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Magnetic-field-assisted cascade electrocatalysis: simultaneous H2O2 generation and ˙OH radical production for coupled hydrogen evolution and water disinfection

Yeonsu Han a, Jungsue Choia, Soyun Oha, Hyun Kob and Hyoyoung Lee*abc
aDepartment of Chemistry, Sungkyunkwan University (SKKU), Suwon, Republic of Korea. E-mail: hyoyoung@skku.edu
bInstitute for Quantum Biophysics (IQB), Sungkyunkwan University (SKKU), Suwon, Republic of Korea
cNational Institute of Climate and Environment (NICE), Sungkyunkwan University, Suwon, Republic of Korea

Received 27th March 2026 , Accepted 8th May 2026

First published on 8th May 2026


Abstract

Current research on green hydrogen mainly focuses on water electrolysis. However, the low commercial utility of oxygen hinders the reduction of hydrogen production costs. Herein, we report a bifunctional Mn-SnO2@Fe3O4 catalyst for simultaneous hydrogen production and water disinfection. Under an external magnetic field, the system triggers a cascade reaction, converting in situ generated H2O2 into ˙OH radicals via a Fenton-like reaction. This synergy achieved 99.9% antibacterial efficacy against Escherichia coli at 2.6 V vs. RHE.


1 Introduction

Driven by global environmental regulations, interest in carbon-free technologies has continuously intensified, with a particular focus on the sustainable production of hydrogen.1,2 As a primary feedstock for various chemical syntheses and a high-density energy carrier, hydrogen plays a pivotal role in energy storage systems. Currently, most of the industrial hydrogen is supplied as a by-product from petrochemical processes. However, this route is associated with substantial carbon dioxide emissions. To address this, water electrolysis has emerged as a promising eco-friendly alternative, utilizing renewable electricity to split water.3,4

The primary bottleneck in conventional water electrolysis is the sluggish oxygen evolution reaction (OER) at the anode.5 The OER is hindered by high overpotentials and the indispensable use of expensive noble metal catalysts. Furthermore, the evolved oxygen gas possesses relatively low market value. Consequently, extensive research has shifted toward replacing the OER with value-added oxidation reactions,6–8 thereby enabling a dual-benefit system that simultaneously generates clean energy at the cathode and performs environmental remediation at the anode. Among these, the electrochemical production of hydrogen peroxide (H2O2) is of significant interest. H2O2 is a potent oxidant widely utilized in chemical synthesis and wastewater treatment. Notably, H2O2 can be efficiently synthesized in KHCO3 electrolytes without complex additives via the two-electron water oxidation reaction (2e-WOR).9 Compared to the four-electron OER, the 2e-WOR is kinetically more favorable due to fewer electron transfer steps, leading to a theoretically lower overpotential.10,11

Despite these advantages, the practical application of electro-synthesized H2O2 for water treatment faces critical limitations. The inherent oxidation potential of H2O2 is relatively modest at 1.76 V vs. normal hydrogen electrode (NHE),12,13 which is often insufficient for the rapid degradation of recalcitrant organic pollutants or the complete inactivation of resilient bacterial strains. As a result, an additional activation step is typically required to generate highly reactive hydroxyl radicals (˙OH).14–16 However, conventional heterogeneous Fenton or Fenton-like processes suffer from sluggish interfacial reaction kinetics, which significantly restrict radical generation efficiency.17 Moreover, performing this activation as a separate, subsequent process often involves complex handling and the inherent challenges of stabilizing and transporting unstable H2O2.18 Conventional strategies to accelerate Fenton-like reactions, such as catalyst structure engineering or thermal activation,19–21 have shown limited success in fundamentally overcoming these kinetic constraints.

Recently, external-field-assisted catalysis has emerged as a promising approach for regulating reaction pathways. Magnetic field-assisted catalysis, in particular, modulates spin-dependent electron transfer processes by aligning electron spins within magnetic materials, which lowers activation energy barriers and accelerates reaction kinetics.22–24 Significant efficiency gains could be realized if we introduce this new concept to the electrochemical generation of H2O2 with its immediate in situ activation, thereby eliminating intermediate handling steps while maximizing reactive radical utilization.

In this study, we report, for the first time, an integrated system that couples the two-electron water oxidation reaction (2e-WOR) for H2O2 production with a magnetic field-enhanced Fenton-like reaction. By coupling the in situ production and simultaneous decomposition of H2O2 into ˙OH, we achieve a strong synergistic effect for high-efficiency water disinfection. To realize this, we synthesized a unique heterostructure comprising Fe3O4 nanospheres decorated with Mn-doped SnO2. In this architecture, Mn doping modulates the electronic structure of SnO2, significantly reducing charge transfer resistance to drive continuous H2O2 generation, while the Fe3O4 serves as the Fenton-like activation center. Notably, an external magnetic field accelerates radical generation at the catalyst interface. This dual-functional system achieves 99.9% bacterial inactivation, offering a new strategy for integrating spin-dependent catalysis with electrochemical systems for sustainable water treatment.

2 Experimental

2.1. Chemicals and materials

FeCl3 (Sigma-Aldrich), NaAc·3H2O (Sigma-Aldrich), PEG 2000 (TCI), ethylene glycol, SnCl4·5H2O, MnCl2·4H2O, DI water, KHCO3, H2SO4, KMnO4, terephthalic acid (TA), Escherichia coli (ATCC 25922, Kisan Bio, Korea), Luria Bertani broth (E. coli, LB, Kisan Bio, Korea).

2.2. Synthesis of Fe3O4

The method was adapted from a previously reported procedure.25 FeCl3 14.2 mmol, NaAc·3H2O 46 mmol, PEG 2000 were dissolved in ethylene glycol 70 mL, and then the solution was stirred overnight. The mixed solution was transferred into a 100 mL Teflon-lined stainless-steel autoclave. The autoclave was sealed and heated to 200 °C for 6 h and then cooled to room temperature. The obtained powder was washed three times with deionized water (DI water) using a magnet and then dried in a vacuum oven at 60 °C overnight.

2.3. Synthesis of Mn-doped SnO2@Fe3O4

Fe3O4 7.24 mmol, SnCl4·5H2O 2.8 mmol, MnCl2·4H2O 0.14 mmol and 2.8 mmol PEG 2000 5 mmol were mixed in 20 mL DI water, and then the solution was stirred for 30 min. NaOH 32 mmol and DI water 15 mL were added to the mixed solution. The mixed solution was transferred into a 100 mL Teflon-lined stainless-steel autoclave. The autoclave was sealed and heated to 180 °C for 10 h and then cooled to room temperature. The obtained powder was washed three times with DI water using a magnet and then dried in a vacuum oven at 60 °C overnight.

2.4. Synthesis of SnO2@Fe3O4

The synthesis was conducted following the same procedure as that of Mn-doped SnO2@Fe3O4, but without the addition of MnCl2·4H2O.

2.5. Materials characterization

The crystalline structure of the catalysts was determined by X-ray diffraction (XRD) on a Rigaku SmartLab (Cu-Kα source with λ of 0.15406 nm). The elemental composition of the material was analyzed by using a PerkinElmer Avio 550 Max ICP-OES spectrometer. The morphology of the catalyst was characterized by scanning electron microscope (SEM) JEOL JSM-7100F and transmission electron microscope (TEM) on JEOL JEM-F200 at 200 kV, element composition and distribution by energy dispersive X-ray spectroscopy (EDS) element mappings. X-ray photoelectron spectroscopy (XPS) was performed to characterize the electronic structures of the catalyst on NEXSA G2 with an Al Kα X-ray source (1.4866 keV).

2.6. Electrocatalytic analysis

All the electrochemical data were collected on a Zive SP-1 potentiostat (Wonatech). Catalytic performance was conducted in 2 M KHCO3 with a 3-electrode system. The catalyst ink, 5 mg of the catalyst powder, was dispersed into the solution, including 490 µL of IPA, 490 µL of DI water, and 20 µL of Nafion (5 wt%). The mixed solution was sonicated for 1 h. Then, 50 µL of the catalyst ink was loaded on 0.5 × 0.5 cm2 carbon paper as the working electrode. The Ag/AgCl as the reference electrode and the Pt mesh as the counter electrode were used. The concentration of produced H2O2 was determined via potentiometric titration using a potassium permanganate KMnO4 solution. The redox reaction is as follows:
2KMnO4 + 5H2O2 + 3H2SO4 → 2MnSO4 + 5O2 + 8H2O + K2SO4

In a typical titration, the reaction solution was titrated with 0.02 M KMnO4 in the presence of 1 mL of 3 M H2SO4 until the light pink endpoint was reached.26

To determine the faradaic efficiency (FE) of hydrogen, we employed the water displacement method.27 The FE was evaluated at potentials ranging from 2.0 to 3.0 V vs. RHE for durations of 5, 10, and 15 min.

Faradaic efficiency = znF/Q
where z is the number of electrons transferred, n is the number of moles of the product produced, F is the Faraday constant (96[thin space (1/6-em)]485 C mol−1), Q is total charge.

To detect ˙OH, radical probe experiments were conducted by adding 12 mM terephthalic acid (TA) to the 2 M KHCO3 electrolyte. The reaction between TA and ˙OH to form the fluorescent product, 2-hydroxyterephthalic acid (2-HTA), proceeded according to the following equation:

C6H4(COOH)2 + ˙OH → C6H3(OH)(COOH)2 + ˙H

The resulting 2-HTA was analysed by using PL spectroscopy, with its characteristic fluorescence signal being monitored at an emission wavelength of 425 nm.

2.7. Antibacterial experiments

For antibacterial experiments, E. coli was incubated in Luria Bertani broth at 37 °C with 200 rpm agitation for 12 h (shaking incubator, LI-BS100, LK LAB KOREA, Korea). Then, the optical density of bacterial suspension was measured at 600 nm (OD600) to determine the number of bacteria using ultra-visible (UV-vis) spectroscopy and diluted to the final concentration of 2 × 106 CFU mL−1 with a 2 M KHCO3 in phosphate-buffer saline (PBS, 1×, Sigma Aldrich, USA) solution. The prepared bacterial suspension (20 mL) was added to a cell containing the catalytic electrode (1 mg mL−1). The reaction was conducted at 2.6 V vs. reversible hydrogen electrode (RHE) at room temperature. At each time, 100 µL of an aliquot from the reaction suspension was diluted 2 times (10−2) followed by 100 µL aliquot was spread on an LB agar plate. After incubation at 37 °C for 12 h, the colony-forming unit of bacteria was estimated using the standard-counting method.

3 Results and discussion

3.1. Structure characterization

The Fe3O4 nanospheres were synthesized via a hydrothermal method, followed by a subsequent hydrothermal process to grow either SnO2 or Mn-doped SnO2, resulting in SnO2@Fe3O4 (TOFO) and Mn-SnO2@Fe3O4 (MTOFO) heterostructures, respectively. To investigate the crystalline structure of the prepared catalysts, XRD analysis was performed. Fig. 1a shows the XRD patterns of TOFO and MTOFO, which clearly exhibit the characteristic peaks of Fe3O4. These peaks remain well-preserved after the incorporation of SnO2, while the emergence of new diffraction peaks corresponding to SnO2 confirms the successful formation of the SnO2@Fe3O4 heterostructure. Furthermore, a discernible peak shift in the SnO2 diffraction lines was observed following Mn-doping, indicating the successful integration of Mn ions into the SnO2 lattice.28 To quantitatively verify the successful doping of Mn, ICP-OES analysis was performed, with the results presented in Fig. S1. The detected Mn content of 0.46 wt% provides quantitative support for the structural shifts observed in XRD.
image file: d6ta02632j-f1.tif
Fig. 1 Characterization of crystal structure and morphology: (a) XRD patterns of Fe3O4, TOFO, MTOFO. (b) SEM image of MTOFO. (c) HR-TEM image of MTOFO. (d) HAADF-STEM images of MTOFO and EDS corresponding elemental and mixed mapping.

The morphological evolution was further examined through SEM, as shown in Fig. 1b and S2. The pristine Fe3O4 displayed a uniform nanospherical morphology, which was maintained even after the secondary growth of the SnO2 layers. For a more detailed structural analysis, HR-TEM was employed. The low-magnification TEM images corroborated the SEM findings, showing well-defined nanospherical structures.

At higher magnification, Fig. 1c and S3, S4 reveal the lattice fringes and the interfacial relationship within the heterostructure. The measured d-spacings of 0.34 and 0.49 nm correspond to the (110) facet of SnO2 and the (111) facet of Fe3O4, respectively.29,30 These findings further substantiate the successful construction of the heterojunction between the two phases. Finally, Fig. 1d and S5 shows the elemental distribution through scanning transmission electron microscopy (STEM)-EDS mapping. The elemental maps demonstrate that Mn and Sn are uniformly distributed over the surface of the Fe3O4, confirming the successful synthesis of the Fe3O4 nanospheres decorated with Mn-doped SnO2.

XPS was conducted to investigate the electronic structures of the synthesized catalysts. As shown in the Sn 3d spectra of Fig. 2a, the binding energies for Sn4+ and Sn2+ in the Sn 3d5/2 state of the pristine TOFO were observed at 487.9 and 487.0 eV, respectively.31,32 Following Mn doping, these peaks shifted to lower binding energies of 487.5 and 486.4 eV. A similar negative shift was observed in the Sn 3d3/2 spectra, where the Sn4+ and Sn2+ peaks moved from 496.6 and 495.7 eV to 496.0 and 495.4 eV, respectively. Furthermore, the successful incorporation of Mn was confirmed by the Mn 2p XPS peaks provided in Fig. S6.


image file: d6ta02632j-f2.tif
Fig. 2 Characterization of electronic structure: (a) XPS analysis of TOFO, MTOFO electrocatalysts in terms of Sn 3d. (b) Fe 2p.

Fig. 2b displays the high-resolution Fe 2p XPS spectra. Notably, the Fe3+ signal is split into two distinct peaks corresponding to the tetrahedral and octahedral sites, which is a characteristic feature of Fe3O4. For the pristine TOFO, the Fe 2p3/2 peaks assigned to Fe2+, octahedral Fe3+ (Feoct3+), and tetrahedral Fe3+ (Fetetra3+) were located at 710.0, 711.4, and 712.6 eV, respectively.33 In the MTOFO catalyst, these peaks shifted to 710.0, 711.2, and 712.4 eV. This shift to lower binding energies is attributed to electron transfer from the Mn-doped SnO2, driven by its relatively lower oxidation state. Correspondingly, in the Fe 2p1/2 spectra, the peaks for Fe2+, Feoct3+, and Fetetra3+ shifted from 723.0, 724.2, and 725.7 eV to 723.3, 724.4, and 725.3 eV. Finally, the O 1s XPS spectra revealed an increase in the proportion of the surface hydroxyl (–OH) peak in Fig. S7.

3.2. Electrocatalytic performance

The electrochemical evaluations were conducted using a three-electrode system to investigate the influence of an external magnetic field on catalytic performance in Fig. S8. As shown in Fig. 3a, linear sweep voltammetry (LSV) revealed that all catalysts exhibited similar onset potentials at 1.7 V vs. RHE. Notably, the MTOFO catalyst under a magnetic field achieved the highest current density. Analysis of the Tafel slopes in Fig. 3b showed that peaks were distributed at similar positions regardless of the magnetic environment. Interestingly, Mn-doping led to a reduction in the Tafel slope at consistent potentials, suggesting that while the magnetic field influences the reaction at the onset, the Mn-dopants fundamentally enhance the intrinsic catalytic reactivity.
image file: d6ta02632j-f3.tif
Fig. 3 Electrocatalytic performance (a) polarization curves of the TOFO and MTOFO with(out) magnet. (b) Tafel plot and (c) Nyquist plot at 1.8 V vs. RHE in 2 M KHCO3. (d) ECSA of each catalyst and with(out) magnet. (e) H2O2 yields at various applied potentials. (f) Stability of MTOFO at 2.6 V vs. RHE.

Electrochemical impedance spectroscopy (EIS) further confirmed this enhancement, where Fig. 3c demonstrates that Mn-doping reduced the charge transfer resistance (Rct) from 4 ohm for TOFO to 3 ohm for MTOFO. The electrochemically active surface area (ECSA) measurements, as shown in Fig. 3d and S9, yielded double-layer capacitance values of 68 mF cm−2 for TOFO and 52 mF cm−2 for MTOFO.

Subsequently, H2O2 production rates were evaluated as a function of applied potential. Fig. 3e presents that at an applied potential of 2.6 V vs. RHE, MTOFO reached a maximum H2O2 production rate of 60.2 µmol min−1. Intriguingly, the H2O2 yield for MTOFO decreased under specific magnetic conditions, which prompted further investigation into radical generation. It was confirmed that the catalyst exhibits significantly higher efficiency compared to previously reported 2e-WOR catalysts, as summarized in Table S1.

In addition, the faradaic efficiency (FE) of MTOFO was measured within the potential range of 2.0–3.0 V vs. RHE to quantify the hydrogen production. A high FE of over 90% was consistently observed across all measured potentials in Fig. S10 and S11. Finally, long-term stability tests at 2.6 V confirmed that the catalyst maintained robust performance for over 15 h in 2 M KHCO3 in Fig. 3f. Finally, long-term stability tests at 2.6 V confirmed that the catalyst maintained robust performance for over 15 h in 2 M KHCO3 in Fig. 3f. Furthermore, to evaluate operational stability under practical conditions, the durability was tested at 2.6 V vs. RHE in tap water, both with and without the addition of 2 M KHCO3. The catalyst exhibited sustained stability for over 15 h and 35 h, respectively, as shown in Fig. S12.

3.3. Electrochemical radical probe and bacterial disinfection

To elucidate the observed decrease in H2O2 production under magnetic fields, we hypothesized that H2O2 was being consumed to generate ˙OH. A radical probe experiment was performed using 12 mM TA in a KHCO3 electrolyte at 2.6 V vs. RHE.34,35 During the initial 30 min, the photoluminescence (PL) peaks at 425 nm saturated at a consistent level regardless of the magnetic field in Fig. 4a. However, after 1 h, only the catalyst that reacted under the magnetic field showed a significant increase in PL intensity. The magnetic field facilitates a Fenton-like reaction and the production of ˙OH for 2-HTA formation, a kinetic acceleration which is primarily attributed to the synergistic effect of spin-state regulation and structural modulation of radical intermediates. Theoretically, radicals are generated as pairs in either singlet (S) or triplet (T) configurations.36 In the absence of a magnetic field, singlet radical pairs (e.g., 1[HO˙↑⋯↓˙OH]) tend to rapidly recombine into H2O2 due to the Pauli exclusion principle, thereby limiting the steady-state concentration of active species.37 The application of an external magnetic field induces Zeeman energy splitting of the triplet sublevels, which effectively promotes S → T intersystem crossing while suppressing the T → S evolution.38,39 Given that the recombination of triplet radical pairs is spin-forbidden, these species exhibit a significantly higher dissociation probability, allowing a greater population of free radicals to escape and participate in the Fenton-like reaction, which effectively lowers the apparent activation energy. Furthermore, literature suggests that the external field acts as an equivalent force that lengthens O–O and O–H bonds in H2O2, further reducing the energy barrier for bond scission and facilitating the observed kinetic promotion and efficient H2O2 utilization.40
image file: d6ta02632j-f4.tif
Fig. 4 Radical probe and antibacterial test (a) PL spectra of TA probe test for 30 m and 60 m. (b) Time-dependent log-reduction of bacteria in 2 M KHCO3 for MTOFO with (out) magnet (n = 3 independent experiments per bacterial concentration). (c) Bacterial colonies images during antibacterial experiments using 2 M KHCO3.

This radical generation mechanism was further applied to water disinfection. Before the antibacterial experiments, the electrolyte concentrations were optimized to exclude antibacterial effects originating from the electrolyte in Fig. S13. Antibacterial experiments were conducted against E. coli, a representative Gram-negative bacterium. While control experiments at open circuit potential (OCP) showed no significant impact on bacterial survival, MTOFO achieved a 96.1% antibacterial rate at 2.6 V vs. RHE. Remarkably, the synergistic combination of an applied potential of 2.6 V and a magnetic field enhanced the antibacterial activity of MTOFO to 99.9% in Fig. 4b and c. These values represent significantly higher efficiency compared to previously reported catalysts for bacterial disinfection, as summarized in Table S2. These results demonstrate that the synergy between electric current and magnetic fields enables MTOFO to efficiently generate H2O2 and subsequently convert it into highly reactive ˙OH, achieving superior disinfection of high-concentration bacteria.

4 Conclusions

In summary, we successfully achieved simultaneous hydrogen and hydrogen peroxide production via a 2e-WOR using a Mn-doped SnO2@Fe3O4 electrocatalyst with magnet. Going beyond conventional 2e-WOR, the incorporation of Fe3O4 enabled the generation of highly reactive ˙OH through an electro-Fenton-like process. Furthermore, TA probe assays confirmed that the application of an external magnetic field significantly enhanced this Fenton-like reactivity. The generated ˙OH were effectively utilized for bacterial disinfection, demonstrating meaningful results for water purification. We believe that this dual-functional system, concurrently producing clean H2 and potent ˙OH, presents a promising new strategy for advanced wastewater treatment. Future studies will focus on implementing this system in more complex, real-world environmental matrices.

Author contributions

Y. H. and J. C. conceived and designed the studies and wrote the paper. Y. H. and S. O. synthesized the materials, performed electrochemical experiments, and PL. H. K. supported the characterization and SEM analysis. H. L. provided direction, supervision, and editing of this paper.

Conflicts of interest

There are no conflicts to declare.

Data availability

The data that support the findings of this study are available in the supplementary information (SI) of this manuscript. Supplementary information: additional ICP-OES data, SEM, TEM, and STEM-EDS images, and XPS Mn 2p and O 1s spectra; stability tests conducted with tap water, the cell setup image, faradaic efficiency of hydrogen, and the viability of E. coli depending on KHCO3 concentration. Additionally, summary tables comparing this work with previously published literature are provided. See DOI: https://doi.org/10.1039/d6ta02632j.

Acknowledgements

This work was supported by the National Research Foundation of Korea (NRF) grant funded by the Korean Government (MSIT) (NRF-2022R1A2C2093415) and partially supported by the Korea Basic Science Institute (National Research Facilities and Equipment Center) grant funded by the Ministry of Education (RS-2022-NF000854).

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Footnote

These authors contributed equally to this work.

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