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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Microbiol.</journal-id>
<journal-title-group>
<journal-title>Frontiers in Microbiology</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Microbiol.</abbrev-journal-title>
</journal-title-group>
<issn pub-type="epub">1664-302X</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
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<article-meta>
<article-id pub-id-type="doi">10.3389/fmicb.2026.1737712</article-id>
<article-version article-version-type="Version of Record" vocab="NISO-RP-8-2008"/>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Original Research</subject>
</subj-group>
</article-categories>
<title-group>
<article-title>Genome-wide analysis of extended-spectrum beta-lactamase-producing <italic>Escherichia coli</italic> from seafood in Bangladesh: population structure, resistome, virulome, and global dissemination patterns</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author"><name><surname>Fahim</surname> <given-names>Naeem Ahammed Ibrahim</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
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<contrib contrib-type="author"><name><surname>Sarwer</surname> <given-names>Afsan</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
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<contrib contrib-type="author"><name><surname>Firdous</surname> <given-names>Zannatul</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
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<contrib contrib-type="author"><name><surname>Rana</surname> <given-names>Md. Liton</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref><xref ref-type="aff" rid="aff2"><sup>2</sup></xref><xref ref-type="aff" rid="aff3"><sup>3</sup></xref>
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<contrib contrib-type="author"><name><surname>Islam</surname> <given-names>Md. Saiful</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref><xref ref-type="aff" rid="aff4"><sup>4</sup></xref>
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<contrib contrib-type="author"><name><surname>Rahman</surname> <given-names>Saifur</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref><xref ref-type="aff" rid="aff5"><sup>5</sup></xref>
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<contrib contrib-type="author"><name><surname>Pondit</surname> <given-names>Amrita</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref><xref ref-type="aff" rid="aff5"><sup>5</sup></xref>
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<contrib contrib-type="author"><name><surname>Hassan</surname> <given-names>Jayedul</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
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<contrib contrib-type="author"><name><surname>Walsh</surname> <given-names>Timothy R.</given-names></name><xref ref-type="aff" rid="aff5"><sup>5</sup></xref>
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<contrib contrib-type="author" corresp="yes"><name><surname>Farzana</surname> <given-names>Refath</given-names></name><xref ref-type="aff" rid="aff5"><sup>5</sup></xref><xref ref-type="corresp" rid="c001"><sup>&#x002A;</sup></xref>
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<aff id="aff1"><label>1</label><institution>Department of Microbiology and Hygiene, Faculty of Veterinary Science, Bangladesh Agricultural University</institution>, <city>Mymensingh</city>, <country country="bd">Bangladesh</country></aff>
<aff id="aff2"><label>2</label><institution>National Engineering Research Center of Industrial Wastewater Detoxication and Resource Recovery, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences</institution>, <city>Beijing</city>, <country country="cn">China</country></aff>
<aff id="aff3"><label>3</label><institution>University of Chinese Academy of Sciences</institution>, <city>Beijing</city>, <country country="cn">China</country></aff>
<aff id="aff4"><label>4</label><institution>Department of Animal Science, University of California, Davis</institution>, <city>Davis</city>, <state>CA</state>, <country country="us">United States</country></aff>
<aff id="aff5"><label>5</label><institution>Department of Biology, Ineos Oxford Institute for Antimicrobial Resistance, University of Oxford</institution>, <city>Oxford</city>, <country country="gb">United Kingdom</country></aff>
<author-notes>
<corresp id="c001"><label>&#x002A;</label>Correspondence: Refath Farzana, <email xlink:href="mailto:refath.farzana@biology.ox.ac.uk">refath.farzana@biology.ox.ac.uk</email>; Md. Tanvir Rahman, <email xlink:href="mailto:tanvirahman@bau.edu.bd">tanvirahman@bau.edu.bd</email></corresp>
</author-notes>
<pub-date publication-format="electronic" date-type="pub" iso-8601-date="2026-02-06">
<day>06</day>
<month>02</month>
<year>2026</year>
</pub-date>
<pub-date publication-format="electronic" date-type="collection">
<year>2026</year>
</pub-date>
<volume>17</volume>
<elocation-id>1737712</elocation-id>
<history>
<date date-type="received">
<day>02</day>
<month>11</month>
<year>2025</year>
</date>
<date date-type="rev-recd">
<day>12</day>
<month>12</month>
<year>2025</year>
</date>
<date date-type="accepted">
<day>22</day>
<month>01</month>
<year>2026</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#x00A9; 2026 Fahim, Sarwer, Firdous, Rana, Islam, Rahman, Pondit, Hassan, Walsh, Farzana and Rahman.</copyright-statement>
<copyright-year>2026</copyright-year>
<copyright-holder>Fahim, Sarwer, Firdous, Rana, Islam, Rahman, Pondit, Hassan, Walsh, Farzana and Rahman</copyright-holder>
<license>
<ali:license_ref start_date="2026-02-06">https://creativecommons.org/licenses/by/4.0/</ali:license_ref>
<license-p>This is an open-access article distributed under the terms of the <ext-link ext-link-type="uri" xlink:href="https://creativecommons.org/licenses/by/4.0/">Creative Commons Attribution License (CC BY)</ext-link>. The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.</license-p>
</license>
</permissions>
<abstract>
<sec>
<title>Objectives</title>
<p>This study aimed to identify multilocus sequence type (MLST), serotype, average nucleotide identity (ANI), antimicrobial resistance genes (ARGs), virulence genes (VGs), and mobile genetic elements (MGEs) from whole-genome sequences of 10 <italic>Escherichia coli</italic> isolated from seafood in Bangladesh and compared them with the global datasets of beta-lactamase-producing <italic>E. coli</italic>.</p>
</sec>
<sec>
<title>Methods</title>
<p>Ten <italic>E. coli</italic> isolates (crab&#x202F;=&#x202F;3, shrimp&#x202F;=&#x202F;1, tuna&#x202F;=&#x202F;6) were subjected to whole-genome sequencing using Oxford Nanopore Technologies (Oxford, UK). In-silico bioinformatics analyses were performed using online tools and Linux-based commands. A systematic advanced search in PubMed identified 722 global genomes of beta-lactamase-producing <italic>E. coli</italic> for comparative analysis. A population structure and global phylogeny were constructed to illustrate the current status of beta-lactamase-producing <italic>E. coli</italic> from diverse sources (seafood, human, aquatic, wastewater, and environmental) across countries, based on their STs, ARGs, VGs, MGEs, and serotypes.</p>
</sec>
<sec>
<title>Results</title>
<p>Bioinformatics analysis revealed that most isolates displayed unique sequence types (STs) and core genome sequence types (cgSTs), while three isolates shared both ST1431 and cgST104784, indicating close genetic relatedness supported by ANI analysis. In shrimp and tuna isolates, both O and H antigens were detected, whereas crab isolates carried either O or H antigens. Pangenome analysis identified 56.4% strain-specific genes, 34.2% dispensable genes, and 9.4% core genes, with functions categorized into clusters of orthologous groups (COGs). Several ARGs, including beta-lactamase genes (<italic>CTX-M-15, AmpC, bla</italic><sub>DHA-1</sub>), were detected across isolates, with crabs harboring the highest number. The VGs were more common in tuna isolates. Plasmids were only detected in crabs (Col440I, IncFIA, IncFIB(pHCM2), and ColRNAI) carrying <italic>qnrB4</italic>, <italic>dfrA17</italic>, <italic>qacE</italic>, <italic>mph(A)</italic>, <italic>sul1</italic>, <italic>bla</italic><sub>DHA-1</sub> ARGs, but were absent in shrimp and tuna. Population structure analysis showed that ST345 in Bangladesh closely matched wastewater (Czech Republic) and human (USA) isolates. Some STs overlapped with international records, while others appeared novel, suggesting limited global distribution. Globally, wastewater and human isolates from the Czech Republic showed the greatest similarity to our strains.</p>
</sec>
<sec>
<title>Conclusion</title>
<p>These findings underscore the potential role of seafood in disseminating beta-lactamase-producing <italic>E. coli</italic>, highlighting the urgent need for integrated surveillance to mitigate antimicrobial resistance risks in humans, animals, and the food chain.</p>
</sec>
</abstract>
<kwd-group>
<kwd>beta-lactamase</kwd>
<kwd>
<italic>Escherichia coli</italic>
</kwd>
<kwd>global-phylogeny</kwd>
<kwd>seafood</kwd>
<kwd>whole-genome-sequencing</kwd>
<kwd>antimicrobial resistance</kwd>
<kwd>one health</kwd>
<kwd>virulence</kwd>
</kwd-group>
<funding-group>
<funding-statement>The author(s) declared that financial support was received for this work and/or its publication. This study was supported by the Bangladesh Agricultural University Research System (BAURES) under grant number 2022/12/BAU. Whole genome sequencing support was provided by Ineos Oxford Institute for Antimicrobial Research.</funding-statement>
</funding-group>
<counts>
<fig-count count="5"/>
<table-count count="0"/>
<equation-count count="0"/>
<ref-count count="67"/>
<page-count count="14"/>
<word-count count="10046"/>
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<custom-meta-group>
<custom-meta>
<meta-name>section-at-acceptance</meta-name>
<meta-value>Antimicrobials, Resistance and Chemotherapy</meta-value>
</custom-meta>
</custom-meta-group>
</article-meta>
</front>
<body>
<sec sec-type="intro" id="sec1">
<label>1</label>
<title>Introduction</title>
<p>Seafood is widely consumed worldwide due to its unique sensory attributes and high nutritional value, particularly its richness in protein, minerals, and omega-3 fatty acids. Global seafood consumption has more than doubled in the past five decades, fueled by population growth, urbanization, and changes in dietary preferences (<xref ref-type="bibr" rid="ref23">Guillen et al., 2019</xref>). However, seafood quality is influenced by multiple factors, including freshness, geographic origin, and post-harvest practices (<xref ref-type="bibr" rid="ref18">Ejeta et al., 2024</xref>). Among foodborne commodities, seafood is particularly vulnerable to microbial contamination because of its direct contact with aquatic ecosystems that may receive untreated waste and industrial effluents. Additionally, inadequate handling, improper storage, and unhygienic processing further increase the risk of contamination of seafood (<xref ref-type="bibr" rid="ref13">Chintagari et al., 2017</xref>). As a result, seafood can act as a reservoir and transmission vehicle for pathogenic microorganisms and antimicrobial-resistant bacteria, raising concerns for food safety, public health, and international trade (<xref ref-type="bibr" rid="ref48">Parlapani et al., 2023</xref>).</p>
<p>Among seafood-borne pathogens, <italic>Escherichia coli</italic> is of special importance. While many strains are commensal inhabitants of the intestinal tracts of humans and animals, pathogenic variants of <italic>E. coli</italic> are capable of causing a wide range of illnesses, including gastroenteritis, urinary tract infections, and septicemia (<xref ref-type="bibr" rid="ref53">Ramos et al., 2020</xref>). Its occurrence has been associated with multiple contamination routes, including the discharge of untreated human or animal waste into water bodies, the use of contaminated ice for storage, unhygienic handling during processing, and cross-contamination within distribution and retail environments (<xref ref-type="bibr" rid="ref15">Costa, 2013</xref>). Consuming raw or undercooked seafood contaminated with <italic>E. coli</italic> can lead to outbreaks of foodborne illness, which may manifest as abdominal cramps, bloody or watery diarrhea, fever, nausea, and vomiting (<xref ref-type="bibr" rid="ref28">Jnani and Ray, 2023</xref>). Previous studies have reported <italic>E. coli</italic> in shrimp (<xref ref-type="bibr" rid="ref25">Immaculate et al., 2012</xref>; <xref ref-type="bibr" rid="ref42">Loest et al., 2022</xref>; <xref ref-type="bibr" rid="ref60">Teophilo et al., 2002</xref>), crabs (<xref ref-type="bibr" rid="ref45">Matulkova et al., 2013</xref>) and tuna fish (<xref ref-type="bibr" rid="ref47">Natalia et al., 2022</xref>; <xref ref-type="bibr" rid="ref55">Sahami and Nursinar, 2019</xref>), underscoring its widespread distribution in seafood species of global commercial importance.</p>
<p>Beyond pathogenicity, seafood-associated <italic>E. coli</italic> may serve as reservoirs of antimicrobial resistance genes (ARGs) that can be horizontally transferred within the bacterial population. Horizontal gene transfer through mobile genetic elements (MGEs), such as plasmids, integrons, and transposons, facilitates the spread of resistance traits across diverse bacterial populations, thereby compounding the public health threat (<xref ref-type="bibr" rid="ref10">Casta&#x00F1;eda-Barba et al., 2023</xref>). Of particular concern is resistance to <italic>&#x03B2;</italic>-lactam antibiotics, largely mediated by extended-spectrum &#x03B2;-lactamases (ESBLs) (<xref ref-type="bibr" rid="ref5">Bajaj et al., 2016</xref>). ESBL-producing <italic>E. coli</italic> compromises the efficacy of critically important antimicrobials and is frequently co-associated with resistance to non-&#x03B2;-lactam classes. Among the ESBL family, CTX-M-type ESBLs are globally prevalent and clinically significant worldwide. The detection of such resistance determinants in seafood is particularly alarming because it suggests the potential for transfer of resistance along the food chain, thereby bridging aquatic, animal, and human health domains.</p>
<p>Bangladesh is one of the world&#x2019;s largest exporters of seafood (<xref ref-type="bibr" rid="ref56">Sheikh et al., 2018</xref>), making it essential to monitor bacterial contamination and AMR and to safeguard public health and international trade. To date, no comprehensive genomic study has evaluated ESBL-producing <italic>E. coli</italic> in seafood in Bangladesh. Therefore, this study aimed to characterize the genomic features, antimicrobial resistance genes (ARGs), virulence genes (VGs), and mobile genetic elements (MGEs) of <italic>E. coli</italic> isolates obtained from shrimp, crab, and tuna, and to compare them with global datasets of ESBL-producing <italic>E. coli</italic> from humans, animals, and the environment. These findings will provide valuable insights into the population structure and global context of seafood-associated <italic>E. coli</italic> in Bangladesh.</p>
</sec>
<sec sec-type="materials|methods" id="sec2">
<label>2</label>
<title>Materials and methods</title>
<sec id="sec3">
<label>2.1</label>
<title>Ethical statement</title>
<p>All research methods were authorized by the Bangladesh Agricultural University (BAU) Animal Welfare and Ethics Committee in Mymensingh, Bangladesh [Approval Number: AWEEC/BAU/2023(25)]. Prior to sampling, informed permission was obtained from the vendors who sold fish in the local market.</p>
</sec>
<sec id="sec4">
<label>2.2</label>
<title>Isolate selection and DNA extraction</title>
<p>In our previously published study (<xref ref-type="bibr" rid="ref21">Firdous et al., 2025</xref>), we screened 102 raw seafood samples to detect extended-spectrum <italic>&#x03B2;</italic>-lactamase-producing <italic>E. coli</italic> (ESBL-EC), identifying ESBL-EC in 18.6% of isolates, with 69.8% exhibiting multidrug resistance and high resistance to ampicillin (100%), cefotaxime (37.2%), and ceftazidime (95.3%). The <italic>E. coli</italic> strains used in the present study (<italic>n</italic>&#x202F;=&#x202F;8) were obtained from that first-cohort sampling, which focused on the detection of extended-spectrum &#x03B2;-lactamase-producing isolates resistant to ampicillin, cefotaxime, and ceftazidime, where preliminary characterization, including isolation and purification, species-level identification, and other microbiological analyses, had been completed. Additionally, two new strains (<italic>n</italic>&#x202F;=&#x202F;2) were collected from a second-cohort sampling (unpublished) following the same methodological procedures and selection criteria as in our previous study. The <italic>E. coli</italic> isolates recovered from seafood were designated according to their source: MTR_EC02, MTR_EC03, and MTR_EC05 from crab; MTR_ES01 from shrimp; and MTR_ET01, MTR_ET06, MTR_ET08, MTR_ET09, MTR_ET11, and MTR_ET12 from tuna.</p>
</sec>
<sec id="sec5">
<label>2.3</label>
<title>Whole genome sequencing and genome assembly</title>
<sec id="sec6">
<label>2.3.1</label>
<title>Genome extraction</title>
<p>Genomic DNA was extracted from an overnight culture using the QIAcube (Qiagen, Hilden, Germany), and the resulting gDNA was quantified using the Qubit 3.0 (Thermo Fisher Scientific, Waltham, United States). Long-read sequencing was performed on the PromethION platform (Oxford Nanopore Technologies, Oxford, United Kingdom).</p>
</sec>
<sec id="sec7">
<label>2.3.2</label>
<title>Library prep, and sequencing</title>
<p>Genomic libraries were prepared using Rapid Barcoding Kit 96 V14Q20+ Kit14 (SQK-RBK114.96) according to the manufacturer&#x2019;s instructions. The R10.4.1 flow cell (FLO-PRO114M) was inserted into the PromethION 2 Solo device, and barcoded DNA was loaded onto the flow cell. PromethION 2 Solo was connected to the MinKNOW Software (24.02.8) to generate the raw reads in pod5 format.</p>
</sec>
<sec id="sec8">
<label>2.3.3</label>
<title>Reads QC and genome assembly</title>
<p>Raw reads in pod5 format were processed utilizing the pod5 subset tool, specifically designed for partitioning pod5 files into multiple output files. Duplex basecalling was conducted with the Dorado basecaller (0.7.2), resulting in raw reads converted to fastq format, employing super accurate model, dna_r10.4.1_e8.2_400bps_sup@v4.2.0 model. Subsequently, the reads were assembled into contigs using Flye (2.9.4), followed by assembly polishing performed with Medaka (1.12.0).</p>
</sec>
<sec id="sec9">
<label>2.3.4</label>
<title>Bioinformatic analyses</title>
<p>The bioinformatic analyses related to genome assembly were carried out at the Advanced Research Computing (ARC) cluster, University of Oxford [arc (CPU: 48 core Cascade Lake (Intel Xeon Platinum 8,268 CPU @ 2.90GHz) Memory: 392GB) and htc (CPUs: mix of Broadwell, Haswell, Cacade Lake GPU: P100, V100, A100, RTX)].<xref ref-type="fn" rid="fn0001"><sup>1</sup></xref> The sequencing data generated in this study have been deposited in the NCBI database under BioSample accessions SAMN52392760&#x2013;SAMN52392769.</p>
</sec>
</sec>
<sec id="sec10">
<label>2.4</label>
<title>Population structure and global phylogeny</title>
<p>This study aims to provide a comprehensive analysis of ESBL-producing <italic>E. coli</italic> strains isolated from various sources, including human subjects, seafood, environmental samples, aquatic environments, and wastewater. To achieve this, the population structure and global phylogeny were performed to understand strain-relatedness, evolutionary history, and transmission patterns of seafood-derived <italic>E. coli</italic> in relation to global strains from diverse sources across various geographical locations. A systematic literature search was conducted on PubMed using the advanced search option on June 9, 2025. A total of 722 strains were selected based on different criteria, including title, full text availability, and availability of assembled genomes, using two queries, as the initial query yielded limited isolates from seafood (<xref ref-type="supplementary-material" rid="SM5">Supplementary Table S1E</xref>). In the first query, ((&#x201C;<italic>CTX-M-15</italic>&#x201D;[Title/Abstract] OR &#x201C;<italic>AmpC</italic>&#x201D;[Title/Abstract] OR &#x201C;<italic>blaDHA</italic>-<italic>1</italic>&#x201D;[Title/Abstract]) AND (&#x201C;<italic>E. coli</italic>&#x201D;[Title/Abstract] OR &#x201C;<italic>E. coli</italic>&#x201D;[Title/Abstract]) AND (&#x201C;genome&#x201D;[Title/Abstract] OR &#x201C;WGS&#x201D;[Title/Abstract] OR &#x201C;genomic&#x201D;[Title/Abstract] OR &#x201C;whole genome sequencing&#x201D;[Title/Abstract] OR &#x201C;next-generation sequencing&#x201D;[Title/Abstract] OR &#x201C;Illumina&#x201D;[Title/Abstract] OR &#x201C;MinION&#x201D;[Title/Abstract] OR &#x201C;PacBio&#x201D;[Title/Abstract]) AND (&#x201C;cefotaxime&#x201D;[Title/Abstract] OR &#x201C;ESBL&#x201D;[Title/Abstract] OR &#x201C;extended-spectrum beta-lactamase&#x201D;[Title/Abstract]) AND (&#x201C;human&#x201D;[Title/Abstract] OR &#x201C;fish&#x201D;[Title/Abstract] OR &#x201C;fish gut&#x201D;[Title/Abstract] OR &#x201C;fish origin&#x201D;[Title/Abstract] OR &#x201C;aquatic environment&#x201D;[Title/Abstract] OR &#x201C;aquaculture&#x201D;[Title/Abstract] OR &#x201C;environment&#x201D;[Title/Abstract] OR &#x201C;environmental water&#x201D;[Title/Abstract] OR &#x201C;environmental isolates&#x201D;[Title/Abstract])) (<xref ref-type="supplementary-material" rid="SM5">Supplementary Table S1A</xref>), and all the matadata was presented in <xref ref-type="supplementary-material" rid="SM5">Supplementary Table S1B</xref>.</p>
<p>While the second query was (&#x201C;<italic>E. coli</italic>&#x201D;[Title/Abstract] OR &#x201C;<italic>E. coli</italic>&#x201D;[Title/Abstract]) AND (&#x201C;genome&#x201D;[Title/Abstract] OR &#x201C;WGS&#x201D;[Title/Abstract] OR &#x201C;genomic&#x201D;[Title/Abstract] OR &#x201C;whole genome sequencing&#x201D;[Title/Abstract] OR &#x201C;next-generation sequencing&#x201D;[Title/Abstract] OR &#x201C;Illumina&#x201D;[Title/Abstract] OR &#x201C;MinION&#x201D;[Title/Abstract] OR &#x201C;PacBio&#x201D;[Title/Abstract]) AND (&#x201C;shrimp&#x201D;[Title/Abstract] OR &#x201C;<italic>Penaeus vannamei</italic>&#x201D;[Title/Abstract] OR &#x201C;<italic>Litopenaeus vannamei</italic>&#x201D;[Title/Abstract] OR &#x201C;<italic>Penaeus monodon</italic>&#x201D;[Title/Abstract] OR &#x201C;crab&#x201D;[Title/Abstract] OR &#x201C;<italic>Scylla serrata</italic>&#x201D;[Title/Abstract] OR &#x201C;<italic>Callinectes sapidus</italic>&#x201D;[Title/Abstract] OR &#x201C;Portunus trituberculatus&#x201D;[Title/Abstract] OR &#x201C;tuna&#x201D;[Title/Abstract] OR &#x201C;<italic>Thunnus albacares</italic>&#x201D;[Title/Abstract] OR &#x201C;<italic>Thunnus obesus</italic>&#x201D;[Title/Abstract] OR &#x201C;<italic>Thunnus thynnus</italic>&#x201D;[Title/Abstract]) (<xref ref-type="supplementary-material" rid="SM5">Supplementary Table S1C</xref>) and all the metadata was presented in <xref ref-type="supplementary-material" rid="SM5">Supplementary Table S1D</xref>. These two searches yielded a total of 30 publications from which 722 assembled genomes were downloaded from the National Center for Biotechnology Information (NCBI).</p>
<p>For global phylogeny, a total of 722 assembled genomes (<xref ref-type="supplementary-material" rid="SM5">Supplementary Table S1</xref>), one reference genome from NCBI (<italic>E. coli</italic> str. K-12 substr. MG1655), and selected 10 <italic>E. coli</italic> isolates from this study, were used to build the phylogenetic tree using Parsnp 2.0.in the Linux command, a tool designed for core genome alignment and single-nucleotide polymorphism (SNP) detection (<xref ref-type="bibr" rid="ref34">Kille et al., 2024</xref>). However, nine genomes were excluded by the parsnp due to being much larger or shorter than the reference genome. The phylogenetic tree built based on core genome alignment of the 724 strains was then visualized using Interactive Tree of Life (iTOL v6) (<xref ref-type="bibr" rid="ref37">Letunic and Bork, 2024</xref>). Minimal spanning trees were built on 723 genomes to show their distribution and core genomic relationships based on the housekeeping genes and 7-loci MLST profile (<xref ref-type="supplementary-material" rid="SM6">Supplementary Table S2</xref>) (<xref ref-type="bibr" rid="ref31">Jolley et al., 2018</xref>)<xref ref-type="fn" rid="fn0002"><sup>2</sup></xref>, using the Grapetree tool in a Linux environment (<xref ref-type="bibr" rid="ref67">Zhou et al., 2018</xref>).</p>
</sec>
<sec id="sec11">
<label>2.5</label>
<title>Pangenome analysis</title>
<p>To investigate the genetic diversity among the selected <italic>E. coli</italic> genomes, a pangenome analysis was performed using PanExplorer (<xref ref-type="bibr" rid="ref17">Dereeper et al., 2022</xref>). PanAcoTA, with a minimum percentage identity of 80% was employed (<xref ref-type="bibr" rid="ref50">Perrin and Rocha, 2021</xref>). This analysis generated comparative results among the genomes and provided data and figures on core, accessory, and unique genes based on the presence or absence of genes across all genomes and their corresponding functional categories.</p>
</sec>
<sec id="sec12">
<label>2.6</label>
<title>Genomic annotation and downstream analysis</title>
<p>Basic genomic features and elements were identified using Prokka and annotated using Bakta in the Proksee platform (<xref ref-type="bibr" rid="ref22">Grant et al., 2023</xref>). The multilocus sequence typing (MLSTs)<xref ref-type="fn" rid="fn0003"><sup>3</sup></xref> (<xref ref-type="bibr" rid="ref36">Larsen et al., 2012</xref>), and cgST<xref ref-type="fn" rid="fn0004"><sup>4</sup></xref> (<xref ref-type="bibr" rid="ref32">Jolley and Maiden, 2010</xref>; <xref ref-type="bibr" rid="ref14">Clausen et al., 2018</xref>) were determined using the Center for Genomic Epidemiology platform.<xref ref-type="fn" rid="fn0005"><sup>5</sup></xref></p>
<p>Average nucleotide identity (ANI) values were determined by using the integrated prokaryotic genome and pan-genome analysis (IPGA) web service platform (<xref ref-type="bibr" rid="ref41">Liu et al., 2022</xref>). The circular genomes were visualized and compared using the BLAST Ring Image Generator (BRIG) (<xref ref-type="bibr" rid="ref4">Alikhan et al., 2011</xref>).</p>
<p>To detect ARGs, several platforms were used, including the Comprehensive Antibiotic Resistance Database (CARD) and CARD resistance gene identifier in proksee (<xref ref-type="bibr" rid="ref2">Alcock et al., 2023</xref>), CARD in abricate<xref ref-type="fn" rid="fn0006"><sup>6</sup></xref>, and ResFinder (<xref ref-type="bibr" rid="ref65">Zankari et al., 2012</xref>). The datasets of the Virulence Factors of Pathogenic Bacteria Database (VFDB) and VFDB from abricate (see footonote 6) were used to identify virulence factors (<xref ref-type="bibr" rid="ref12">Chen et al., 2005</xref>). After each result from these analyses, the results were merged, and missing genes were added from different platforms to produce a comprehensive report. The Mobile Element Finder<xref ref-type="fn" rid="fn0008"><sup>8</sup></xref> on the CGE and the mobileOG-db of Proksee<xref ref-type="fn" rid="fn0009"><sup>9</sup></xref> were used to identify mobile elements, plasmids, and their associated AMR and virulence genes (VGs) (<xref ref-type="bibr" rid="ref30">Johansson et al., 2021</xref>; <xref ref-type="bibr" rid="ref8">Brown et al., 2022</xref>). <italic>E. coli</italic> serotyping was done using Ectyper<xref ref-type="fn" rid="fn0010"><sup>10</sup></xref> (<xref ref-type="bibr" rid="ref7">Bessonov et al., 2021</xref>) and seroTypeFinder<xref ref-type="fn" rid="fn0011"><sup>11</sup></xref> (<xref ref-type="bibr" rid="ref29">Joensen et al., 2015</xref>).</p>
</sec>
</sec>
<sec sec-type="results" id="sec13">
<label>3</label>
<title>Result</title>
<sec id="sec14">
<label>3.1</label>
<title>Basic genomic features, MLST, cgMLST, serotype, and average nucleotide identity (ANI)</title>
<p>The genomic features of all 10 genomes were presented in the <xref ref-type="supplementary-material" rid="SM7">Supplementary Table S3A</xref>, with assembled chromosomes (<xref ref-type="fig" rid="fig1">Figure 1A</xref>), comprising a total of 4,641,652 bp. Genome sizes ranged from 4,048,090 to 4,961,915, while GC contents varied between 50.5% and 50.89%. While most isolates exhibited unique MLST and cgST profiles (<xref ref-type="supplementary-material" rid="SM7">Supplementary Table S3B</xref>), three isolates (MTR_ET06, MTR_ET08, and MTR_ET11) belonged to ST1431 and cgST104784. Isolates MTR_ES05 and MTR_ET09 were assigned to ST10 and a variant ST10&#x002A;, respectively, but each had distinct cgSTs (27,089 and 23,638, respectively). Serotype profile of the <italic>E. coli</italic> isolates showed variations among seafood sources: isolates recovered from shrimp and tuna fish possessed both O and H antigens, while crab exhibited only a single antigen type, either O or H alone.</p>
<fig position="float" id="fig1">
<label>Figure 1</label>
<caption>
<p>Genomic characteristics of <italic>E. coli</italic> isolates. <bold>(A)</bold> Circular genomes of the 10 isolates of <italic>E. coli</italic> from seafood. <bold>(B)</bold> ANI analysis of <italic>E. coli</italic> isolates. The color indicates the value of ANI; the value range is 96%&#x2013;100%, with the color turning from blue to red. The numbers 0&#x2013;3 refer to relative branch distance levels within the hierarchical clustering. Solid lines indicate major cluster separation, whereas dotted lines mark sub-cluster boundaries.</p>
</caption>
<graphic xlink:href="fmicb-17-1737712-g001.tif" mimetype="image" mime-subtype="tiff">
<alt-text content-type="machine-generated">Circular genome map of E. coli isolates (seafood-Bangladesh) with different colored tracks indicating various strains labeled MTR_EC02 to MTR_ET12. A heatmap displays genetic relationships between these strains, with a color gradient from blue to red. A dendrogram below shows the hierarchical clustering of strains, also using the same color gradient.</alt-text>
</graphic>
</fig>
<p>ANI values were calculated to assess the pair-wise nucleotide-level similarity among <italic>E. coli</italic> strains, ranging from 96 to 100% (<xref ref-type="fig" rid="fig1">Figure 1B</xref>). The resulting dendrogram revealed three distinct phylogenetic clades: the first clade exclusively contained tuna-derived isolates (MTR_ET11, MTR_ET06, MTR_ET08, MTR_ET12, and MTR_ET01); the second clade comprised isolates from multiple seafood sources, including tuna, shrimp, and crab (MTR_ET09, MTR_ES05, MTR_EC02, and MTR_EC03); and the third clade consisted solely of MTR_EC05, a crab isolate that formed a distinct, independent lineage.</p>
</sec>
<sec id="sec15">
<label>3.2</label>
<title>Pangenomic analysis</title>
<p>In the pangenome analysis, the highest percentage of genes was strain-specific (56.4%), while core genes comprised 9.4% and dispensable genes 34.2% (<xref ref-type="supplementary-material" rid="SM1">Supplementary Figure S1</xref> and <xref ref-type="supplementary-material" rid="SM8">Supplementary Tables S4A&#x2013;C</xref>). The highest number of strain-specific genes was found in genomes of <italic>E. coli</italic> isolates in carbs, with MTR_EC05 (4246), MTR_EC05 (1484), and MTR_EC03 (244). In the isolates from shrimp, 200 specific genes were identified in MTR_ES05. Among <italic>E. coli</italic> from tuna, the highest number of core genes was found in MTR_ET01 (207), followed by MTR_ET12 (200), MTR_ET11 (109), MTR_ET09 (<xref ref-type="bibr" rid="ref6">Balistreri et al., 2025</xref>), MTR_ET06 (3), and MTR_ET08 (2). However, we found partial sequence homology in core genes that were shared among 10 isolates (<xref ref-type="supplementary-material" rid="SM2">Supplementary Figure S2</xref> and <xref ref-type="supplementary-material" rid="SM8">Supplementary Table S4D</xref>). According to the presence-absence genes matrix, MTR_ET12 and MTR_ET01, MTR_ET08 and MTR_ET06, and MTR_ET09 and MTR_ES05 were highly correlated. Due to the high number of genes in MTR_EC05, a separate denogram was generated, which differed significantly from those of other isolates (<xref ref-type="supplementary-material" rid="SM3">Supplementary Figure S3</xref> and <xref ref-type="supplementary-material" rid="SM8">Supplementary Table S4E</xref>).</p>
<p>In the functional categories of Clusters of Orthologous Groups (COG), the highest number of genes was involved in metabolism, followed by poorly characterized cellular processes, signaling, and information storage and processing. In metabolism categories, genes related to inorganic ion transport and metabolism were highly prevalent in one genome (MTR_ET11) of tuna fish. In contrast, other genes were present in low percentages among all the genomes. Genes related to signal transduction mechanisms in cellular processes and signaling categories presented a higher rate than other genes involved in this process and were found to be the highest percentage in the genome of the crab (MTR_EC02). For information storage and processing, transcriptional factors were present in high numbers compared to other genes and were highly present in the shrimp genome (MTR_ES05). The highest percentage of genes involved in general function prediction only was present in the poorly characterized group and found in the MTR_ET06 and MTR_ET08 genomes present in the poorly characterized group and was found in the MTR_ET06 and MTR_ET08 genomes (<xref ref-type="supplementary-material" rid="SM4">Supplementary Figure S4</xref> and <xref ref-type="supplementary-material" rid="SM8">Supplementary Table S4F</xref>).</p>
</sec>
<sec id="sec16">
<label>3.3</label>
<title>Antimicrobial resistance genes (ARGs) in chromosomes of isolated <italic>E. coli</italic> from seafood</title>
<p>Several ARGs were identified across all <italic>E. coli</italic> isolates from seafish, with the highest number found in crabs. <italic>AmpC</italic> beta-lactamase was present in all isolates. <italic>CTX-M-15</italic> was found in MTR_EC03, and <italic>bla</italic><sub>DHA-1</sub> in MTR_EC02 (<xref ref-type="supplementary-material" rid="SM9">Supplementary Tables S5A,B</xref>). Moreover, fluoroquinolone resistance (<italic>qnrS1</italic>, <italic>qnrB4</italic>) in MTR_EC02, tetracycline resistance (<italic>tetA</italic>) in all genomes except MTR_EC02 and MTR_EC05, sulfonamide resistance (<italic>sul1</italic>) in MTR_EC02, aminoglycoside resistance (<italic>cpxA</italic>) in MTR_EC03, MTR_ET01, MTR_ET06, MTR_ET08, MTR_ET11, MTR_ET12, vancomycin resistance (<italic>vanG</italic>) in all genomes except MTR_EC02 and MTR_EC05 were observed.</p>
<p>All isolates exhibited a broader range of efflux pump systems and additional resistance mechanisms (<xref ref-type="supplementary-material" rid="SM9">Supplementary Table S5A</xref>), including protein overexpression and regulatory mutations (e.g., <italic>soxR, soxS</italic>, and <italic>marA</italic>), except for MTR_EC05. The major facilitator superfamily (MFS) pumps (e.g., <italic>emrK, emrY, mdfA</italic>, and <italic>mdtM</italic>), resulting in resistance to tetracyclines, phenicols, and other antibiotics, were present in almost all genomes. The genomes also included ATP-binding cassette (ABC) transporters, such as <italic>msbA</italic> and <italic>TolC</italic>, that contribute to resistance to nitroimidazoles and peptide antibiotics.</p>
<p>The distribution of resistance genes due to chromosomal mutation was: <italic>gyrA</italic> (MTR_ET01), <italic>parC</italic> (MTR_ET01), <italic>PBP3</italic> (All), <italic>cyaA</italic> (MTR_EC02), <italic>GlpT</italic> (except MTR_EC04, MTR_ES05, and MTR_ET09), <italic>UhpT</italic> (MTR_ET11), and <italic>EF-Tu</italic> (All). Biocide resistance and metal resistance genes were found across all genomes. We also observed the presence of additional resistance factors such as antibiotic target protection, antibiotic target alteration, antibiotic inactivation, reduced permeability to antibiotics, and other mechanisms (<xref ref-type="fig" rid="fig2">Figure 2</xref>). All genomes showed the concurrent presence of multiple ARGs (<xref ref-type="supplementary-material" rid="SM9">Supplementary Table S5A</xref>).</p>
<fig position="float" id="fig2">
<label>Figure 2</label>
<caption>
<p>Presence of AMR genes and their resistance mechanisms in 10 <italic>E. coli</italic> isolates from seafood, each color corresponds to a specific AMR (antimicrobial resistance) mechanism. Blue: antibiotic efflux; Orange: antibiotic efflux + reduced permeability to antibiotic; Green: antibiotic inactivation; Red: antibiotic target alteration; Purple: antibiotic target alteration + antibiotic efflux; Pink: antibiotic target alteration + antibiotic efflux + reduced permeability to antibiotic; Dark purple: antibiotic target protection.</p>
</caption>
<graphic xlink:href="fmicb-17-1737712-g002.tif" mimetype="image" mime-subtype="tiff">
<alt-text content-type="machine-generated">Heatmap titled "AMR Mechanism and related Gene Heatmap" showing resistance mechanisms across different gene isolates. Color-coded legend indicates mechanisms like antibiotic efflux, inactivation, and target alteration. Gene labels on the x-axis and isolate labels on the y-axis. Various colored bars represent specific resistance mechanisms linked to each gene.</alt-text>
</graphic>
</fig>
</sec>
<sec id="sec17">
<label>3.4</label>
<title>Virulence genes (VGs) in the chromosomes of isolated <italic>E. coli</italic> from seafood</title>
<p>A substantial number of VGs were found with a variation across all <italic>E. coli</italic> isolates, exhibiting considerable variation in their distribution patterns. Tuna-derived isolates harbored the highest abundance of adherence genes. Among those, curli fibers (<italic>cgsD, csgA, csgB, csgB, csgC, csgD, csgF</italic>), which play a role in biofilm formation, were detected, while MTR_EC02 contains <italic>csgA</italic> only, and <italic>csgC</italic> was only found in MTR_EC05. Nearly complete fimbrial operon (<italic>fimA-fimI</italic>) was identified across all genomes, except for MTR_EC02, which lacked <italic>fimB</italic> and <italic>fimI</italic>.</p>
<p>Multiple autotransporter genes (<italic>tibA, tibC, aida, aatA, agn43, cah, ehaA, ehaB, air/eaeX, upaG, upaH, fepA-fepD, fepG</italic>) were found with variable distribution patterns among the <italic>E. coli</italic> isolates. MTR_EC05, MTR_ES05, and MTR_ET09 possessed the most extensive repertoire of these genes. Iron uptake genes (<italic>sitA, fes, entA-entF, entS</italic>) were present in almost all genomes, though distribution showed strain-specific variations: <italic>sitA</italic> was only found in MTR_EC02, <italic>entD</italic> was absent in MTR_EC02 and MTR_EC05, and <italic>entE</italic> was missing from MTR_EC05.</p>
<p>Toxin-related genes had differential distribution patterns. The hemolysin gene (<italic>hlyE/clyA</italic>) was present in all isolates except MTR_EC05, while <italic>astA</italic> was identified in MTR_ES05 and MTR_ET09. The gene, <italic>hha</italic> was found in MTR_EC03, MTR_ES05, MTR_ET09, MTR_ET11, and MTR_ET12, but absent in MTR_EC02, MTR_EC05, MTR_ET01, MTR_ET06 and MTR_ET08. Stress survival genes were ubiquitously distributed, with <italic>gad</italic> in all isolates, while <italic>clpK1</italic> was uniquely detected in MTR_EC05 (<xref ref-type="fig" rid="fig3">Figure 3</xref>). Other genes related to virulence were also detected and summarized in <xref ref-type="supplementary-material" rid="SM9">Supplementary Table S5C</xref>.</p>
<fig position="float" id="fig3">
<label>Figure 3</label>
<caption>
<p>Virulence gene profile of <italic>E. coli</italic> isolates displayed as a heatmap. Heatmap illustrating the distribution of virulence-associated genes among the <italic>E. coli</italic> isolates obtained in this study. Each column represents an individual virulence gene, and each row corresponds to an isolate. The presence of a gene is indicated by a color-coded block, whereas its absence is represented in grey. Virulence genes are grouped into functional categories, with the following color representations: Adherence (blue), Autotransporter (orange), Fimbrial adherence determinants (green), Immune evasion (red), Invasion (purple), Iron uptake systems (brown), Non-LEE encoded TTSS effectors (light pink), Secretion system (olive green), Serum resistance (yellow-green), Stress survival (cyan), Toxin (pink), and Others (dark brown), as indicated in the legend. The heatmap demonstrates diversity in the virulence gene composition among isolates, highlighting variation in potential pathogenicity.</p>
</caption>
<graphic xlink:href="fmicb-17-1737712-g003.tif" mimetype="image" mime-subtype="tiff">
<alt-text content-type="machine-generated">Virulence gene heatmap showing gene expression patterns across nine isolates labeled on the y-axis. The x-axis lists specific genes. Colors represent VF classes: blue for adherence, orange for autotransporter, brown for iron uptake, pink for non-LEE encoded TTSS effectors, and others. A legend on the right explains the color coding for different virulence functions.</alt-text>
</graphic>
</fig>
</sec>
<sec id="sec18">
<label>3.5</label>
<title>Genomic islands and prophage-associated resistance and virulence determinants</title>
<p>A variable number of genomic islands and prophages were identified in the genomes of <italic>E. coli</italic> isolated from crabs, including some notable ARGs, such as <italic>blaDHA-1, blaCTX-M-15, sul1, tetA</italic>, and <italic>mph(A),</italic> which confer resistance to beta-lactamase, sulfonamide, tetracycline, and macrolides, respectively. Several essential VGs were also detected in these GIs, with curli fiber genes (<italic>csgC-csgG</italic>) being particularly prominent. Additional virulence factors identified within these GIs included diverse fimbrial genes (<italic>fimB, fimD, fimE, fimH</italic>), adhesion factors (<italic>fdeC</italic>), secretion system proteins (<italic>espX4, rhs, vgrG, espL1, vgrG, tssM, tssA, hcp1</italic>), and immune evasion genes (<italic>gmhA</italic> and <italic>gtrB</italic>).</p>
<p><italic>Escherichia coli</italic> derived from shrimp and tuna fish also exhibited a large number of GIs and prophages harboring ARGs related to multidrug efflux pump (<italic>mdfA</italic>) and several virulence factors (<xref ref-type="supplementary-material" rid="SM10">Supplementary Table S6</xref>).</p>
</sec>
<sec id="sec19">
<label>3.6</label>
<title>Mobile elements and plasmids identified from <italic>E. coli</italic> isolated in this study</title>
<p>Plasmids were detected in only three of the 10 <italic>E. coli</italic> genomes, all exclusively from crab isolates. MTR_EC02 harbored plasmids of multiple plasmid replicon types, including IncFII, IncFIA, IncFIB (pHCM2), and ColRNAI. IncFII carried ARGs [<italic>qnrB4, dfrA17, qacE, mph(A), sul1, bla</italic><sub>DHA-1</sub>] associated with IS<italic>6100</italic>. No VGs were found in these plasmids. MTR_EC03 and MTR_EC05 contained only the Col440I plasmid, which harbored no ARGs or VGs.</p>
<p>Across all 10 genomes, VGs were consistently identified in chromosomes flanked by mobile elements, whereas ARGs were located in both chromosomes and plasmids (<xref ref-type="supplementary-material" rid="SM11">Supplementary Table S7</xref>). Genes involved in Integration/Excision, Replication / Recombination / Repair, Phage, Transfer, and stability genes were detected in both the chromosome and plasmid of all isolates (<xref ref-type="supplementary-material" rid="SM9">Supplementary Table S5D</xref>).</p>
</sec>
<sec id="sec20">
<label>3.7</label>
<title>Population structure and its distribution</title>
<p>A total of 102 sequence types (STs) were identified among the 723 isolates, including five STs (ST3107, ST3298, ST345, ST1431, ST10) from our isolates (<xref ref-type="supplementary-material" rid="SM6">Supplementary Table S2</xref>). Genomic similarity was observed between <italic>E. coli</italic> belonged to ST345 and ST10 in this study and the isolates reported from Czech Republic (Wastewater) and USA (Human) and the isolates from Czech Republic (Wastewater and Human), Singapore (Human), Germany (Seafood and Aquatic water), Norway (Wastewater), USA (Human), Tunisia (Human), and Ghana (Human), accordingly (<xref ref-type="fig" rid="fig4">Figure 4A</xref>). <italic>E. coli</italic> ST27089 and ST23638 exhibited limited geographical distribution. Additionally, a few other STs were more prevalent in the comparison strains, including ST131 was the highest occurrence of a single type of ST detected from the Czech Republic (Wastewater, Human), New Zealand (Aquatic water), Norway (Wastewater), USA (Human), and Singapore (Human), and ST38 in Czech Republic (Wastewater and Human), Norway (Wastewater), India (Human), and USA (Human) (<xref ref-type="fig" rid="fig4">Figure 4B</xref>).</p>
<fig position="float" id="fig4">
<label>Figure 4</label>
<caption>
<p>Population structures and their distribution. <bold>(A)</bold> Population structure of different sequence types among 723 strains from around the globe, by country <bold>(B)</bold> Population structure of varying sequence types of 723 strains from around the world according to their sample source.</p>
</caption>
<graphic xlink:href="fmicb-17-1737712-g004.tif" mimetype="image" mime-subtype="tiff">
<alt-text content-type="machine-generated">Network diagrams labeled 4A and 4B. Diagram 4A clusters nodes with colors representing countries, such as Czech Republic, USA, and Norway. Diagram 4B groups nodes by sample sources, like wastewater and human samples. Both diagrams use pie charts at node centers to show the distribution, indicating relationships among different categories. The key for 4A identifies countries, while 4B identifies sample sources.</alt-text>
</graphic>
</fig>
</sec>
<sec id="sec21">
<label>3.8</label>
<title>Global phylogenetic relationships and comparative insights</title>
<p>The genomes of 10 <italic>E. coli</italic> were compared with a total of 713 global isolates, including a reference genome from different sources in different countries, using core genome SNP analysis (<xref ref-type="supplementary-material" rid="SM12">Supplementary Table S8</xref>). According to phylogenetic analysis, strains from this study form several minor clusters with other global strains (<xref ref-type="fig" rid="fig5">Figure 5A</xref>). A total of 108,456 SNPs were observed following core genome alignment, resulting in diverse phylogenetic clustering. Based on SNP tree analysis, isolates from tuna fish (MTR_ET06, MTR_ET0, and MTR_ET11) formed a close cluster with the isolates from diverse sources from different countries, such as Ecuador (seafood) and the Czech Republic (wastewater). MTR_ET01 formed a cluster with isolates from the USA (Human), the Czech Republic (wastewater), and MTR_ET12, which formed a cluster with isolates from Singapore (Human). The isolates from one tuna fish and shrimp (MTR_ET09 and MTR_ES05) showed a closer cluster with the isolates from Singapore (Human), Germany (Seafood), and the Czech Republic (Human). However, slightly different branches were observed for the isolates from crab, showing MTR_EC02 with Czech Republic (Wastewater), Singapore (Human), and USA (Seafood), and MTR_EC03 with Pakistan (Wastewater). Additionally, MTR_EC05 exhibited a distinct node within some closely clustered regions (<xref ref-type="fig" rid="fig5">Figure 5B</xref>).</p>
<fig position="float" id="fig5">
<label>Figure 5</label>
<caption>
<p>Global phylogeny and zoomed-in clade of 724 <italic>E. coli</italic> genomes. <bold>(A)</bold> Shows the maximum-likelihood global phylogeny constructed from 724 genomes, including the reference genome and 10 seafood-derived isolates analyzed in this study (nine additional genomes were excluded from assembled genomes due to their poor sizes were outside the expected range, indicating likely sequencing or assembly errors during Parsnp v2.0 filtering). A total of 108,456 core SNPs revealed diverse phylogenetic clustering, with concentric metadata rings representing country (<italic>n</italic>&#x202F;=&#x202F;1), the most inner circle, followed by sample source (2nd ring, <italic>n</italic>&#x202F;=&#x202F;1), serotype (3rd ring, <italic>n</italic>&#x202F;=&#x202F;6), plasmid replicons (4th ring, <italic>n</italic>&#x202F;=&#x202F;4), resistance genes (5th ring, <italic>n</italic>&#x202F;=&#x202F;3), and virulence genes (6th ring, <italic>n</italic>&#x202F;=&#x202F;9). The reference genome (pink) and the 10 isolates (green) are prominently highlighted in the inner tree. <bold>(B)</bold> Resents a zoomed-in view of the specific clade containing these 10 isolates, allowing clear visualization of their immediate phylogenetic neighbors and cluster relationships using the same metadata annotations as in the global tree. All the rings are the same as <bold>(A)</bold>, except for virulence genes (5th ring, <italic>n</italic>&#x202F;=&#x202F;9) and resistance genes (6th ring, <italic>n</italic>&#x202F;=&#x202F;3).</p>
</caption>
<graphic xlink:href="fmicb-17-1737712-g005.tif" mimetype="image" mime-subtype="tiff">
<alt-text content-type="machine-generated">Circular phylogenetic trees labeled 5A and 5B, displaying relationships among samples with detailed annotations. Multiple concentric rings indicate data such as country of origin, sample source, serotype, plasmid replicon, virulence genes, resistance genes, colored genome references, and clades. Legends explain colors and symbols used for each category.</alt-text>
</graphic>
</fig>
<p>Serotype comparison revealed limited concordance with international strains. Only two serotypes identified in our study (08: H19 and H12) matched the isolates from the Czech Republic (wastewater), while the remaining serotypes were unique to our seafood isolates (<xref ref-type="fig" rid="fig5">Figure 5A</xref>).</p>
<p>Resistance gene profiling revealed that <italic>ampC</italic> was nearly ubiquitous, present in approximately 100% of isolates. The <italic>bla</italic><sub>CTX-M-15</sub>, identified only in MTR_EC02, had been distributed among isolates from geographically diverse human and environmental sources, including the Czech Republic (wastewater and human), India (Human), the USA (Human), Tunisia (Human), and Norway (Wastewater). The resistance gene, <italic>bla</italic><sub>DHA-1</sub>, found also in MTR_EC02, appeared to be dominant in isolates from Norway (Wastewater) and Tunisia (Human) (<xref ref-type="fig" rid="fig5">Figure 5A</xref>).</p>
<p>The essential VGs involved in key pathogenic mechanisms, including adhesion (<italic>fimH</italic>), toxin production (<italic>astA</italic>), biofilm formation (<italic>csgD</italic>), iron acquisition (<italic>entA, entB, fepA</italic>), secretion system (<italic>espx1, gspD</italic>), and surface structure modulation (<italic>gtrA</italic>) were found to be distributed in global strains. Isolates from Tunisia (Human), Norway (Wastewater), Ghana (Environment and Human), and Singapore (Human) showed higher abundance of VGs than Bangladeshi seafood isolates characterized in this study (<xref ref-type="fig" rid="fig5">Figure 5A</xref>).</p>
<p>The Col440I_1 plasmid type, identified in MTR_EC03 and MTR_EC05, was most frequently detected in isolates from the Czech Republic (wastewater). The ColRNAI_1 and IncFIA_1 plasmids present in MTR_EC02 demonstrated broader geographic distribution, predominantly occurring in isolates from the Czech Republic (wastewater and human), the USA (Seafood and Human), and Ghana (Environmental and Human). The IncFIB (pHCM2) plasmid exhibited a more restricted distribution, being associated with the Czech Republic isolates (wastewater) (<xref ref-type="fig" rid="fig5">Figure 5A</xref>).</p>
</sec>
</sec>
<sec sec-type="discussion" id="sec22">
<label>4</label>
<title>Discussion</title>
<p>This comprehensive genomic study investigates ESBL-producing <italic>E. coli</italic> from seafood in Bangladesh. <italic>E. coli</italic> is noted for its genetic flexibility and its ability to transmit ARGs and VGs through horizontal gene transfer (<xref ref-type="bibr" rid="ref38">Li et al., 2024</xref>; <xref ref-type="bibr" rid="ref24">Hasegawa et al., 2018</xref>). This analysis offers critical insights into the landscape of AMR and virulence among these pathogens, while also contextualizing their relationship with global strains. The findings underscore significant public health and food safety concerns, as well as the broader challenges associated with the dissemination of AMR within aquatic food systems.</p>
<p>In Bangladesh, untreated sewage, agricultural runoff, and livestock waste consistently introduce <italic>E. coli</italic> and other faecal bacteria into aquaculture and coastal waters, with monsoon-driven hydrological pulses further intensifying microbial loads. Coupled with unsafe wash water, inadequate chilling, and frequent cross-contamination during harvest, processing, and retail, these conditions enable persistent transfer of faecal bacteria onto processed food, exposing a major weakness in the national supply chain (<xref ref-type="bibr" rid="ref49">Parvin et al., 2022</xref>). The ANI-based phylogenetic analysis in this study (<xref ref-type="fig" rid="fig1">Figure 1B</xref>), revealing source-specific clustering, particularly the segregation of tuna isolates into a distinct clade sharing identical STs (ST1431/cgST104784), indicates possible vertical transmission within aquaculture systems or persistent contamination from shared sources throughout the seafood production chain. The presence of MTR_EC05 as a phylogenetically distant outlier suggests introduction from an alternative contamination source, highlighting the complexity of microbial ecology in seafood supply chains (<xref ref-type="bibr" rid="ref57">Sheng and Wang, 2021</xref>). Decentralized wastewater treatment, improved runoff control, safe-water access, and stricter hygiene and cold-chain management across aquaculture and food-handling nodes provide practical, locally actionable means to prevent faecal bacterial contamination in Bangladesh (<xref ref-type="bibr" rid="ref26">Islam and Islam, 2022</xref>).</p>
<p>The serotype variation between seafood sources, complete O: H antigen profiles in shrimp and tuna versus incomplete antigen expression in crab, may reflect differential immune evasion strategies or adaptation to distinct ecological niches (<xref ref-type="bibr" rid="ref54">Rheman et al., 2024</xref>). Functional genomic characterization revealed adaptive features directly relevant to seafood contamination dynamics across all sources. The significant presence of inorganic ion transport and metabolism genes in tuna isolates (<xref ref-type="fig" rid="fig3">Figure 3</xref>), the high prevalence of signal transduction genes in crab isolates, and the abundance of transcriptional factors in the shrimp isolate collectively demonstrate that seafood-associated <italic>E. coli</italic> populations harbor genetic architectures specifically adapted for persistence under refrigeration and processing conditions, tolerance to preservation-associated stresses, and expression of virulence determinants that enhance pathogenic potential (<xref ref-type="bibr" rid="ref58">Sung et al., 2024</xref>; <xref ref-type="bibr" rid="ref64">Xie et al., 2022</xref>).</p>
<p>Core genome SNP analysis, revealing 108,456 polymorphisms, demonstrates substantial evolutionary divergence among the 723 isolates, yet the phylogenetic clustering of Bangladeshi seafood isolates belonged to ST345 and ST10 with international strains from Ecuador, the Czech Republic, the USA, Singapore, Germany, and Pakistan across human clinical, wastewater, and seafood sources indicates recent common ancestry and ongoing global dissemination of this lineage (<xref ref-type="fig" rid="fig5">Figure 5A</xref>). Globally, ST10 is recognised as a &#x201C;high-risk&#x201D; and frequently observed sequence type in extraintestinal clinical <italic>E. coli</italic> infections, including urinary tract infections, bloodstream infections, and other hospital/community-acquired infections, and is often associated with antimicrobial resistance (<xref ref-type="bibr" rid="ref44">Manges et al., 2019</xref>). According to Ecuador&#x2019;s Aquaculture and Fisheries Industry, Ecuador represents a major seafood exporter. The phylogenetic linkages with Bangladeshi tuna isolates (MTR_ET06, MTR_ET08, MTR_ET11) and strains from Ecuadorian seafood and Czech wastewater are particularly significant for food safety, suggesting potential contamination through international seafood trade networks or shared environmental reservoirs affecting geographically distant aquaculture operations (<xref ref-type="bibr" rid="ref3">Alexandre et al., 2025</xref>).</p>
<p>The phylogenetic clustering of crab isolates to human clinical strains from Singapore and the USA, alongside wastewater isolates from the Czech Republic and Pakistan, suggests bidirectional transmission between environmental, food, and human (<xref ref-type="fig" rid="fig5">Figure 5A</xref>). This interconnectedness indicates that contaminated seafood may serve as a vehicle for introducing antimicrobial-resistant strains into human populations, while simultaneously, wastewater contamination can introduce human-associated pathogens back into aquatic food production environments, creating a concerning epidemiological cycle (<xref ref-type="bibr" rid="ref46">Meradji et al., 2025</xref>; <xref ref-type="bibr" rid="ref1">Albini et al., 2022</xref>).</p>
<p>The limited serotype concordance with international strains, only O8: H19 and H12 matching Czech wastewater isolates (<xref ref-type="fig" rid="fig5">Figure 5A</xref>), while other serotypes remain unique to Bangladeshi seafood, suggests that, despite core genome relatedness, surface antigen diversity has evolved through localized selection pressures or recombination events (<xref ref-type="bibr" rid="ref40">Liu et al., 2020</xref>; <xref ref-type="bibr" rid="ref35">Lang et al., 2023</xref>). This serotype divergence has important implications for surveillance and outbreak detection, as traditional serotype-based monitoring may fail to identify genetically related strains that have undergone antigenic variation. The unique serotypes in Bangladeshi seafood could represent endemic adaptations to local aquaculture environments and emerging variants with potential to disseminate internationally through seafood trade (<xref ref-type="bibr" rid="ref33">Kavinesan et al., 2023</xref>).</p>
<p>Consistent with global ESBL-producing <italic>E. coli</italic>, seafood-derived isolates in this study harbored chromosomal <italic>AmpC &#x03B2;</italic>-lactamase, conferring broad-spectrum resistance to &#x03B2;-lactams, including third-generation cephalosporins and &#x03B2;-lactamase inhibitor combinations (<xref ref-type="fig" rid="fig5">Figure 5A</xref>). Phenotypic AST showed uniform resistance to third-generation cephalosporins (cefotaxime and ceftazidime) across all isolates, and this was strongly aligned with the genomic resistome (<xref ref-type="supplementary-material" rid="SM9">Supplementary Table S5B</xref>). All isolates carried a plasmid-mediated <italic>bla-ampC</italic> gene, which is known to confer resistance to expanded-spectrum cephalosporins and is not inhibited by &#x03B2;-lactamase inhibitors (<xref ref-type="bibr" rid="ref61">Thomson, 2010</xref>; <xref ref-type="bibr" rid="ref27">Jacoby, 2009</xref>). In contrast, blaCTX-M-15 and blaDHA1 were detected only in a minority of isolates, indicating that <italic>ampC</italic> production was the principal mechanism explaining the observed cephalosporin-resistance phenotype. The absence of <italic>blaCTX-M-15</italic> and <italic>blaDHA1</italic> in most isolates suggests that mechanisms such as <italic>ampC</italic> hyperproduction, efflux pumps, or porin alterations may contribute to the observed resistance phenotype (<xref ref-type="bibr" rid="ref39">Li et al., 2015</xref>). These findings are consistent with global reports on the increasing clinical relevance of plasmid-borne <italic>ampC</italic> enzymes in <italic>E. coli</italic> (<xref ref-type="bibr" rid="ref51">Philippon et al., 2002</xref>; <xref ref-type="bibr" rid="ref59">Tamma and Rodriguez-Bano, 2017</xref>). This ubiquitous distribution across environmental, food production, and clinical pathways presents serious public health challenges by substantially limiting treatment options for infections originating from contaminated seafood consumption (<xref ref-type="bibr" rid="ref20">Farrukh et al., 2025</xref>). Chromosomal mutations affecting antibiotic targets, <italic>gyrA, parC, PBP3, and EF-Tu</italic>, constitute stable, vertically inherited resistance mechanisms that persist regardless of plasmid loss or mobile element excision (<xref ref-type="fig" rid="fig2">Figure 2</xref>) (<xref ref-type="bibr" rid="ref9">Bush et al., 2020</xref>; <xref ref-type="bibr" rid="ref16">Darby et al., 2023</xref>; <xref ref-type="bibr" rid="ref43">Long et al., 2025</xref>). Their widespread occurrence across Bangladeshi seafood isolates indicates sustained antimicrobial selection pressure within aquaculture environments, evidencing systematic antibiotic misuse throughout production chains.</p>
<p>The extensive efflux pump repertoire generates constitutively resistant phenotypes that persist independently of antibiotic exposure by continuously reducing intracellular antimicrobial concentrations (<xref ref-type="bibr" rid="ref66">Zhang et al., 2024</xref>). These systems confer cross-resistance to structurally unrelated antimicrobials and chemical disinfectants used in processing facilities. Consequently, bacteria with robust efflux systems can survive sanitation procedures, persist on food contact surfaces, and contaminate finished products.</p>
<p>Pangenome analysis revealed that strain-specific genes (56.4%) substantially outnumber core genes (9.4%), demonstrating remarkable genomic plasticity within seafood-associated <italic>E. coli</italic> populations (<xref ref-type="supplementary-material" rid="SM1">Supplementary Figure S1</xref>). Comprehensive ARGs and VGs profiling also revealed substantial genetic diversity across seafood-derived <italic>E. coli</italic> isolates. This genetic flexibility indicates active horizontal gene transfer and adaptive evolution driven by antimicrobial pressures and environmental stresses encountered throughout aquaculture production, processing, and storage. The chromosomal localization of typically plasmid-borne resistance genes, including <italic>bla</italic><sub>CTX-M-15</sub>, <italic>qnrS1, qnrB4, tetA, and sul1,</italic> and chromosomally encoded virulence genes flanked by mobile genetic elements, provides evidence of mobile element-mediated genomic restructuring (<xref ref-type="supplementary-material" rid="SM11">Supplementary Table S7</xref>). Such chromosomal incorporation stabilizes resistance and virulence determinants by preventing gene loss during bacterial replication in the absence of selection pressure, thereby establishing permanently resistant and pathogenic strains that persist within seafood products (<xref ref-type="bibr" rid="ref11">Chekole et al., 2025</xref>). Interestingly, the variable distribution of curli components across isolates, with MTR_EC02 possessing only <italic>csgA</italic> and <italic>csgC</italic> exclusively present in MTR_EC05 (<xref ref-type="supplementary-material" rid="SM10">Supplementary Table S6</xref>), suggests strain-specific biofilm-forming capabilities that may influence persistence characteristics within different seafood matrices or processing environments (<xref ref-type="bibr" rid="ref19">Elafify et al., 2024</xref>; <xref ref-type="bibr" rid="ref6">Balistreri et al., 2025</xref>).</p>
<p>Particularly concerning is the co-localization of ESBL genes (<italic>bla</italic><sub>DHA-1</sub>, <italic>bla</italic><sub>CTX-M-15</sub>) with VGs (e.g., curli operons, fimbrial genes, type VI secretion system components, and immune evasion factors) within mobile genetic islands and prophages in crab-derived isolates (<xref ref-type="supplementary-material" rid="SM10">Supplementary Table S6</xref>). This genetic architecture facilitates the simultaneous horizontal transfer of both pathogenic and resistance traits (<xref ref-type="bibr" rid="ref62">Tokuda and Shintani, 2024</xref>). The identification of resistance genes (<italic>qnrB4, dfrA17, sul1, bla</italic><sub>DHA-1</sub>) associated with IS<italic>6100</italic> on IncFII plasmids of a seafood-associated <italic>E. coli</italic> further demonstrates active horizontal transfer capability among these populations (<xref ref-type="supplementary-material" rid="SM11">Supplementary Table S7</xref>). IS<italic>6100</italic>, recognized as a highly mobile IS, facilitates both intra- and inter-genomic rearrangements (<xref ref-type="bibr" rid="ref63">Varani et al., 2021</xref>), accelerating resistance evolution and enabling rapid bacterial adaptation to antimicrobial environments encountered during seafood production and processing.</p>
<p>The observation that international isolates from Tunisia, Norway, Ghana, and Singapore exhibit higher virulence gene abundance compared to Bangladeshi seafood strains suggests geographic variation in pathogenic potential, possibly reflecting differences in aquaculture practices, environmental conditions, or evolutionary histories (<xref ref-type="fig" rid="fig5">Figure 5A</xref>) (<xref ref-type="bibr" rid="ref52">Prakasan et al., 2022</xref>). However, the presence of core virulence determinants in Bangladeshi isolates (<xref ref-type="fig" rid="fig3">Figure 3</xref>) indicates sufficient potential pathogenic capacity to cause foodborne illness if not cooked or handled properly, and the concurrent presence of resistance determinants compromises treatment options.</p>
<p>Our findings indicate that seafood products represent high-risk vehicles for transmitting antimicrobial-resistant <italic>E.coli</italic>. There is an urgent need for stringent microbiological surveillance throughout seafood production chains, implementation of validated pathogen reduction technologies, elimination of prophylactic antibiotic use in aquaculture, enhanced wastewater treatment to prevent environmental contamination, and harmonized international food safety standards to protect consumer health and maintain the integrity of global seafood trade. Without coordinated One Health interventions addressing the aquaculture-environment-human interface, seafood will continue serving as a potentially important reservoir and dissemination pathway for antimicrobial-resistant pathogens, undermining global efforts to combat the AMR crisis while compromising food security and public health.</p>
</sec>
<sec sec-type="conclusions" id="sec23">
<label>5</label>
<title>Conclusion</title>
<p>This study provides the first comprehensive genomic characterization of ESBL-producing <italic>E. coli</italic> from seafood in Bangladesh, revealing significant genetic diversity, multidrug resistance, and the presence of key virulence factors. The detection of diverse MLSTs, <italic>&#x03B2;</italic>-lactamase genes such as <italic>blaCTX-M-15, ampC,</italic> and <italic>blaDHA-1</italic>, and plasmid-mediated ARGs underscores the potential of seafood to act as a reservoir and transmission vehicle for AMR. Notably, crab isolates harbored the highest number of ARGs and plasmids, while virulence genes were widely distributed across isolates, suggesting possible pathogenic potential. Comparative genomic analysis demonstrated strong links between Bangladeshi isolates and global strains from humans, animals, and the environment, highlighting the interconnectedness of AMR dissemination through food systems and aquatic environments. These findings emphasize the urgent need for strengthened AMR surveillance and strict hygiene practices in aquaculture and seafood processing, guided by a One Health approach, to mitigate public health risks associated with seafood-borne <italic>E. coli.</italic></p>
</sec>
</body>
<back>
<sec sec-type="data-availability" id="sec24">
<title>Data availability statement</title>
<p>The datasets presented in this study can be found in online repositories. The names of the repository/repositories and accession number(s) can be found in the article/<xref ref-type="supplementary-material" rid="SM1">Supplementary material</xref>.</p>
</sec>
<sec sec-type="ethics-statement" id="sec25">
<title>Ethics statement</title>
<p>The animal study was approved by Bangladesh Agricultural University (BAU) Animal Welfare and Ethics Committee in Mymensingh, Bangladesh [Approval Number: AWEEC/BAU/2023(25)]. The study was conducted in accordance with the local legislation and institutional requirements.</p>
</sec>
<sec sec-type="author-contributions" id="sec26">
<title>Author contributions</title>
<p>NF: Conceptualization, Data curation, Formal analysis, Investigation, Methodology, Software, Visualization, Writing &#x2013; original draft, Writing &#x2013; review &#x0026; editing. AS: Data curation, Formal analysis, Investigation, Methodology, Software, Visualization, Writing &#x2013; original draft. ZF: Investigation, Methodology, Writing &#x2013; review &#x0026; editing. MRan: Writing &#x2013; review &#x0026; editing. MI: Writing &#x2013; review &#x0026; editing. SR: Methodology, Writing &#x2013; review &#x0026; editing. AP: Methodology, Writing &#x2013; review &#x0026; editing. JH: Supervision, Writing &#x2013; review &#x0026; editing. TW: Resources, Validation, Funding acquisition, Writing &#x2013; review &#x0026; editing. RF: Resources, Validation, Writing &#x2013; review &#x0026; editing. MRah: Conceptualization, Funding acquisition, Project administration, Resources, Supervision, Validation, Writing &#x2013; review &#x0026; editing.</p>
</sec>
<ack>
<title>Acknowledgments</title>
<p>The authors would like to thank shop owners who helped with the sampling procedure.</p>
</ack>
<sec sec-type="COI-statement" id="sec27">
<title>Conflict of interest</title>
<p>The author(s) declared that this work was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.</p>
</sec>
<sec sec-type="ai-statement" id="sec28">
<title>Generative AI statement</title>
<p>The author(s) declared that Generative AI was not used in the creation of this manuscript.</p>
<p>Any alternative text (alt text) provided alongside figures in this article has been generated by Frontiers with the support of artificial intelligence and reasonable efforts have been made to ensure accuracy, including review by the authors wherever possible. If you identify any issues, please contact us.</p>
</sec>
<sec sec-type="disclaimer" id="sec29">
<title>Publisher&#x2019;s note</title>
<p>All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.</p>
</sec>
<sec sec-type="supplementary-material" id="sec30">
<title>Supplementary material</title>
<p>The Supplementary material for this article can be found online at: <ext-link xlink:href="https://www.frontiersin.org/articles/10.3389/fmicb.2026.1737712/full#supplementary-material" ext-link-type="uri">https://www.frontiersin.org/articles/10.3389/fmicb.2026.1737712/full#supplementary-material</ext-link></p>
<supplementary-material xlink:href="Image_1.png" id="SM1" mimetype="image/png" xmlns:xlink="http://www.w3.org/1999/xlink">
<label>SUPPLEMENTARY FIGURE S1</label>
<caption>
<p>The percentage of genes distributed among the ten isolates in the Pangenomic analysis.</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="Image_2.jpeg" id="SM2" mimetype="image/jpeg" xmlns:xlink="http://www.w3.org/1999/xlink">
<label>SUPPLEMENTARY FIGURE S2</label>
<caption>
<p>UpSet plot showing shared and unique gene intersections among the analyzed genomes. The upper histogram displays the number of genes contained in each intersection (i.e., gene sets shared by a specific combination of genomes). Each bar corresponds to the intersection highlighted directly below it in the connected-dot matrix. Taller bars represent larger shared gene sets. The dot matrix indicates which genomes contribute to each intersection: filled circles denote presence in a genome, and connected lines show the combination of genomes forming that intersection. The left bar plot shows the total number of genes identified in each genome.</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="Image_3.jpeg" id="SM3" mimetype="image/jpeg" xmlns:xlink="http://www.w3.org/1999/xlink">
<label>SUPPLEMENTARY FIGURE S3</label>
<caption>
<p>Presence-absence matrix of gene cluster among the ten <italic>E. coli</italic> isolates.</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="Image_4.jpeg" id="SM4" mimetype="image/jpeg" xmlns:xlink="http://www.w3.org/1999/xlink">
<label>SUPPLEMENTARY FIGURE S4</label>
<caption>
<p>Distribution of COG functional categories among the ten <italic>E.coli</italic> isolates.</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="Table_1.xlsx" id="SM5" mimetype="application/vnd.openxmlformats-officedocument.spreadsheetml.sheet" xmlns:xlink="http://www.w3.org/1999/xlink">
<label>SUPPLEMENTARY TABLE S1</label>
<caption>
<p>List of 722 <italic>E. coli</italic> strains selected through two independent PubMed queries based on title, full-text availability, relevance to the study, and availability of assembled genomes. The table includes all publications identified through the searches and metadata, along with the corresponding genomes downloaded from NCBI. Multi-sheet table summarizing the PubMed search strategy, metadata, and genome selection process for this study. <bold>(A)</bold> (First_query) contains the full search string and results from the initial query, while <bold>(B)</bold> (Metadata_first_query) provides metadata for genomes retrieved from that query. <bold>(C)</bold> (Second_query) presents the search string and results from the secondary query focused on seafood-associated <italic>E. coli</italic>, and <bold>(D)</bold> (Metadata_second_query) includes the corresponding genome metadata. <bold>(E)</bold> (Total_no_genome_by_sample) summarizes the total number of genomes grouped by sample source across both queries.</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="Table_2.xlsx" id="SM6" mimetype="application/vnd.openxmlformats-officedocument.spreadsheetml.sheet" xmlns:xlink="http://www.w3.org/1999/xlink">
<label>SUPPLEMENTARY TABLE S2</label>
<caption>
<p>Metadata for the 723 <italic>E. coli</italic> genomes used for minimal spanning tree analysis, including genome ID, sequence type (ST), country of origin, and sample source.</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="Table_3.xlsx" id="SM7" mimetype="application/vnd.openxmlformats-officedocument.spreadsheetml.sheet" xmlns:xlink="http://www.w3.org/1999/xlink">
<label>SUPPLEMENTARY TABLE S3</label>
<caption>
<p>Summary of genomic and typing information for all genomes analyzed. <bold>(A)</bold> Genomic features, and <bold>(B)</bold> MLST and cgST profiles.</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="Table_4.xlsx" id="SM8" mimetype="application/vnd.openxmlformats-officedocument.spreadsheetml.sheet" xmlns:xlink="http://www.w3.org/1999/xlink">
<label>SUPPLEMENTARY TABLE S4</label>
<caption>
<p>Pangenome analysis. <bold>(A)</bold> List of strain specific clusters with functional annotation and COG categories. <bold>(B)</bold> List of core gene clusters with functional annotation and COG categories. <bold>(C)</bold> List of dispensary gene clusters with functional annotation and COG categories. <bold>(D)</bold> Presence&#x2013;absence matrix of gene clusters across 10 genomes. <bold>(E)</bold> Clustered accessory gene presence/absence matrix for the 10 genomes (1 = present, 0 = absent). <bold>(F)</bold> COG assignment of each gene cluster.</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="Table_5.xlsx" id="SM9" mimetype="application/vnd.openxmlformats-officedocument.spreadsheetml.sheet" xmlns:xlink="http://www.w3.org/1999/xlink">
<label>SUPPLEMENTARY TABLE S5</label>
<caption>
<p>Summarization of ARGs <bold>(A)</bold>, phenotype and genotypic profile <bold>(B)</bold>, VGs <bold>(C)</bold>, and MGEs <bold>(D)</bold> of ten <italic>E. coli</italic> isolates in this study.</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="Table_6.docx" id="SM10" mimetype="application/vnd.openxmlformats-officedocument.wordprocessingml.document" xmlns:xlink="http://www.w3.org/1999/xlink">
<label>SUPPLEMENTARY TABLE S6</label>
<caption>
<p>Genomic characterization of <italic>E. coli</italic> isolates, detailing the presence of genomic islands (GIs), prophages, virulence genes (VGs), and antimicrobial resistance genes (ARGs) within the chromosome. For each isolate, the table reports the number of GIs and prophages, the virulence factor classes and specific virulence genes identified, as well as the drug classes and corresponding ARGs detected.</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="Table_7.docx" id="SM11" mimetype="application/vnd.openxmlformats-officedocument.wordprocessingml.document" xmlns:xlink="http://www.w3.org/1999/xlink">
<label>SUPPLEMENTARY TABLE S7</label>
<caption>
<p>Summary of mobile genetic elements and plasmid content in ten <italic>E. coli</italic> strains. The table reports detected mobile elements, plasmid types, and the presence of associated antimicrobial resistance genes (ARGs) and virulence genes (VGs).</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="Table_8.xlsx" id="SM12" mimetype="application/vnd.openxmlformats-officedocument.spreadsheetml.sheet" xmlns:xlink="http://www.w3.org/1999/xlink">
<label>SUPPLEMENTARY TABLE S8</label>
<caption>
<p>Metadata and genomic characteristics of <italic>E. coli</italic> isolates (<italic>n</italic>&#x202F;=&#x202F;723) used to construct the global phylogeny. The table includes isolate ID, sample source, and country of origin, along with detected antimicrobial resistance (AMR) genes, virulence-associated genes, plasmid replicon types, and serotypes, all of which were used to annotate and interpret phylogenetic relationships. The last 10 isolates at the bottom of the sheet were our isolates, which were compared (Yellow marking).</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="Table_9.docx" id="SM13" mimetype="application/vnd.openxmlformats-officedocument.wordprocessingml.document" xmlns:xlink="http://www.w3.org/1999/xlink"/>
</sec>
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<fn-group>
<fn fn-type="custom" custom-type="edited-by" id="fn0012">
<p>Edited by: <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/600178/overview">Mohammad Tahir Siddiqui</ext-link>, Indian Institute of Technology Delhi, India</p>
</fn>
<fn fn-type="custom" custom-type="reviewed-by" id="fn0013">
<p>Reviewed by: <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/295164/overview">Yanhong Liu</ext-link>, United States Department of Agriculture (USDA), United States</p>
<p><ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/3134555/overview">Abdulafiz Musa</ext-link>, East Tennessee State University, United States</p>
<p><ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/3268119/overview">Saniya Zaidi</ext-link>, Indian Institute of Technology Delhi, India</p>
</fn>
</fn-group>
<fn-group>
<fn id="fn0001">
<label>1</label>
<p>
<ext-link xlink:href="https://www.arc.ox.ac.uk" ext-link-type="uri">https://www.arc.ox.ac.uk</ext-link>
</p>
</fn>
<fn id="fn0002">
<label>2</label>
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<ext-link xlink:href="https://github.com/tseemann/mlst" ext-link-type="uri">https://github.com/tseemann/mlst</ext-link>
</p>
</fn>
<fn id="fn0003">
<label>3</label>
<p>
<ext-link xlink:href="https://cge.food.dtu.dk/services/MLST/" ext-link-type="uri">https://cge.food.dtu.dk/services/MLST/</ext-link>
</p>
</fn>
<fn id="fn0004">
<label>4</label>
<p>
<ext-link xlink:href="https://cge.food.dtu.dk/services/cgMLSTFinder/" ext-link-type="uri">https://cge.food.dtu.dk/services/cgMLSTFinder/</ext-link>
</p>
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<fn id="fn0005">
<label>5</label>
<p>
<ext-link xlink:href="https://www.genomicepidemiology.org/services/" ext-link-type="uri">https://www.genomicepidemiology.org/services/</ext-link>
</p>
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<fn id="fn0006">
<label>6</label>
<p>
<ext-link xlink:href="https://github.com/tseemann/abricate" ext-link-type="uri">https://github.com/tseemann/abricate</ext-link>
</p>
</fn>
<fn id="fn0008">
<label>8</label>
<p>
<ext-link xlink:href="https://cge.food.dtu.dk/services/MobileElementFinder/" ext-link-type="uri">https://cge.food.dtu.dk/services/MobileElementFinder/</ext-link>
</p>
</fn>
<fn id="fn0009">
<label>9</label>
<p>
<ext-link xlink:href="https://proksee.ca/" ext-link-type="uri">https://proksee.ca/</ext-link>
</p>
</fn>
<fn id="fn0010">
<label>10</label>
<p>
<ext-link xlink:href="https://ecotyper.stanford.edu" ext-link-type="uri">https://ecotyper.stanford.edu</ext-link>
</p>
</fn>
<fn id="fn0011">
<label>11</label>
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<ext-link xlink:href="https://cge.food.dtu.dk/services/SerotypeFinder/" ext-link-type="uri">https://cge.food.dtu.dk/services/SerotypeFinder/</ext-link>
</p>
</fn>
</fn-group>
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</article>