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Ferrous iron (Fe(II)) species are prevalent in reductive subsurface environments, where some active Fe(II) species can generate hydroxyl radical (·OH) during oxidation under O perturbation, facilitating pollutant attenuation. However, aqueous Fe(II), a common form of ferrous iron, can be rapidly oxidized but scarcely contributes to ·OH production. Herein, this study proposes a thermodynamic control strategy by introducing micro-nanobubbles (MNBs) into an aqueous Fe(II)/O system to stimulate its potential. Experimental results indicate that MNBs alter the electron transfer pathway from aqueous Fe(II) to O, shifting the predominant mechanism from a one-electron transfer pathway to a two-electron transfer pathway; this can reduce energy loss and improve the overall electron utilization efficiency. Under optimal conditions, ·OH production and pollutant degradation reached 20 μM and 15%, respectively, compared to almost 0 in the system without MNBs. Thermodynamic analysis reveals that MNBs lower the oxidation-reduction potential (ORP) of the system and reduce the Gibbs free energy of key reaction steps, enabling efficient ·OH production. The aqueous Fe(II)/MNBs/O system demonstrates a broad applicability for the degradation of various pollutants with removal rates ranging from 25% to 36%, highlighting its potential as a promising approach for green and sustainable groundwater remediation.
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http://dx.doi.org/10.1021/acs.est.5c09634 | DOI Listing |
Water Res
August 2025
State Key Laboratory of Water Pollution Control and Green Resource Recycling, College of Environmental Science and Engineering, Tongji University, Shanghai 200092, China; Shanghai Institute of Pollution Control and Ecological Security, Shanghai 200092, China. Electronic address:
Anaerobic co-digestion of sulfur-containing organic wastes with waste-activated sludge containing iron-phosphorus compounds (FePs) was recently suggested as an environment-friendly strategy to promote phosphate release, energy recovery, and hydrogen sulfide (HS) control. Nevertheless, the mechanistic coupling between FePs speciation and the concurrent transformation of carbon, sulfur, iron, and phosphorus within this system remains to be fully elucidated. To address this knowledge gap, methionine, a typical hydrolysis product of sulfur-containing organics, and five FePs prevalent in sludge (ferric-phosphate tetrahydrate (FePO⋅4HO), ferric-phosphate dihydrate (FePO⋅2HO), vivianite (Fe(PO)·8HO), phosphate coprecipitated with Fe(III) (COP-P), and phosphate adsorption on hydrous ferric oxide (HFO-P)) were selected to elucidate C-S-Fe-P transformations in this study.
View Article and Find Full Text PDFEnviron Sci Technol
September 2025
State Key Laboratory of Pollution Control and Resources Reuse, Tongji University, Shanghai 200092, China.
Ferrous iron (Fe(II)) species are prevalent in reductive subsurface environments, where some active Fe(II) species can generate hydroxyl radical (·OH) during oxidation under O perturbation, facilitating pollutant attenuation. However, aqueous Fe(II), a common form of ferrous iron, can be rapidly oxidized but scarcely contributes to ·OH production. Herein, this study proposes a thermodynamic control strategy by introducing micro-nanobubbles (MNBs) into an aqueous Fe(II)/O system to stimulate its potential.
View Article and Find Full Text PDFEnviron Sci Process Impacts
August 2025
State Key Laboratory of Geomicrobiology and Environmental Changes, School of Environmental Studies, China University of Geosciences, Wuhan 430074, Hubei, China.
The bacterium strain HJ-2 has been reported as a nitrate-dependent iron-oxidizing bacterium, surprisingly with Fe(III) reduction ability. The control of iron redox cycling by the strain HJ-2 in the Fe(II)-Fe(III) co-existing system is mysterious and worthy of exploration. The present study demonstrates that HJ-2 utilizes nitrate as an electron acceptor to rapidly oxidize Fe(II), with negligible Fe(III) reduction, under neutral pH and anaerobic conditions in a co-existing Fe and ferrihydrite system.
View Article and Find Full Text PDFEnviron Res
August 2025
State Key Laboratory of Pollution Control and Resource Reuse, School of Environment, Nanjing University, Nanjing, 210023, PR China.
Various organic acids commonly coexist with Cr(VI) in wastewater. However, direct electron transfer between Cr(VI) and electron-rich organic acids is typically slow. Current Fe-based mediators primarily operate through the aqueous Fe(III)/Fe(II) cycle, which faces challenges in achieving efficient Fe recycling.
View Article and Find Full Text PDFJ Environ Manage
August 2025
Hubei Key Laboratory of Microbial Transformation and Regulation of Biogenic Elements in the Middle Reaches of the Yangtze River, School of Environmental Ecology and Biological Engineering, Wuhan Institute of Technology, 206 Guanggu 1st Road, Wuhan, 430205, PR China. Electronic address:
As(III) and Fe(II) co-oxidation by oxygen is an important process in arsenic migration, transformation, and pollution remediation in various aqueous environments. Fe(II) frequently co-exists with Mn(II) in natural settings, and their synergistic oxidation process is typically regarded as the supporting factor for As(III) oxidation. Herein, we found that Mn(II) significantly inhibited As(III) oxidation during As(III) and Fe(II) co-oxidation under near-neutral pH (6.
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