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Shewanella oneidensis

Shewanella oneidensis is a Gram-negative, rod-shaped, facultatively anaerobic bacterium belonging to the class Gammaproteobacteria in the phylum Pseudomonadota, renowned as a model electrochemically active bacterium (EAB) for its versatile respiratory metabolism and capacity for extracellular electron transfer (EET). This heterotrophic species, primarily utilizing low-molecular-weight organic compounds such as lactate as carbon sources, thrives in freshwater sediments rich in organics and solid electron acceptors, such as those in Lake Oneida. First isolated in 1988 from the anoxic mud of Oneida Lake in New York, the type strain MR-1 has a fully sequenced genome of approximately 4.8 million base pairs, enabling extensive genetic and physiological studies. The bacterium's defining feature is its respiratory versatility, allowing it to utilize a broad spectrum of acceptors under both aerobic and conditions, including oxygen, , fumarate, (DMSO), and various metals such as iron(III), (IV), and uranium(VI). This capability is facilitated by specialized EET pathways involving multi-heme (e.g., MtrC and OmcA) and electrically conductive pilus-like structures known as bacterial nanowires, which enable direct with insoluble substrates or electrodes without physical contact. Ecologically, S. oneidensis plays a key role in biogeochemical cycles, particularly in the reduction of metal oxides and the remediation of contaminated environments by immobilizing toxic . In , S. oneidensis MR-1 serves as a platform organism for bioelectrochemical systems, including microbial fuel cells (MFCs) for , microbial electrolysis cells (MECs) for , and electro-fermentation processes for value-added . Its genetic tractability, supported by tools like synthetic plasmids and CRISPR-based editing, has advanced applications in and , such as enhancing bioelectricity output or enabling controlled via living electrodes. Despite its promise, challenges remain in optimizing its limited substrate utilization and scaling EET efficiency for industrial use.

Classification and Discovery

Taxonomy

Shewanella oneidensis belongs to the domain Bacteria, phylum Pseudomonadota, class Gammaproteobacteria, order Alteromonadales, family Shewanellaceae, and genus Shewanella. This placement reflects its phylogenetic position among facultatively anaerobic, Gram-negative bacteria within the γ-Proteobacteria subgroup. The species Shewanella oneidensis was formally described in 1999, with the type strain designated as MR-1 (ATCC 700550). This strain serves as the reference for the species and has been deposited in multiple culture collections, including 106686 and LMG 19005. Phylogenetically, S. oneidensis is closely related to Shewanella putrefaciens, sharing approximately 97% 16S rRNA gene sequence similarity. However, genomic distinctions, such as 35.7% DNA-DNA hybridization and 85% gyrB gene sequence identity with S. putrefaciens, support its classification as a separate . These metrics fall below established thresholds for species delineation (70% for DNA-DNA hybridization and 90% for gyrB). The epithet oneidensis is derived from in , , the freshwater habitat from which the type strain was isolated, highlighting its ecological origin within the genus.

Discovery and Etymology

Shewanella oneidensis was first isolated in 1988 from sediment samples collected in , , by researchers Carol R. Myers and Kenneth H. Nealson. The strain, initially designated MR-1 and classified under Alteromonas putrefaciens, was obtained through enrichment cultures designed to select for microorganisms capable of dissimilatory reduction of oxides using as the . This isolation highlighted the bacterium's unique metabolic versatility in freshwater environments. Initial characterization in the late 1980s and early 1990s, primarily from the Nealson laboratory at the University of Southern California, focused on its dissimilatory metal reduction capabilities. Key studies demonstrated that the isolate could respire manganese(IV) and iron(III) oxides as terminal electron acceptors under anaerobic conditions, establishing it as a model organism for understanding microbial contributions to biogeochemical cycles of metals in sediments. These early investigations, including publications on coupled iron and sulfur oxide biogenesis, laid the groundwork for recognizing its broader respiratory flexibility. The was formally described and named Shewanella oneidensis in 1999 through a polyphasic taxonomic study led by Kasthuri Venkateswaran and colleagues, which reclassified the MR-1 strain based on 16S rRNA sequencing, DNA-DNA hybridization, and physiological traits, placing it within the Shewanella in the family Shewanellaceae. The name Shewanella honors the Scottish James M. Shewan for his pioneering work on marine and fish , while the specific epithet oneidensis derives from the Latinized form of , referencing its site of isolation.

Morphology and Physiology

Cell Structure

Shewanella oneidensis is a Gram-negative, rod-shaped , with cells typically measuring 0.5 μm in and 2–3 μm in length. These dimensions can vary slightly depending on growth conditions, with widths ranging from 0.5–0.65 μm observed in some strains. The bacterium exhibits via a single polar , which is essential for and initial surface attachment. As a Gram-negative , S. oneidensis features a complex cell envelope, including an outer embedded with lipopolysaccharides (LPS) that contribute to structural integrity and protection against environmental stresses. The outer also contains porins, which facilitate the passive diffusion of small hydrophilic molecules across the . The periplasmic space, located between the inner cytoplasmic and the outer , harbors c-type such as CymA, which are integral to the cellular architecture. S. oneidensis is capable of forming biofilms on surfaces and pellicles at air-liquid interfaces, structures that enhance survival in diverse environments. These pellicles develop as three-dimensional matrices primarily composed of an extracellular polymeric substance (EPS) rich in proteins and polysaccharides, with mannose being a prominent sugar component in the polysaccharide fraction. The protein elements of the EPS are critical for matrix stability, as demonstrated by their degradation upon treatment with proteinase K, which disrupts pellicle integrity. Biofilms similarly rely on this EPS matrix, incorporating extracellular proteins and polysaccharides to maintain community cohesion.

Growth Conditions

Shewanella oneidensis is a facultative anaerobe capable of growth under both aerobic and conditions. Optimal growth occurs at mesophilic temperatures between 20°C and 35°C, with the fastest rates observed around 30°C, though it can tolerate extremes down to 4°C and up to 37°C. The bacterium thrives at a range of 6.0 to 9.0, with neutral pH (around 7.0–7.6) supporting maximal proliferation. In laboratory settings, S. oneidensis is routinely cultured in rich media such as (TSB) for aerobic growth or lactate-based minimal media for defined conditions. Under aerobic conditions, oxygen serves as the terminal , while anaerobic growth utilizes alternative acceptors like fumarate or . Carbon sources such as or are essential, often supplied at concentrations of 15–70 mM in minimal media, with micronutrients including iron (e.g., FeCl₂) and (e.g., Na₂MoO₄) required for enzymatic functions and metabolic processes. The organism exhibits tolerance to moderate , with optimal growth in media containing 0.1–0.3 M NaCl (approximately 0.6–1.8%), and reduced but viable growth up to 0.5–0.6 M NaCl (about 3–3.5%), beyond which is severely inhibited. These conditions reflect its adaptability in controlled environments, though growth rates decline under .

Metabolic Capabilities

Respiration Mechanisms

Shewanella oneidensis is a facultative anaerobe capable of aerobic , utilizing oxygen (O₂) as the terminal through an (ETC) that culminates in cytochrome oxidases. The ETC features three terminal oxidases: the cbb₃-type (encoded by the cco operon, SO_2364–2357), which predominates under aerobic conditions due to its high O₂ affinity; the aa₃-type (encoded by cox genes, SO_4606–4609), active under nutrient or with specific carbon sources like pyruvate or ; and the bd-type (cydABX, SO_3286–3284), functional under microaerobic conditions. Aerobic growth is regulated by factors such as the cAMP receptor protein (CRP), which mildly affects growth on , and the cAMP phosphodiesterase CpdA, whose disruption causes significant deficiencies suppressible by mutations in SO_3550. Under anaerobic conditions, S. oneidensis respire alternative electron acceptors including fumarate, , and trimethylamine N-oxide (TMAO), with electrons transferred via menaquinones and c-type . Menaquinones serve as key electron carriers in the anaerobic , facilitating proton translocation. The tetraheme c-type cytochrome CymA (SO_4591) is essential for shuttling electrons to these acceptors, particularly for fumarate and DMSO reduction. Fumarate reduction involves the periplasmic fumarate reductase FccA (SO_0970), which receives electrons from CymA, while DMSO reduction relies on the membrane-bound DmsC (SO_1427); TMAO reduction is mediated by the TorA enzyme in the torECAD . In extreme anaerobiosis without external electron acceptors, S. oneidensis resorts to , converting pyruvate to via . This process, which does not support growth but allows maintenance, produces , , , H₂, and CO₂ from pyruvate, with Dld-II (SO_1521) catalyzing the NAD(P)H-independent reduction of pyruvate to D-. Mutants lacking dld-II exhibit reduced production rates, underscoring its role. These intracellular and mechanisms provide the foundational flow that, in metal-rich environments, can be extended to extracellular processes.

Metal Reduction Processes

Shewanella oneidensis engages in dissimilatory metal reduction, utilizing metals and metalloids as terminal electron acceptors in , thereby reducing their oxidation states. This process couples the oxidation of organic electron donors, such as , to the reduction of metals like (III) to Fe(II), Mn(IV) to Mn(II), U(VI) to U(IV), and Cr(VI) to Cr(III). These reductions occur extracellularly, enabling the bacterium to access insoluble mineral phases in its environment. The reduction mechanisms involve direct contact with solid metal oxides or interaction with chelated, soluble forms. For insoluble substrates, electrons are transferred via outer proteins that bridge the surface to the surface, while soluble chelates, such as Fe(III)-citrate or Fe(III)-NTA, are reduced more readily in the or at the . Key enzymes include the periplasmic triheme PpcA, which shuttles electrons from inner quinol oxidases like CymA to outer transporters, and the decaheme cytochromes MtrC and OmcA, which serve as terminal reductases embedded in the outer . MtrC, part of the MtrCAB complex, facilitates across the outer to insoluble acceptors, while OmcA exhibits specificity for certain substrates, including flavin-mediated reductions. Reduction rates vary significantly with metal solubility and environmental conditions. Soluble forms, like chelated Fe(III), are reduced faster than insoluble oxides, with MtrC and OmcA exhibiting second-order rate constants up to approximately 10^5 M^{-1} s^{-1} for Fe(III)-NTA under conditions at 7. Insoluble minerals, such as or , exhibit slower rates due to the need for direct contact, influenced by (optimal near ) and availability, where supports sustained reduction at concentrations around 20-30 mM. For U(VI), c-type including MtrC and OmcA are essential, with mutants lacking these proteins showing near-complete loss of activity. Similarly, Cr(VI) reduction is strongly impacted by OmcA and MtrC deletions, though less so for Mn(IV). These reductions often lead to , forming stable secondary phases. Fe(III) oxide reduction can produce (Fe_3O_4), a mixed-valence iron mineral, through extracellular precipitation facilitated by the Mtr pathway. U(VI) reduction yields (UO_2) nanoparticles, which aggregate into micrometer-sized particles, enhancing immobilization under lactate-oxidizing conditions. Such transformations alter metal and in natural settings.

Extracellular Electron Transfer

Shewanella oneidensis employs (EET) to respire insoluble electron acceptors outside the , enabling dissimilatory metal reduction and interactions with electrodes. This process involves both direct and indirect pathways, with the direct pathway relying on multi-heme complexes that span the outer , while the indirect pathway utilizes secreted flavins as soluble shuttles. These mechanisms allow electrons derived from intracellular metabolism to reach extracellular targets without physical contact in some cases. The primary direct EET pathway is the Mtr respiratory system, comprising the MtrCAB porin- complex. MtrC, an outer- decaheme , accepts electrons from the periplasmic MtrA and is embedded in the porin MtrB, facilitating across the outer membrane to extracellular acceptors. This complex is essential for reducing both soluble flavins and insoluble substrates, with the pathway being reversible to support both outward and inward electron flow. Indirect EET is mediated by secreted flavins, primarily riboflavin and flavin mononucleotide (FMN), which act as redox shuttles by cycling between oxidized and reduced states. These flavins, actively secreted by S. oneidensis, account for approximately 75% of electron transfer to insoluble acceptors and can bind to outer-membrane cytochromes to enhance transfer rates. Filamentous structures known as bacterial nanowires, formed as extensions of the outer membrane and periplasm enriched in cytochromes like MtrC and OmcA, further support long-distance electron conduction along micrometer scales at rates up to 10^9 electrons per second. The potentials of key components, such as certain hemes in MtrC, range from -100 to -260 mV versus the , enabling efficient under physiological conditions. Recent studies have highlighted the role of EET in oxic Fe(III) reduction, where S. oneidensis maintains reduction rates of about 0.54 µM h⁻¹ under oxic conditions, approximately sevenfold slower than anoxic rates, through persistent microscale gradients. Additionally, long-term cultivation over 320 days under competition with other bacteria sustains EET capacity, with parallel genomic adaptations enhancing metabolic efficiency and reduction.

Habitat and Ecology

Natural Environments

Shewanella oneidensis was first isolated from the sediments of , a freshwater body in , , where it was identified as a manganese-reducing bacterium thriving in anoxic conditions. This strain, designated MR-1, exemplifies the species' preference for sediment environments, and subsequent studies have confirmed its presence in similar freshwater lake and river sediments globally. Beyond freshwater systems, S. oneidensis has been detected in , estuarine, and even environments, indicating a broad distribution across aquatic and terrestrial interfaces. The species is particularly associated with anoxic zones in sediments that are rich in metals such as iron and , where it facilitates dissimilatory metal reduction. Its facultative nature allows adaptation to fluctuating oxygen levels and gradients, enabling survival in microaerobic niches like sediment aggregates or interfaces between oxic and anoxic layers. These habitats often feature organic matter decomposition and metal accumulation, providing acceptors essential for its metabolism. Detection of S. oneidensis in natural environments commonly relies on 16S rRNA gene-based molecular surveys, which have identified it in sediments from lakes, rivers, and metal-contaminated sites worldwide. For instance, suspension array techniques targeting 16S rRNA have quantified its abundance in subsurface sediments influenced by iron and sulfate reduction. These methods reveal sporadic but consistent occurrence in low-oxygen depositional areas. Ecologically, S. oneidensis contributes to biogeochemical cycles in low-oxygen sediments by mediating the reduction of metals and other electron acceptors, thereby influencing carbon, nitrogen, , and metal transformations at interfaces. Its activities promote recycling and degradation, supporting overall dynamics in stratified environments.

Microbial Interactions

Shewanella oneidensis engages in through the production and detection of extracellular , which acts as a signaling to coordinate community behaviors such as formation under conditions. Low concentrations of , typically in the nanomolar range, trigger upregulation of genes like speC (encoding ), leading to enhanced development on surfaces. This -mediated mechanism represents a novel form of distinct from traditional acyl-homoserine lactone systems, enabling S. oneidensis to sense and respond collectively to environmental cues like limitation. In mixed microbial communities, S. oneidensis participates in co-formation with other , where its signals and components facilitate structured multispecies , particularly in anaerobic environments such as sediments. For instance, co-cultures with electroactive like Geobacter species promote layered architectures that enhance overall community adhesion and stability through shared polymeric substances and pathways. S. oneidensis forms syntrophic relationships with other microbes, notably accepting electrons from Geobacter species in microbial communities to support mutual respiration. In these interactions, Geobacter oxidizes organic substrates and transfers electrons directly or via mediators to S. oneidensis, which then reduces extracellular acceptors like metals, allowing both partners to thrive in substrate-limited settings. Such syntrophy is evident in anaerobic digesters and sediment consortia, where S. oneidensis acts as an electron sink, boosting biogas production and metal reduction efficiency in co-cultures augmented with conductive materials. Competition for electron acceptors in sediments drives antagonistic interactions between S. oneidensis and co-occurring microbes, as limited availability of compounds like Fe(III) oxides favors species with efficient reduction capabilities. S. oneidensis outcompetes rivals by leveraging to access insoluble acceptors, leading to altered community dynamics and reduced growth of less versatile . Additionally, S. oneidensis produces siderophores that chelate iron, indirectly antagonizing iron-dependent competitors by sequestering this essential , though these siderophores do not directly solubilize Fe(III) for its own . This siderophore-mediated antagonism is regulated by multiple environmental signals, enhancing S. oneidensis survival in iron-scarce niches. Recent studies from 2025 highlight the role of membrane vesicles () from S. oneidensis in enhancing in mixed cultures, where containing c-type facilitate interspecies to like Paracoccus denitrificans. These vesicles attach selectively to partner cells, boosting nitrate reduction rates in co-cultures without altering S. oneidensis growth, demonstrating species-specific modulation of .

Genomics and Genetics

Genome Overview

The complete of Shewanella oneidensis MR-1 was sequenced in , consisting of a single circular of 4,969,803 and a single of 161,613 , for a total size of 5,131,416 . The harbors 4,758 predicted protein-coding genes (coding sequences, or CDSs), of which approximately 54% have assigned functions based on similarity and other evidence, while the encodes 173 CDSs, with 61% functional assignments. The overall of the is 45.9%. This structure underscores the bacterium's genetic capacity for versatile , with a notable emphasis on genes involved in environmental . A prominent feature of the is the high abundance of genes, particularly over 40 c-type , including 42 identified through of the -binding motif CXXCH, many of which contain multiple heme sites (up to 10 in decaheme variants like those in the Mtr pathway). Functional categorization reveals a strong enrichment in systems, such as the Mtr (mtrCAB), which encodes outer-membrane proteins essential for extracellular and metal reduction, alongside numerous transporters for ions like Fe³⁺, Mn⁴⁺, and CrO₄²⁻. Respiration-related genes are diverse, encompassing multiple terminal reductases, biosynthesis pathways, and components that support on various acceptors. Stress response genes are also prominent, including 88 two-component regulatory systems for sensing environmental changes like metal ions or . Comparative genomics highlights S. oneidensis MR-1's close relation to other Shewanella species, sharing a core set of approximately 2,128 genes (about 22% of the ) enriched in core metabolic and translational functions, with 92–100% 16S rRNA identity across analyzed strains. Key similarities include the near-identical mtrCAB locus for metal reduction, conserved in most Shewanella genomes examined. However, unique loci adjacent to mtrCAB vary, reflecting species-specific adaptations for metal ; for instance, S. oneidensis exhibits distinct flanking genes that enhance its broad metal-reducing capabilities compared to strains like S. amazonensis or S. frigidimarina, with average identity (ANI) values around 79% to close relatives. These differences underscore evolutionary divergence in metal reduction loci while maintaining shared respiratory infrastructure.

Genetic Engineering Advances

Genetic engineering of Shewanella oneidensis has advanced through the development of precise tools like CRISPR-Cas9 systems, enabling targeted knockouts and edits to enhance stability and functionality. An all-in-one, broad-host-range CRISPR-Cas9 vector, pBBR1-Cas9, facilitates efficient genome editing in this proteobacterium by integrating Cas9 expression with guide RNA delivery, achieving high specificity for gene inactivation. For instance, CRISPR-deaminase-mediated inactivation of the ISSod2 transposase gene has been used to stabilize the genome by preventing random insertions that cause mutations under stress, as demonstrated in 2025 studies where complete ISSod2 knockout reduced transposon activity and improved long-term strain reliability. Complementing CRISPR, transposon mutagenesis via miniHimar RB1 or similar systems generates random insertion libraries for functional genomics, identifying essential genes in processes like cytochrome c biogenesis and enabling the creation of over 39,000 mutants for high-throughput screening. Key genetic modifications focus on enhancing extracellular (EET) and metabolic capabilities. Overexpression of Mtr pathway genes, such as mtrC and mtrA, under inducible promoters like pLacI has boosted EET efficiency by increasing outer membrane cytochrome assembly, leading to up to 1.5-fold higher ferric reductase activity compared to wild-type strains. Similarly, insertion of metabolic pathways for production has been explored, including of genes from sources to redirect electrons toward synthesis during . These modifications leverage the native periplasmic electron transport network as a base for integration, minimizing metabolic burden. Recent achievements in 2025 highlight genome stabilization efforts and optimization. Targeted ISSod2 inactivation via not only curbed genomic instability but also preserved electrogenic traits under , as validated in multi-generational cultures. Concurrently, genome-scale interference (CRISPRi) libraries have allowed tailored expression of enzymes like adhesins and exopolysaccharides, enhancing formation and colonization for improved performance in microbial cells. Despite these advances, challenges persist in plasmid maintenance and transformation. Plasmid instability arises from restriction-modification systems that degrade foreign DNA, often resulting in loss of constructs after a few passages, though optimized vectors with stable replicons like repB mitigate this to some extent. Electroporation efficiency remains a bottleneck, with early methods yielding fewer than 10^5 transformants per μg DNA, necessitating refined protocols that achieve ~4 × 10^6 transformants/μg through optimized cell preparation and pulse conditions. Addressing these via host strain engineering, such as RM system knockouts, has improved overall manipulability.

Applications and Research

Bioremediation

Shewanella oneidensis plays a significant role in by reducing soluble radionuclides such as uranium(VI) (U(VI)) and technetium(VII) (Tc(VII)) to insoluble forms, thereby immobilizing them in contaminated and soils. The bacterium facilitates the of U(VI) to U(IV) through extracellular mediated by outer c-type like MtrC, resulting in the formation of (UO₂) nanoparticles that precipitate outside the cell and associate with extracellular polymeric substances for stability. This process follows Michaelis-Menten and can achieve complete of up to 1 mmol/L U(VI) within 24 hours under conditions with as an . For Tc(VII), S. oneidensis reduces it to Tc(IV) via a - and cytochrome-dependent pathway, with acting as an electron shuttle to enhance the rate at concentrations of 10 μM. In addition to radionuclides, S. oneidensis reduces toxic including (Cr(VI)) and arsenic(V) (As(V)) in and soils, converting them to less mobile and toxic species. is reduced to trivalent chromium (Cr(III)) through an inducible process involving chromate reductase enzymes, leading to as Cr(OH)₃ or adsorption onto biogenic minerals. For As(V), the bacterium promotes its transformation and immobilization, often in conjunction with reduction, which alters arsenic and in sediments. Field applications of S. oneidensis for bioremediation include biostimulation through lactate amendments in uranium-polluted aquifers to stimulate indigenous populations. Microbial consortia incorporating S. oneidensis with other metal-reducers, such as sulfate-reducing bacteria, improve overall contaminant removal by synergistically addressing multiple electron acceptors and preventing reoxidation. The primary mechanisms for immobilization involve enzymatic reduction followed by precipitation of insoluble oxides or hydroxides, as seen in UO₂ formation, which can be hindered by co-occurring manganese oxides that reoxidize U(IV) back to soluble U(VI). Recent advancements, including 2025 research on manganese ferrite (Mn₀.₂Fe₂.₈O₄) nanoparticles, show they protect S. oneidensis from Cr(VI) toxicity by adsorbing 61% of Cr(VI) (16.8 mg/g) and facilitating a 2.1-fold increase in reduction efficiency compared to bacteria alone, while boosting cell viability 3.3-fold through physical shielding and enhanced electron transfer. Despite these capabilities, limitations in scalability arise from challenges in maintaining S. oneidensis survival , where high contaminant concentrations inhibit growth and activity, as evidenced by reduced reduction rates under toxic Cr(VI) levels exceeding 100 μM. Adaptive strategies have improved , but field-scale deployment remains constrained by delivery and competition with native microbes.

Energy and Nanotechnology

Shewanella oneidensis has been extensively studied for its role in microbial fuel cells (MFCs), where it colonizes to generate electricity from organic waste substrates such as or effluents. In these systems, the bacterium facilitates extracellular (EET) to , enabling the conversion of into electrical power without the need for external mediators in some configurations. Typical power densities achieved with S. oneidensis in MFCs range from 0.1 to 2 W/m², depending on electrode materials and operational conditions, with optimized setups reaching up to 2.63 W/m² through to enhance flavin production. These densities highlight S. oneidensis's potential for scalable from low-value organics, though challenges like stability limit long-term performance. Beyond electricity generation, S. oneidensis contributes to through the of metal nanoparticles via enzymatic reduction of metal ions. The bacterium reduces precursors like and Ag⁺ extracellularly, yielding stable and silver nanoparticles (typically 5-50 in size) with properties superior to chemically synthesized counterparts. This green synthesis leverages the pathway for donation, producing nanoparticles suitable for biomedical applications such as wound dressings. Additionally, under electron-acceptor limitation, S. oneidensis assembles conductive bacterial nanowires—pilus-like extensions rich in multi-heme —that exhibit metallic-like along micrometer scales, with transport rates up to 10⁹ s⁻¹ at 100 mV. These nanowires serve as natural conductive materials for bioelectronic interfaces. Hybrid systems integrating S. oneidensis with electrodes have advanced bio-battery development, where the bacterium acts as a living in rechargeable setups. In these biohybrids, S. oneidensis interfaces with carbon-based electrodes to store and release energy, achieving discharge capacities comparable to enzymatic batteries while offering self-regeneration. Recent 2025 advancements focus on enhancing long-term EET stability through material coatings, enabling sustained performance in flow-cell configurations with minimal loss. In , S. oneidensis's enable self-assembling structures for applications. Outer like OmcA self-organize on electrode surfaces or s, forming redox-active layers that detect environmental analytes such as with high sensitivity (limits down to levels). These bioassembled films, often integrated into liposome-gold hybrids, facilitate real-time monitoring of events, paving the way for portable biosensors in energy and environmental tech.

Emerging Research Directions

Recent advancements in Shewanella oneidensis research have positioned it as a versatile chassis for applications, particularly through for bioelectrosynthesis. Engineered strains of S. oneidensis MR-1 have been developed using dual-plasmid systems to overexpress the reductive pathway for assimilation from CO₂ and an alternative malate biosynthetic pathway, enabling direct conversion of CO₂ to the C₄ compound malate. This proof-of-concept achieved a malate production of 1.18 mmol·L⁻¹, demonstrating the bacterium's potential for sustainable CO₂ valorization in microbial systems. Proteomic analyses of S. oneidensis exudates have revealed significant perturbations in response to metal exposure, highlighting adaptive mechanisms for environmental stress. In the presence of Se(IV), identified 955 exuded proteins, with 144 showing differential expression (54 up-regulated and 90 down-regulated, ≥ 2, BH-adjusted p < 0.05), including up-regulation of redox-active proteins like AhpF and Sye4 bearing sulfhydryl sites that facilitate Se(IV) . Additionally, from S. oneidensis MR-1 play a key role in modulating processes, enhancing growth rates and consumption in select denitrifying species such as (growth rate increased from 0.32 to 0.46 h⁻¹, p = 6.0 × 10⁻⁷; consumption from 23.8 to 57.6 mM, p = 3.9 × 10⁻²) via c-type without altering gene transcription. Long-term cultivation experiments underscore the robustness of S. oneidensis MR-1's extracellular (EET) capabilities under competitive conditions. In a 320-day coculture with An1 and , S. oneidensis maintained EET and ferrihydrite reduction, achieving relative abundances up to 30.94% ± 0.74% while exhibiting parallel genomic evolution in genes related to , ATP synthesis, and . Under oxic conditions, S. oneidensis MR-1 sustains ferrihydrite reduction at cell-specific rates of 2.6 × 10⁻¹⁰ ± 0.5 × 10⁻¹⁰ µM h⁻¹ ⁻¹, approximately 120 times slower than anoxic rates (3.2 × 10⁻⁸ ± 1.6 × 10⁻⁸ µM h⁻¹ ⁻¹), yet contributing to persistent Fe(II) mobilization (0.54 ± 0.089 µM h⁻¹) in sediments. These developments suggest S. oneidensis's emerging role in by enhancing carbon cycling through bioelectrosynthetic CO₂ fixation and iron-mediated organic carbon stabilization in soils and sediments.

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