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Cytochromes as microbial electron ‘wires’ — and how on-site qPCR turns this into decisions

Cytochromes as microbial electron ‘wires’ — and how on-site qPCR turns this into decisions

Cytochromes are heme proteins that carry electrons. In many bacteria, multi-heme c-type cytochromes form chains that conduct electrons across the cell envelope to solids (minerals, metals, electrodes). We outline the science, why it matters for MIC, and how MICBUSTERS’ on-site qPCR makes it actionable.

What is a cytochrome?

A cytochrome is a hemoprotein whose heme cycles between Fe(II)/Fe(III), enabling electron transfer. Classes (a, b, c) refer to heme type/binding; c-types are covalently bound via the CXXCH motif. In bacteria, membrane- and surface-exposed cytochromes underpin respiration and extracellular electron transfer (EET).

From single heme to ‘heme wires’: multi-heme c-types

Multi-heme cytochromes stack several hemes within one polypeptide. Efficient electron flow emerges from heme–heme coupling and a graded set of redox potentials. Canonical systems include:

  • Shewanella (Mtr/Omc): MtrA (periplasm), MtrC/OmcA (outer membrane, decaheme), plus a β-barrel conduit to the surface.
  • Geobacter (OmcS/OmcZ): outer-surface cytochromes forming nanowires; OmcZ filaments exhibit high conductivity and support large current densities.
  • Desulfovibrio (SRB): periplasmic cytochrome c3 (tetraheme) interfaces with hydrogenases and Hmc complexes toward sulfate reduction.

Cytochromes in EET: direct, mediated, hybrid

Multi-heme cytochromes enable direct transfer to/from solids; mediated routes via soluble shuttles (e.g., flavins) extend reach. Real biofilms often run a hybrid of both.

Why this matters for MIC

In MIC, the cathodic step frequently limits overall rates. Surface cytochromes can draw electrons from metals/conductive films more efficiently, raising cathodic current and corrosion.

  • Current → loss (rule-of-thumb): 1 µA/cm² ≈ 0.011–0.012 mm/y uniform loss; +10 µA/cm² ≈ +0.12 mm/y (order-of-magnitude; pitting can exceed this).
  • Consortia: EET-active, cytochrome-rich bacteria can coexist with methanogen-linked routes (e.g., micH), jointly aggravating corrosion.
  • Films/minerals: FeS, magnetite and other conductive phases can bridge cytochromes to metal, shaping MIC kinetics.

MICBUSTERS on-site qPCR: making cytochrome-EET actionable

The practical question is: “Do we host a cytochrome-rich, EET-active community that elevates MIC risk?” Our on-site qPCR answers this within hours, via:

1) Marker panel (asset-specific)

  • EET/cytochrome genes: outer-membrane/periplasmic markers such as mtrC/omcA (Shewanella), omcS/omcZ (Geobacter), hmc complex (Desulfovibrio).
  • Community anchors: bacterial/archaeal 16S rRNA plus functional targets (e.g., mcrA for methanogens); optional micH for methanogen-linked corrosion.
  • Assay design: degenerate primers as needed, matrix-validated efficiency/specificity (melt curves or probe assays).

2) Quantification & normalization

  • Absolute qPCR: standard curves; report as gene copies per mL (fluids/sludge) or per cm² (biofilm/coupons).
  • Relative indices: normalize EET markers to 16S to compute an Cytochrome-EET Index (CEI) (sum or weighted sum of mtrC/omcA/omcS/omcZ/hmc vs 16S).
  • Live fraction (optional): PMA-qPCR to distinguish intact cells from relic DNA.

3) Reporting to decisions

  • Trends & heatmaps: CEI, 16S load, functional markers across time and location.
  • Electrochemistry linkage: Rising CEI concurrent with increased cathodic current supports an EET-driven MIC hypothesis.
  • Action bands (heuristics; calibrate on site):
    • Low/stable CEI + low Icath → routine monitoring.
    • Rising/high CEI + moderate Icath → targeted tests (biofilm/cathode assays).
    • High CEI + high Icath (>~13 µA/cm² ≈ >0.15 mm/y) → escalate mitigation; verify impact with qPCR + ER/coupons.

From genes to mm/y

qPCR quantifies capacity, not current. By co-trending CEI with cathodic current/potential and metal-loss (ER/coupons), site-specific models convert biology into predicted mm/y and document mitigation impact within a single maintenance window.

References (selected)

  • Shi L. et al. (2016) Extracellular electron transfer mechanisms between microorganisms and minerals. Nat Rev Microbiol.
  • Breuer M., Rosso K.M., Blumberger J. (2014) Electron flow in multiheme bacterial cytochromes. PNAS.
  • Gu Y. et al. (2023) Structure & conductivity of Geobacter OmcZ nanowires. Nat Microbiol.
  • Marsili E. et al. (2008) Flavin-mediated EET in Shewanella. PNAS.
  • Valente F.M.A. et al. (2001) Tetraheme cytochrome c3 in Desulfovibrio. J Bacteriol.
  • Lahme S. et al. (2021) Severe corrosion linked to methanogens via micH. Appl Environ Microbiol.
  • Knisz J. et al. (2023) MIC—more than microbes. FEMS Microbiol Rev.

Disclaimer
This article is intended for informational and educational purposes and does not replace site-specific engineering or scientific assessment. MICBUSTERS has a commercial interest in improving MIC diagnostics and monitoring for industrial clients.

MICBUSTERS specializes in measuring microbiological processes that lead to the degradation of metals.
(NL: “MICBUSTERS is gespecialiseerd in het meten van microbiologische processen die leiden tot aantasting van metalen.”)

Results and recommendations depend on sampling quality, analytical methods, and operational variability. Implementation of mitigation measures remains the responsibility of the asset owner and their appointed advisors.

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