Harnessing solar energy for environmental cleanup: Iron mineral-bacterial biofilms degrade pollutants
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Harnessing solar energy for environmental cleanup: Iron mineral-bacterial biofilms degrade pollutants

25/10/2025 TranSpread

This process significantly enhances the degradation of antibiotics like tetracycline hydrochloride (TCH) and chloramphenicol (CPL), marking a new frontier in bioremediation techniques and sustainable pollution control.

Solar radiation is a crucial driver of biological processes, traditionally recognized for its role in plant photosynthesis. Recent studies have uncovered the ability of non-phototrophic microorganisms, such as those in soils and sediments, to harvest solar energy through mineral-microbe interactions. These findings point to the broader influence of sunlight on microbial metabolism and geochemical processes, even in saturated environments like soils and sediments. By harnessing the interaction between minerals like iron and microorganisms, this emerging field of biophotoelectrochemistry provides a new mechanism for energy storage and pollutant mitigation in dark zones of soil, where light penetration is limited.

A study (DOI: 10.48130/ebp-0025-0006) published in Environmental and Biogeochemical Processes on 15 September 2025 by Bo Pan’s & Baoshan Xing’s team, Kunming University of Science and Technology & University of Massachusetts, offers a sustainable, efficient, and scalable method for addressing soil and groundwater pollution, opening new possibilities for clean-up strategies in diverse ecosystems.

In this study, the interaction between iron minerals (Fe2O3 or FeOOH) and the bacterium Bacillus megaterium (B. megaterium) was explored to investigate the accumulation and release of electrons during light-dark cycles. The co-culturing system showed a continuous charge-discharge function and a photovoltage memory effect. The electron storage capacity, measured as the total accumulated charge (∑σ), increased with higher bacterial density, indicating that denser biofilms facilitate more efficient charge capture and storage. The system demonstrated a clear disparity between charge accumulation in the light and release in the dark, with the light-exposed systems consistently achieving higher charge values. Notably, the net accumulated charge increased from 2.87 μC·cm−2 to 4.08 μC·cm−2 after several cycles. This unique "photovoltaic memory" feature of the biofilm was further evidenced by a significant increase in the degradation efficiency of pollutants, such as TCH and CPL, during the dark phase following light exposure. After 60 minutes of light exposure, degradation efficiency for TCH and CPL improved by 66.7% and 46.7%, respectively. The mechanism behind this degradation was attributed to the synergistic interaction between the iron minerals and bacteria, which facilitated efficient electron transfer and storage, enabling the system to function as a "biological capacitor." The structural and electrochemical analyses revealed that the bacteria-mineral biofilms enhanced electron transfer and facilitated charge storage, leading to significant improvements in pollutant degradation. These findings suggest that the Fe2O3 /B. megaterium biofilm system offers a promising, sustainable method for addressing environmental pollution, particularly in soil and groundwater, through light-driven charge storage and release mechanisms.

This study provides valuable insights into the potential for using solar-powered biofilms to treat environmental pollutants in soils and sediments. The biocapacitor mechanism demonstrated by the Fe2O3/B. megaterium system offers a sustainable method for pollution control that does not require continuous illumination. The ability of these biofilms to store and release energy for pollutant degradation in dark environments could revolutionize bioremediation practices, particularly for soil and groundwater treatment. This system has the potential to enhance the effectiveness of current methods, providing a cost-effective and energy-efficient solution for cleaning up antibiotic-contaminated sites.

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References

DOI

10.48130/ebp-0025-0006

Original Source URL

https://doi.org/10.48130/ebp-0025-0006

Funding Information

This work was supported by the National Natural Science Foundation of China (42130711, 42377250, and 42267003), the National Key Research and Development Program of China (2023YFC3709100), the Yunnan Major Scientific and Technological Projects (202202AG050019), the Yunnan Fundamental Research Projects (202301AU070078, 202201BE070001-040), and Guided by the Central Government for Local Science and Technology Development Funds (202407AB11026).

About Environmental and Biogeochemical Processes

Environmental and Biogeochemical Processes is a multidisciplinary platform for communicating advances in fundamental and applied research on the interactions and processes involving the cycling of elements and compounds between the biological, geological, and chemical components of the environment.

Title of original paper: A bio-photovoltage soil-microbe battery for antibiotic degradation in the dark
Authors: Shunling Li1,2, Ye Chen1,2, Min Wu1,2,3, Peng Zhang1,2, Peng Cui1,2, Wenyan Duan1,2, Bo Pan1,2, , & Baoshan Xing3
Journal: Environmental and Biogeochemical Processes
Original Source URL: https://doi.org/10.48130/ebp-0025-0006
DOI: 10.48130/ebp-0025-0006
Latest article publication date: 15 September 2025
Subject of research: Not applicable
COI statement: The authors declare that they have no competing interests.
Attached files
  • Figure 3. B. megaterium reduces the Fe(III) in Fe2O3 to Fe3(PO4)2, along with the altered elemental composition and electronic structure of the mineral. The content of Fe(II) increased with the increase of (a) bacteria proportion, (b) crystal type, and (c) Raman intensity also changed after B. megaterium and Fe2O3 co-culturing.
25/10/2025 TranSpread
Regions: North America, United States
Keywords: Science, Environment - science, Applied science, Engineering

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