-assisted sludge conversion using these experimental findings reveal electrolysis as a promising route for sludge valorization and nutrient recovery, with potential advantages in integration simplicity, distributed operation, and compatibility with intermittent electricity.6
A central challenge in valorizing wastewater-derived feedstocks is that sludge composition varies widely with source, thus complicating product distribution and electrode stability analyses. In sewage sludge, the total solids (TS) content is typically 2–9%, of which organic solids account for approximately 20–44%.13 Within this organic fraction, carbon constitutes roughly 20–40% of TS,13–16 while total nitrogen is present at 2.8–4.9%.13,14,16,17 Proteins represent a dominant component of the organic matter (40–60%),18 alongside polysaccharides, lipids, and fatty acids.19 At alkaline conditions, proteins can be depolymerized into their constituent amino acids, and analyses of waste-activated sludge have identified ∼18 amino acids with distinct compositional distributions (see Table 1).20 As the highest nitrogen-density fraction of sludge, proteins and their amino acid building blocks are therefore attractive targets for electrochemical upgrading strategies aimed at ammonia recovery. Of these, glycine is a practical model molecule for two reasons: it is one of the most abundant amino acids in municipal sludge and extracellular polymeric substances, and it is the simplest amino acid, containing only an amine and a carboxylate group with no side chains. This minimal chemical complexity makes glycine an ideal benchmark system for isolating how experimental variables influence key observables such as nitrogen and carbon product distributions, Faradaic efficiencies, and electrode stability.
| Amino acid | wt% of crude protein in sludge |
|---|---|
| Aspartic acid (Asp) | 8.3 |
| Glutamic acid (Glu) | 8.1 |
| Alanine (Ala) | 7.3 |
| Leucine (Leu) | 5.6 |
| Glycine (Gly) | 4.9 |
| Threonine (Thr) | 4.2 |
| Valine (Val) | 4.1 |
| Serine (Ser) | 3.4 |
| Lysine (Lys) | 3.3 |
| Proline (Pro) | 3.1 |
| Phenylalanine (Phe) | 3.1 |
| Arginine (Arg) | 2.9 |
| Isoleucine (Ile) | 2.7 |
| Tyrosine (Tyr) | 2.4 |
| Cystine (Cys) | 2.1 |
| Methionine (Met) | 1.45 |
| Tryptophan (Trp) | 0.8 |
| Histidine (His) | 0.6 |
Electrochemical glycine oxidation has been explored on a range of electrode materials, including Pt, Au and more recently Ni-based metals. The oxidation of glycine on Pt has been extensively investigated. For example, Marangoni et al. have studied glycine (at 0.45 M) on Pt at both pH 1 and 13 via cyclic voltammetry and constant potential measurements, whose findings lead to mechanisms involving glycine adsorption through the carboxyl group followed by CO2 evolution and methylamine to form ammonia and formaldehyde.21 The ammonia selectivity at pH 13 at 1.06 VSCE (i.e. ∼1.8 VRHE)21 was reported at ∼83%, although the number of electrons (ne−) in the calculation was not specified and the ammonia detection via the Kjeldahl method22 could be interfered with by organic N as well as NO2/3−.23 The proposed mechanism of glycine oxidation on Pt24 and Au25 is supported by in situ vibrational spectroscopy, revealing the glycine adsorption by the COO− down configuration and reaction intermediates such as CN− and CNO−, alongside the detected reaction products such as CO2 and NH3. However, the quantification of ammonia efficiency and product distribution is not reported. More recently, Ni-based electrodes that can convert surface Ni(OH)2 (Ni(II)) to NiOOH (Ni(III)) upon oxidation and effectively oxidize urea26,27 and alcohols,28 are reported for glycine oxidation, including doped Ni(OH)2 catalysts such as Ni0.77Co0.20Cd0.03(OH)29 and Ni1.5Mn1.5O.29 Furthermore, amino acid conversion to ammonia, including glycine, was reported to have enhanced charge efficiency by potential pulsing on Au and Ni,30 an established strategy in enhancing the turnover of the desired products as demonstrated in CO2 reduction to C2+ products,31 NO3− reduction to NH4+,32 and urea oxidation.27 Despite these reports, systematic analyses of reaction products generated during glycine oxidation on metals, of electrode stability in the presence of glycine and N-containing ligands, and of the impact of experimental conditions on the measured Faradaic efficiencies, are lacking.
In this work, we have performed a coordinated cross-institutional study to investigate experimental details of electrochemical glycine conversion to ammonia. Three independent labs at different institutions have executed a nominally identical protocol spanning cell/component cleaning, electrode treatment, reference electrode calibration, electrochemical operation, and product quantification. With the shared benchmarking effort, using polished Ni foil in 0.1 M KOH + 0.1 M glycine, ammonia was detected under oxidative potentials (>1.60 VRHE). At 2.00 VRHE, ammonia dominates the solution-phase nitrogen products (∼70% of the N-product distribution) with ammonia Faradaic efficiency (FE) of 23.5 ± 2.2% across institutions, but this selectivity is accompanied by parasitic reactions including substantial Ni dissolution (>12%), formation of oxidized nitrogen products (NO2/3−, ∼24%), and O2 evolution (∼40%), cumulatively leading to complete charge balance. Comprehensive carbon analysis via high performance liquid chromatography (HPLC), ion chromatography (IC), and carbon nuclear magnetic resonance (13C-NMR) revealed multiple oxidation products such as glycolate, glyoxylate, formaldehyde, cyanide, formate, and CO2 in the form of carbonate (CO32−) indicating parallel pathways involving C
N and C–C scission in glycine activation. Furthermore, extending the study to alanine, lysine, and aspartic acid revealed that ammonia-dominated production was correlated with Ni2+ dissolution, highlighting Ni complexation as a possible origin of ammonia-dominated production. Critically, nitrogen selectivity, Ni corrosion rates, and carbon product distribution were found to depend on experimental conditions such as stirring rate, electrode area, cell architecture, and potential pulsing, demonstrating the strong influence of local reaction environment and underscoring the need for exhaustive reporting and community-facing best-practice protocols. Recommended experimental practices are discussed to improve reproducibility and accelerate the mechanistic understanding of electrochemical amino acid conversion towards scalable ammonia recovery from organic waste.
Electrochemical glycine oxidation experiments were conducted in a two-compartment H-cell, separated by an anion exchange membrane (DSVN, thickness = 95 µm, Bellex International Corp.) with both compartments containing 0.1 M as-received KOH (semiconductor grade, 99.99% trace metals basis, Sigma Aldrich) and 0.1 M glycine (≥99%, Sigma Aldrich). Hg/HgO or Ag/AgCl reference electrodes were employed, and a Pt mesh (99.99%, StonyLab) served as the counter electrode. Prior to glycine experiments, the Ni working electrode was electrochemically conditioned by cycling through the oxygen evolution region (1.10–1.70 VRHE) for 25 cycles in glycine-free electrolyte (0.1 M KOH). Then, electrolytes were replaced and the working electrode compartment was bubbled with Ar (99.999%, Airgas or Linde) for 20 min at 20 sccm before the start of electrolysis; the step-by-step protocol can be found in Note S1. The potentials reported against RHE follow eqn (1), where the electrolyte pH was consistently measured to be 10.7 via a pH meter. To maintain a consistent applied potential during the potential holds and to prevent overcompensation at high currents caused by auto compensation (an issue previously reported),33 the voltage was manually corrected for the IR drop. The solution resistance used for this correction was determined from the high-frequency real-axis intercept obtained by impedance spectroscopy measurements conducted after 15 minutes, 30 minutes, 1 hour, and 2 hours of electrolysis. The applied electrochemical potentials were converted to the reversible hydrogen electrode scale (VRHE) using the following equation:
| VRHE = Vmeas + Vref + 0.059 × pH − IR | (1) |
All three institutions employed anion chromatography with a conductivity detector to measure nitrate (NO3−) and nitrite (NO2−), where the specific instrument column configurations can be found in the SI and each independently yielded linear calibration curves against NO3− and NO2− standards of known concentrations (Fig. S8 and S9). At institution 1, 250 µL samples were diluted by a factor of 2 with deionized water and measured at 0.25 mL min−1 of sodium carbonate and bicarbonate eluent. At institution 2, samples were diluted 100 times with deionized water and measured at 0.15 mL min−1 of the same eluent. At institution 3, 25 µL of standard solution was injected into the eluent stream. The flow rate was maintained at 1.0 mL min−1 under a linear gradient elution from 20 mM to 40 mM KOH.
Ni dissolution was measured via inductively-coupled plasma-mass spectrometry (ICP-MS, institution 1) and ICP-OES (institutions 2 and 3), for which linear calibration curves as a function of Ni2+ concentration (ICP standard) were achieved (Fig. S10) and independently generated for each ICP measurement. Samples were diluted with a factor of 5–500 in 2% HNO3 (ICP grade).
Gas quantification was performed by connecting the H-cell to a SpectroInlet electrochemistry mass spectrometer (EC-MS) Professional, which was equipped with a quadrupole mass spectrometer (QMG 250, Pfeiffer). A Spectro Inlet aqueous chip enabled gaseous products to enter the mass spectrometer; all other openings were sealed except the connection to the H-cell (Fig. S11). During operation, Ar was continuously flowed through the system at 30 mL min−1. Prior to measurements, signals were recorded for 10 min to establish a stable baseline, after which the electrochemical program was initiated. For quantification, an O2 calibration curve was constructed by performing oxygen evolution on Ni foil in 0.1 M KOH. Constant current steps (30, 20, 10, 5, and 2.5 mA) were applied, with open-circuit intervals between each step to allow signal to decay back to the baseline level. The mass spectrometry signal at m/z = 32 was then correlated with the expected O2 production (assuming 100% Faradaic efficiency with ze− = 4, see Table 2) to generate calibration curves for both O2 production rate (µmol s−1) and total O2 evolved (µmol), exhibiting excellent linearity (see Fig. S12). This calibration was subsequently used to convert OER signals obtained during amino acid oxidation.
| Compound | z | Equations |
|---|---|---|
| a Since glycolic acid/glycolate is a 2-electron reduction from glyoxylic acid/glyoxylate, ne− = 2 for the glycine-to-glyoxylate conversion has been used in the faradaic efficiency calculation of glycolate. | ||
| Ni | 2 | Ni(s) → Ni2+ + 2e− |
| NH3 | 6 | NH2CH2COOH + 2H2O → NH3 + 2CO2 + 6H+ + 6e− (acid) |
| NH2CH2COO− + 5OH− → NH3 + 2CO2 + 3H2O + 6e− (alkaline) | ||
| NO2− | 12 | NH2CH2COOH + 4H2O → NO2− + 2CO2 + 13H+ + 12e− |
| NH2CH2COO− + 12OH− → NO2− + 2CO2 + 8H2O + 12e− | ||
| NO3− | 14 | NH2CH2COOH + 5H2O → NO3− + 2CO2 + 15H+ + 14e− |
| NH2CH2COO− + 14OH− → NO3− + 2CO2 + 9H2O + 14e− | ||
| O2 | 4 | 2H2O → O2 + 4H+ + 4e− |
| 4OH− → O2 + 2H2O + 4e− | ||
| CN− | 4 | NH2CH2COOH → CN− + CO2 + 5H+ + 4e− |
| NH2CH2COO− + 4OH− → CN− + CO2 + 4H2O + 4e− | ||
| Glyoxylic acid | 2 | NH2CH2COOH + H2O → OCH–COOH + NH3 + 2H+ + 2e− |
| NH2CH2COO− + 2OH− → OCH–COO− + NH3 + H2O + 2e− | ||
| Glycolic acid | 2a | OCHCOOH (glyoxylic acid) + 2H+ + 2e− → HOCH2COOH (glycolic acid) |
| (net) NH2CH2COOH + H2O → HOCH2COOH + NH3 | ||
| (net) NH2CH2COO− + H2O → HOCH2COO− + NH3 | ||
| Formic acid | 4 | NH2CH2COOH + 2H2O → HCOOH + CO2 + NH3 + 4H+ + 4e− |
| NH2CH2COO− + 4OH−→ HCOO− + CO2 + NH3 + 2H2O + 4e− | ||
Carbon products were independently detected at the three institutions to determine key reaction byproducts during glycine electrolysis. At institution 1, 13C-NMR was employed for which the glycine electrolysis was performed following the same electrochemical protocol but instead used 13C2 glycine (99 atom% 13C, Sigma) where the two carbons are labelled. 500 µL sample was mixed with 50 µL D2O and measured with 500.18 MHz Bruker AVANCE NEO spectrometer. Spectra were acquired using a zgdepq pulse sequence with broadband 1H decoupling. A total of 512 scans were accumulated with a relaxation delay of 1.0 s over a spectral width of 30 kHz (∼240 ppm), centered at 100 ppm. At institution 2, high-performance liquid chromatography was used with HPX-87H organic acid analysis column (AMINEX) paired with Biorad, equipped with a UV-vis detector positioned at 260 nm (2489 UV/Vis Detector, Waters). The eluent was 5 mM H2SO4, the column flow rate was 0.4 mL min−1 and the column temperature was 30 °C. At institution 3, anion chromatography was used to identify and quantify detected carbon products such as glycolate, formate, acetate, glyoxylate, and oxalate using gradient elution, where the temperature (30–50 °C), elution time, and KOH concentrations for linear gradient were optimized for each carbon product which resulted in linear calibration curves (Fig. S13). Full details of instrument configuration can be found in the SI. Cyanide quantification was done with the Pyridine barbituric acid method (see SI). Chemical Oxygen Demand (COD) was attempted but suffered from significant interference from glycine, glyoxylic acid and formic acid (see SI and Fig. S14).
![]() | (2) |
484 C mol−1), and Q is the amount of charge transferred during the reaction.
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| Fig. 1 Experimental benchmarking of electrochemical glycine oxidation on Ni. (a) H-cell setup for electrochemical glycine oxidation with Ni foil at 2.00 VRHE 0.1 M KOH + 0.1M glycine (Ar-sat). (b) cross-institution benchmarking of nitrogen products in the electrolyte, showing ammonia-dominated nitrogen product. Error bars indicate n ≥ 3 repeats (Fig. S21 and Table S1). It is noted that the benchmarking condition for institution 3 corresponds to no stirring condition, which is more similar to data from institution 1 and 2 using a small stir bar (10 mm at 300 rpm). More discussion can be found in relation to Fig. 4. (c) Time-dependent profile of ammonia (blue, measured via Ion chromatography or H-NMR) and Ni corrosion (gray, measured via ICP-MS) with respected to cumulative charge passed on Ni foil at 2.00 VRHE, showing significant electrode dissolution alongside ammonia generation. (d) Potential-dependent faradaic efficiency to ammonia, calculated assuming ze− = 6 from NH2CH2COOH + 2H2O(l) → NH3(g) + 2CO2(g) + 6(H+ + e−), see Table 2. The faradaic efficiency at 2.00 VRHE corresponds to the benchmarking condition over 2 h electrolysis, while the Faradaic efficiencies at other potentials were obtained from the potential screening experiment where 15 min chronoamperometry holds (CA) were conducted over time in the same electrolyte (see Fig. S5). The right panel shows cross-institution cumulative Faradaic efficiencies for the different products, assuming ze− = 14, 12, 2 and 4 for NH2CH2COOH/NO3−,CO2; NH2CH2COOH/NO2,CO2, Ni/Ni2+ and OH−/O2 respectively. Details of Faradaic efficiency calculation can be found in Table 2. Tabulated Faradaic efficiency values from the three institutions can be found in Table S1. | ||
Ammonia formation was found to increase linearly over the 2 h electrolysis at 2.00 VRHE as a function of charge passed (Fig. 1c). The assignment of ammonia as a glycine-derived product was further corroborated by isotope-labelling experiments using commercially available 15N-glycine, which showed a quantitative agreement in the ammonia production relative to experiments with unlabeled glycine (Fig. S23 and S24). However, alongside abundant 15NH3, a non-negligible fraction of 14NH3 was also detected, which suggests isotopic or nitrogen impurities in the commercial 15N-labeled glycine, highlighting the need for caution when employing 15N-labeled glycine in mechanistic studies of nitrogen-containing products.
The increase in ammonia was linearly accompanied by significant Ni2+ dissolution. The Ni2+ concentration in the electrolyte, quantified by ICP after 2 h of electrolysis, reached up to ∼120 µmol, which is substantially larger than the ∼25–30 µmol of ammonia produced, indicative of ∼2–5× more Ni dissolved than ammonia formed. While all three institutions encountered challenges in reliably quantifying dissolved Ni (Fig. S25 and S26), the Ni2+ values shown in Fig. 1c were quantified with confidence (see Note S3) and represented the upper bound across trials. Notably, the Ni dissolution without glycine was found to be negligible (<0.1 umol in 0.1 M KOH electrolyte at 2.00 VRHE over 2 hours, see Fig. S27). The glycine-promoted Ni dissolution can be attributed to the exothermic complexation of Ni(II) with glycinate (the deprotonated form of glycine), for which the aqueous complexation enthalpy at 25 °C has been reported as −36.7 kJ mol−1.39 Notably, the coupled ammonia production and Ni dissolution could point to a dissolution-mediated pathway for ammonia formation, wherein Ni-ammonia complexation lowers the thermodynamic and/or kinetic barrier of making ammonia. For example, the formation of Ni–NH3 complex (i.e. Ni2+ + 6NH3 → [Ni(NH3)6]2+) has an overall reaction enthalpy of −94.6 kJ mol−1 at 25 °C according to DFT computation,40 indicating strong stabilization of coordinated ammonia, which can stabilize NH3 in solution from further oxidation to NO2− or NO3− under the oxidative conditions used in this work. This is discussed further in the screening of other amino acids below. Further mechanistic studies are required to understand how glycine enhances Ni corrosion and whether soluble Ni species facilitate ammonia production under oxidative conditions. Interestingly, prior electrochemical studies on real waste activated sludge under pulsed electrolysis conditions (1.35 V vs. Hg/HgO, 0.2 M NaOH, 2 h) did not report significant Ni dissolution,12 suggesting that the complex matrix of real sludge comprising proteins, polysaccharides, lipids, and extracellular polymeric substances may provide passivation or competitive complexation that protects the Ni surface. The particularly strong complexation of Ni(II) with glycinate may be uniquely aggressive compared to the diverse ligand environment present in real sludge, with important implications for catalyst design: electrode alloys or surface modifications that reduce glycinate complexation may improve stability during amino acid electrolysis. Overall, the high anodic overpotential and Ni instability raise concerns regarding the practical viability of ammonia recovery from amino acids on Ni. Further assessment of electrode stability under continuous operation in more practical setups (e.g., flow cells), as well as understanding and mitigating surface passivation in real sludge, will be important directions for future work.
The ammonia Faradaic efficiency became larger when the working electrode potential was increased from 1.60 to 2.05 VRHE, and then decreased at higher potentials (Fig. 1d). The Faradaic efficiency of ammonia, calculated using eqn (2) with ze− = 6 assuming full oxidation of carbon to CO2 as an upper bound of efficiency (Table 2), increased from ∼10% to ∼38%, where the latter was operated at a higher potential than the 2.00 VRHE benchmarking condition, which corresponds to 2.05 VRHE after iR-correction. The logarithm of the ammonia formation rate was found to be proportional to the applied potential between 1.60 VRHE and 2.05 VRHE, with a Tafel slope of 277 ± 22 mV dec−1 (Fig. S5). This behavior suggests that ammonia formation is governed either by an electrochemical rate-determining step or by a chemical rate-determining step involving electrochemically-generated active sites. It is noted that the potential (≥1.60 VRHE) needed to produce ammonia (Fig. 1d and Fig. S5) is significantly more positive than the standard thermodynamic potential of glycine oxidation to make ammonia, NH2CH2COOH(s) + 2H2O(l) → 2CO2 + NH3 + 6H+ + 6e−, E0 = +0.06 VRHE (see Table S2 for details), indicative of slow kinetics for ammonia production. Nevertheless, Ni foil exhibited a considerably lower oxidative overpotential than Au and Pt, where ammonia production became apparent only at potentials >2.1 VRHE and >2.6 VRHE, respectively (Fig. S5), signifying the surface-dependence of glycine conversion to ammonia. For Ni, the decrease in ammonia FE upon further increase in the potential beyond 2.05 VRHE is not understood. We hypothesize that this may occur due to competing processes such as O2 evolution and Ni corrosion, and/or lower activity toward glycine oxidation on further oxidized Ni surfaces41 (e.g. NiO2). On the other hand, reduction at constant potentials such as −0.4 VRHE and below did not show any ammonia production (Fig. S28), suggesting the role of electrochemical oxidation (rather than reduction) in glycine activation, nitrogen liberation and ammonia formation. At the benchmarking condition (representative data shown in the right panel of Fig. 1d), the three institutions consistently reported an ammonia FE of 23.5 ± 2.2%, where the uncertainty was attributed to experimental factors such as variations in the iR-corrected potential across trials and electrode and electrolyte preparations (e.g. dilution errors). The Faradaic efficiency toward NO2−/NO3− collectively accounted for comparable percentages of ∼25%. A significant portion of charge (on average ∼10%) was associated with Ni corrosion while the remaining charge (∼40%) was attributed to O2 evolution, thereby closing the charge balance. Overall, these benchmarking efforts, which are focused on uncovering the Faradaic efficiency and distribution of N products and Ni dissolution, demonstrated consistent cross-institution alignment in capturing the experimental findings of glycine oxidation on Ni. Next, a more detailed understanding of glycine transformation was investigated through multi-technique carbon detection to enable the elucidation of possible reaction pathways during glycine oxidation.
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| Fig. 2 Characterization of carbon byproducts during electrochemical glycine oxidation on Ni at 2.00 VRHE. (a) HPLC of electrolyte solutions at increasing reaction time up to 2 h. Carbon product standards are shown in the lower panel. (b) Anion chromatography spectra of electrolyte solutions undergoing electrochemical glycine oxidation at increasing time stamps up to 2 h. The glycolate-acetate detection (right panel) has been specifically conducted at a higher column temperature to separate these peaks, which would otherwise overlap at room temperature (see SI). (c) 13C-NMR spectra of glycine electro-oxidation using 13C2 glycine, where products such as carbonate, cyanide, formaldehyde, glyoxylate and formic acid appeared after 2 h of electrolysis. The experimental condition corresponds to the benchmarking condition of Ni electrode at 2.00 VRHE as described in Fig. 1. | ||
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| Fig. 3 Reaction pathways during electrochemical glycine oxidation. (a) Proposed reaction pathways based on the detected reaction products, denoted in red as characterized in Fig. 2. Free energy diagrams of the pure phases with increasing oxidation state of the carbon are depicted for pathway 1 (b) and pathway 2 (c) based on the available thermodynamic data. All species and reactions are expressed in their protonated form and used the standard free energy of formation of the pure phases: crystalline solids for glycine, glyoxylic acid (i.e. in its hydrated form, dihydroxyacetic acid) and glycolic acid; liquids for acetic acid, formic acid, cyanic acid (HCN); gases for formaldehyde, methylamine, CO2, NH3 and H2. Formal oxidation states were assigned using the ionic approximation by attributing bonding electrons to the more electronegative atom, and the resulting charge defines the oxidation state. Zero free energy corresponds to CO2(g), NH3(g), H2(g) at 1 bar and 298 K. Full chemical equations and the reaction free energy calculations can be found in Table S3. | ||
Alternatively, the existence of C2 products that do not contain nitrogen, such as glyoxylate (OCH–COO−) and glycolate (HOCH2COO−) suggests that direct C–N bond cleavage to liberate ammonia occurs on Ni, as depicted in pathway 2 (Fig. 3, bottom). In this route, glycine is oxidized directly to glyoxylate (OCH-COO−) and ammonia according to NH2CH2COO− + 2OH− → OCH–COO− + NH3 + H2O + 2e− and the carbon in glyoxylate is further oxidized to formate and ultimately CO2. Interestingly, glycolate likely comes from two-electron reduction of glyoxylate, which is commonly observed in biological systems through glyoxylic acid reductase (GAR).48 Thus, its presence at 2.00 VRHE may imply a coupled oxidation–reduction process occurring on Ni, which warrants further investigation. Overall, glycine activation via either C–C cleavage (pathway 1) or C–N cleavage (pathway 2) appears to be feasible during electrochemical oxidation on Ni, but the extent of the two pathways requires consideration of the reaction energetics.
We further discuss the feasibility of different mechanisms by examining the thermodynamic stability of the reaction intermediates using the gas or solution phase free energies (Fig. 3b and c). We note that the bulk thermodynamic values do not include surface adsorption or electric field effects prominent in electrochemical reactions on a heterogeneous surface, but can provide a starting point in understanding the relative stability of reaction intermediates. Such thermodynamic analysis indicates that both pathways involve a similarly uphill step, and that C–N bond cleavage is generally the most energetically uphill step. Using standard Gibbs formation energies for carbon-containing species (Table S3), the energy diagram for pathway 1 (Fig. 3b) shows that the conversion of methylamine to formaldehyde and ammonia, CH3NH2(g) + 2OH− → CH2O(g) + NH3(g) + 2e− + H2O(l) is the most uphill step, with ΔGr = +133.0 kJ mol−1. The subsequent oxidation of formaldehyde to formic acid and CO2 is energetically downhill. When cyanide is considered as an intermediate, its formation from methylamine CH3NH2(g) + 5OH− → HCN(l) + 2e− + H2O(l) is the most uphill step (ΔGr = 140.5 kJ mol−1), while further oxidation to NH3 and CO2 is thermodynamically favorable. The experimental observation of CN− as a prominent byproduct is at odds with the thermodynamic analysis, indicating that kinetic barriers on the surface or other surface thermodynamic reaction steps should be considered. For pathway 2 (Fig. 3c) involving sequential oxidation of glycine to glyoxylic acid, formic acid, and CO2, glycine oxidation to glycolic acid via NH2CH2COOH(s) + 2H2O(l) → CH(OH)2COOH + NH3 + 2H+ + 2e−, ΔGr = +150.4 kJ mol−1, is the most uphill step. The subsequent oxidation steps of carbon from glyoxylic acid to ultimately CO2 appears to be strongly downhill. This analysis supports C–N bond cleavage as the rate-determining step. However, capturing the true rate-limiting steps and reaction selectivity will require a detailed investigation of charged species adsorption (e.g., glycinate/carboxylate species and CN−). This will involve grand-canonical density functional theory and microkinetic modeling, supported by experimental probes such as kinetic isotope effects and Tafel slope analysis, and is the subject of future work.
We consider several hypotheses regarding the origin of the oxidizing species responsible for glycine oxidation on the Ni surface. One possibility is oxidation mediated by NiOOH formed through the Ni2+/Ni3+ redox transition,49,50 described by Ni(OH)2(s) + OH−(aq) → NiOOH(s) + H2O(l) + e−. NiOOH can therefore act as a primary oxidant, which has been demonstrated for the electrochemical oxidation of urea27,37 and alcohols.28 This hypothesis is supported by the fact that glycine oxidation to ammonia occurs at potentials >1.60 VRHE (Fig. 1d), which are well above the Ni2+/Ni3+ redox transition at ∼1.35 VRHE.51 Alternatively, the formation of surface NiOx species may enable the generation of reactive oxygen species such as peroxide and superoxide species, with prior studies indicating that hydroperoxides52 and OH˙ radical,53 such as those generated via Fenton chemistry, can oxidize amino acids. Another possibility involves singlet oxygen (1O2), a highly reactive oxidant that can arise from spin-conservation constraints during oxygen evolution and then decay to triplet oxygen (3O2). The generation of 1O2 has been reported on Ni-based cathodes,54 where it induces severe oxidative decomposition of aprotic solvents to generate carbon-byproducts such as Li–acetate, Li–formate and Li2CO3 that severely limit the cyclability of Li-ion and Li–O2 batteries,54 and is thermodynamically accessible with a calculated reversible potential of 1.475 VRHE for 2H2O → 1O2 + 4H+ + 4e−.55 Interestingly, these aprotic byproducts are structurally similar to glycinate (structurally equivalent to acetate but with an -NH2 group substituted onto the methyl carbon), formate and CO32− detected in this work (Fig. 2), hinting at 1O2 as a possible oxidant assuming similar reactivity in protic environments. Further mechanistic studies are therefore required to identify the dominant oxidizing species responsible for glycine activation, which will inform future catalyst design aimed at decoupling oxidant generation from electrode corrosion.
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| Fig. 4 Effect of experimental design on the nitrogen and carbon products of electrochemical glycine oxidation on Ni. The benchmarking condition (most left) corresponds to conditions described in Fig. 1, using an H-cell containing an anion-exchange membrane and micro stir bar (10 mm) rotated at 300 rpm. The faradaic efficiencies from experiment 3–1 from institution 3 has been plotted (see Table S1) as the carbon product quantification is available for this experiment. Relative to the benchmarking condition, three changes of experimental conditions have been investigated: larger convection via higher rotation of a larger stir bar, larger electrode area and undivided compartment (i.e. single cell) in lieu of H-cell, showing significant influence of these factors on the production and distribution of the N- (top panel) and C-based (bottom panel) products. The faradaic efficiency calculation for NH4+, NO3−, NO2− and CN− and for glycolate, glyoxylate and formic acid can be found in Experimental section. | ||
The effect of electrode surface area was investigated by doubling the electrode area while keeping the same electrolyte volumes in both compartments (i.e. 0.05 to 0.1 cmgeo2: mL ratio), with no stirring. Increasing the electrode area led to a substantial enhancement in ammonia Faradaic efficiency, from ∼26% to ∼40% (Fig. 4, top). In contrast, the faradaic efficiency toward NO3− decreased markedly from 31.5% to 11.2% with the larger electrode. The carbon product distribution also exhibited discernible changes, with glycolate Faradaic efficiency increasing to 2.7% for the larger electrode compared to 0.5% at benchmarking (Fig. 4, bottom). Taken together, these results indicate that a larger electrode area favors ammonia production, potentially by enabling a greater extent of coupled oxidation–reduction processes at the electrode surface when the oxidative potential 2.00 VRHE was applied. In this context, both methylamine formation from glycine and glycolate formation from glyoxylate involve reductive steps (Fig. 3a), which may benefit from increased electrode area. These findings also suggest that reactor design and optimization of mass transport is critical in controlling the activity and selectivity of practical amino acid electrolysis. Finally, the influence of cell design was evaluated by comparing the H-cell configuration (i.e. the benchmarking condition) with a single-compartment/undivided cell, while keeping the electrode area-to-volume ratio (i.e. 0.05 cmgeo2: mL) the same without stirring. The undivided cell produced an overall Faradaic efficiency for nitrogen-containing products (NH3, NO3−, NO2−, and CN−) of 66.1%, comparable to the benchmark H-cell value of 63.2%, but with a larger fraction of NO3− relative to NH3 (Fig. 4, top). In addition, glycolate Faradaic efficiency increased to 3.3% from 0.5% in benchmarking condition (Fig. 4, bottom). This shift in selectivity may be linked to the pH drop during electrolysis: during the benchmarking H-cell conditions with an anion-exchange membrane, the working electrode compartment experienced a larger pH drop (ΔpH ≈ −0.5) compared to the undivided cell (ΔpH ≈ −0.2, see Fig. S34 and Table S4). These observations suggest that electrolyte pH may influence glycine oxidation pathways and the resulting ammonia and carbon product selectivity, warranting further investigation.
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| Fig. 5 Investigating the impact of potential pulsing on NH3 efficiency. (a) Chronoamperometry profile of electrochemical glycine oxidation with polished Ni at 2.00 VRHE 0.1 M KOH + 0.1 M glycine (Ar-sat) over 1 hour, corresponding to the ‘benchmarking condition’ outlined in Fig. 1. (b)–(d) Electrochemistry profile of three pulsing conditions at increasing values of the positive potentials from +1.65 VRHE (pulsing 1, b), 1.78 VRHE (pulsing 2, c) and 1.83 VRHE (pulsing 3, d), while the negative potential values are kept nominally similar but showed differences in currents resulting in differences in iR-corrected potentials. Zoomed-in view of the current profiles are shown in panels e, f and g for pulsing 1, 2 and 3 respectively, where the positive and negative potentials were held for 5 s. The average and standard deviation of the potentials are determined from the last 1 s of the 5 s pulse (see Fig. S38–S40 for demonstration), during which the current is stable, over the entire 1 h duration and across 3 independent repeats. (h) NH3 faradaic efficiency comparison between the constant potential experiments at 2.00 VRHE and the pulsing experiments with three different methods of charge accounting: the sum of positive and negative charges (left), the positive charges only (middle) and the absolute values of the positive and negative charges. The faradaic efficiency to ammonia, calculated assuming ze− = 6 from NH2CH2COOH + 2H2O(l) → NH3(g) + 2CO2(g) + 6(H+ + e−), see Table 2. Error bars indicate n ≥ 3 independent measurements (see Tables S5 and S6 for the tabulated results). | ||
Ammonia Faradaic efficiency (FE) with pulsing generally shows a significant improvement relative to constant-potential electrolysis, yet the magnitude of this enhancement is highly sensitive to how the Faradaic charge is accounted for (Fig. 5h). The constant-potential experiment yielded an ammonia FE of 18.4 ± 0.9% over 1 h across three independent repeats. Notably, the same experiments produced an FE of 23.8 ± 1.0% over 2 h (Table S1), consistent with cross-institution benchmarking results (Fig. 1), indicating higher efficiency at longer electrolysis times. In calculating the FE from pulsing experiments, three accounting methods were used to determine the total Faradaic charge (Qtotal): (i) summing positive and negative charges with their signs preserved (Fig. 5h, left), (ii) considering only the positive charge (Fig. 5h, middle), and (iii) summing the absolute values of positive and negative charges (Fig. 5h, right). When method (i) is considered, serving as the most ‘optimistic’ estimate of the Faradaic efficiency, pulsing 1 and 2 yield substantially higher ammonia FEs of up to ∼80%. In contrast, when negative charge contributions are excluded or counted in absolute terms (methods ii and iii), the calculated FEs decrease markedly and converge toward those obtained under constant-potential conditions. The sensitivity of FE to charge accounting is most pronounced for pulsing 1 (Fig. 5b and e), where the total positive charge passed is the lowest in magnitude and at levels comparable to the negative charge (Table S5). In addition, the FE from pulsing experiments exhibit generally larger error bars, which we attribute to the greater variation of the working electrode potential associated with iR-correction. Despite these variations, the enhancement in FE relative to constant-potential electrolysis remains robust beyond experimental uncertainty. In particular, pulsing 2, which employs a lower positive potential of 1.78 VRHE ± 17 mV, delivers at least ∼10% higher ammonia FE (∼30% as the lower bound) than the static experiments at 2.00 VRHE (Fig. 5h, right) regardless of the accounting methods used.
The enhancement in ammonia FE via pulsing suggests several mechanistic implications. The effectiveness of pulsing to the *H coverage regime (<−0.1 VRHE on Ni56) implies that the rate-limiting step of C–N bond cleavage, which we hypothesized in accordance with the thermodynamic analyses in Fig. 3, is linked to the hydrogenation of the amine group to form ammonia. At oxidative potentials, hydrogen availability is limited because water preferentially undergoes oxidation to O2 and H+ above 1.23 VRHE. Pulsing to negative potentials may therefore transiently increase *H coverage, facilitating amine hydrogenation and C–N bond cleavage. Alternatively, the benefit of pulsing may arise from active-site regeneration. In this case, cycling the potential enables repeated Ni2+/Ni3+ redox transitions, regenerating NiOOH as the active oxidizing species and sustaining the conversion. The sensitivity of pulsing results highlights the need for clear charge accounting and further mechanistic investigation to elucidate the contributions of positive and negative charge toward ammonia production. Nevertheless, these results highlight opportunities to optimize pulsing conditions to enhance ammonia efficiency while reducing anodic overpotential, which should ultimately align with the practical energy efficiency targets defined by future technoeconomic analyses.
We correlate ammonia production with competing processes and side-chain character to probe the mechanism of ammonia generation during amino acid oxidation. In lieu of FE, the product converted in moles normalized to the total charge passed (in units of mol of products per coulomb of passed charge, µmolprod C−1), denoted as the charge efficiency to the product, has been used to avoid ambiguity in the number of electrons ze−. Firstly, increasing charge efficiency toward ammonia was linearly correlated with decreasing charge efficiency to O2 (Fig. 6b), indicating that O2 is parasitic to ammonia production. Mechanistically, this correlation supports the hypothesis that both processes share a common active site. In this context, NiOOH associated with the Ni2+/Ni3+ transition is known to be key for O2 evolution activity51,57 but may also competitively act as the primary oxidant for amino acid conversion to ammonia. Secondly, the charge efficiency to ammonia correlated approximately logarithmically with increased Ni dissolution (Fig. 6c). This observation supports the hypothesis that dissolved Ni plays an active role in thermodynamically stabilizing ammonia, such as via the Ni–NH3 complex. Another hypothesis consistent with this observation is that Ni2+ may kinetically accelerate amino acid decomposition via redox mediation: initial Ni2+-amino acid complexation followed by oxidation to Ni3+ by the electrode generates a solution-phase oxidant that promotes oxidative deamination, releasing ammonia.58,59 We further examine the relationship between Ni2+ dissolution and side-chain character. Previous computation60 has shown that aspartic acid binds Ni2+ much more strongly (Ebinding = ∼350 kJ mol−1) than other amino acids (Ebinding = ∼250 kJ mol−1 for glycine, alanine and lysine) due to its two negatively charged carboxyl groups. However, the Ni2+ dissolution in aspartic acid (0.003 µmolNi C−1) is the lowest among the amino acids studied. This result suggests that the Ni electrode instability in the presence of amino acids stems not from the parasitic Ni2+-amino acid coordination, but instead actively facilitates ammonia formation via nickel complexation, which improves the thermodynamic stability of ammonia and reaction intermediates and concurrently lowers kinetic barriers. Thirdly, increasing charge efficiency to ammonia is associated with increasing NO2/3− (Fig. 6d). This result supports the hypothesis that NH3 and NO2/3− production are bottlenecked by a common rate-limiting step of C–N cleavage (see Fig. 4b and c). Based on these correlations, we hypothesize that the electrochemical activity for amino acid activation can be rationalized by the side-chain character (see top of Fig. 6). (i) Glycine and alanine, with simple side groups, exhibit higher NH3 and NOx efficiencies, likely due to higher surface coverage of amino acid adsorption. (ii) Lysine shows moderate efficiencies, where the longer side chain may reduce adsorption coverage despite the additional amine. (iii) Aspartic acid exhibits the lowest efficiencies, due to alternative COO−-down adsorption25 on the positively charged Ni surface from the carboxylate side-group rather than the α-functional group. While further work is needed to quantitatively link charge efficiency with broader amino acid structures, these results provide insight into the origin of ammonia production and its dissolution-mediated mechanism under oxidative potentials.
For product quantification, we caution against the use of colorimetric methods for ammonia, nitrate/nitrite, and carbon product detection, as these techniques were shown to suffer from interferences arising from amino acids, metal ions, and reaction byproducts (see the Experimental section). In contrast, 1H NMR spectroscopy and ion chromatography were found to be reliable when implemented with consistent sample preparation protocols, including immediate electrolyte acidification and appropriate storage. Furthermore, while 15N isotope labeling can provide valuable mechanistic insights, careful interpretation is required due to the presence of 14N-nitrogen impurities observed in this work (Fig. S24). Finally, we recommend comprehensive reporting of scientifically relevant metrics, such as product distributions, Faradaic efficiencies toward nitrogen- and carbon-containing products, and electrode dissolution, together with the corresponding experimental conditions. Particular attention is given to the reporting of pulsing experiments, as the methodology used to account for Faradaic charge such as how capacitive currents are excluded and how anodic and cathodic charges are treated in efficiency calculations can significantly influence quantitative comparisons (Fig. 5) and should therefore be explicitly reported. Such standardized reporting is essential to enable meaningful cross-laboratory comparisons and will be critical for advancing our understanding of electrochemical ammonia recovery from amino acids and organic waste.
Finally, we discuss potential strategies to improve ammonia efficiency and electrode stability based on the trends identified in this work. First, we show that potential pulsing is effective in enhancing ammonia efficiency (Fig. 5). Future efforts can focus on optimizing pulse parameters (potential, duration, and frequency), which have been shown in other systems (e.g., CO2 reduction30,31 and urea oxidation12,27) to improve selectivity and activity. Second, the observed coupling between ammonia production and Ni dissolution (Fig. 1 and 6) also highlights a fundamental bottleneck. One potential strategy is to decouple amino acid activation (i.e., C–N cleavage) from ammonia stabilization. This may be achieved by leveraging molecular oxidants (e.g., OH−, H2O2)52,53 to enable amino acid activation at lower potentials, as well as through electrolyte engineering with ionic additives that enhance solution-phase ammonia stability while maintaining environmental compatibility. More urgently, a systematic assessment of Ni stability in real wastewater systems is needed, coupled with chemically resolved characterization of organic nitrogen beyond bulk metrics (e.g., total nitrogen). Notably, prior studies using complex sludge matrices have not reported significant Ni dissolution,12 suggesting additional matrix effects and/or a surface passivation mechanism that warrants further investigation and may present opportunities for catalyst engineering.
Footnote |
| † Equally contributing authors. |
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