4.8 Article

Electron Hopping Enables Rapid Electron Transfer between Quinone-/Hydroquinone-Containing Organic Molecules in Microbial Iron(III) Mineral Reduction

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ENVIRONMENTAL SCIENCE & TECHNOLOGY
卷 54, 期 17, 页码 10646-10653

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AMER CHEMICAL SOC
DOI: 10.1021/acs.est.0c02521

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  1. German Research Foundation [KA1736/37-1]
  2. Alexander von Humboldt Foundation

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The mechanism of long-distance electron transfer via redox-active particulate natural organic matter (NOM) is still unclear, especially considering its aggregated nature and the resulting low diffusivity of its quinone- and hydroquinonecontaining molecules. Here we conducted microbial iron(III) mineral reduction experiments in which anthraquinone-2,6-disulfonate (AQDS, a widely used analogue for quinone- and hydroquinone-containing molecules in NOM) was immobilized in agar to achieve a spatial separation between the iron-reducing bacteria and ferrihydrite mineral. Immobilizing AQDS in agar also limited its diffusion, which resembled electron-transfer behavior of quinone- and hydroquinone-containing molecules in particulate NOM. We found that, although the diffusion coefficient of the immobilized AQDS/AH(2)QDS was 10 times lower in agar than in water, the iron(III) mineral reduction rate (1.60 +/- 0.28 mmol L(-)1 Fe(II) d(-1)) was still comparable in both media, indicating the existence of another mechanism that accelerated the electron transfer under low diffusive conditions. We found the correlation between the heterogeneous electron-transfer rate constant (10(-3) cm s(-1)) and the diffusion coefficient (10-7 cm(2) s(-1)) fitting well with the diffusion-electron hopping model, suggesting that electron transfer via the immobilized AQDS/AH(2)QDS couple was accomplished through a combination of diffusion and electron hopping. Electron hopping increased the diffusion concentration gradient up to 10(6)-fold, which largely promoted the overall electron-transfer rate during microbial iron(III) mineral reduction. Our results are helpful to explain the electron-transfer mechanisms in particulate NOM.

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