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Aquaculture is one of the fastest-growing food-producing sectors worldwide, and its production practices are intended to satisfy the rising food demand for human consumption. Global aquaculture production has tripled from 34 million tonnes (Mt) in 1997 to 112 Mt in 20171. The main species groups, contributing to nearly 75% of the production, were seaweed, carps, bivalves, catfish, and tilapia (Oreochromis spp.)1. However, the appearance of diseases caused by microbial entities is unavoidable because of intensive fish farming, leading to potential economic losses2.
Antibiotic usage in fish farming practices is well known for preventing and treating bacterial infections, the main limiting factor in productivity3,4. Nonetheless, residual antibiotics accumulate in aquaculture sediments and water, exerting selective pressure and modifying the fish-associated and the residing bacterial communities5,6,7,8. Consequently, the aquaculture environment serves as a reservoir for antimicrobial resistance genes (ARGs), and the further emergence and spread of antibiotic-resistant bacteria (ARB) in the surrounding milieu9. In addition to the bacterial pathogens commonly observed affecting fish farming practices, members of the Enterobacteriaceae family are often encountered, including human pathogen strains of Enterobacter spp., Escherichia coli, Klebsiella spp., and Salmonella spp.10. E. coli is the most common microorganism isolated from fish meal and water in fish farming11,12,13,14,15.
E. coli is a versatile gram-negative bacterium that inhabits the gastrointestinal tract of mammals and birds as a commensal member of their intestinal microbiota. However, E. coli possess a highly adaptive capacity to colonize and persist in different environmental niches, including soil, sediments, food, and water16. Because of the gene gain and loss through the horizontal gene transfer (HGT) phenomenon, E. coli has rapidly evolved into a well-adapted antibiotic-resistant pathogen, able to cause a broad spectrum of diseases in humans and animals17, 18. Based on the isolation origin, pathogenic variants are defined as intestinal pathogenic E. coli (InPEC) or extra-intestinal pathogenic E. coli (ExPEC). Furthermore, InPEC and ExPEC are subclassified into well-defined pathotypes according to disease manifestation, genetic background, phenotypic traits, and virulence factors (VFs)16,17,19.
Traditional culture and molecular techniques for pathogenic E. coli strains have allowed the rapid detection and identification of different pathotypes. However, they may be time-consuming, laborious, and frequently require high technical training19. Furthermore, no single method can be used to reliably study all pathogenic variants of E. coli because of the complexity of their genetic background. Currently, these drawbacks have been overcome with the advent of high-throughput sequencing (HTS) technologies. Whole-genome sequencing (WGS) approaches and bioinformatic tools have improved the exploration of microbial DNA affordably and at a large scale, facilitating the in-depth characterization of microbes in a single run, including closely related pathogenic variants20,21,22. Depending on the biological questions, several bioinformatics tools, algorithms, and databases can be used to perform data analysis. For instance, if the main goal is to assess the presence of ARGs, VFs, and plasmids, tools such as ResFinder, VirulenceFinder, and PlasmidFinder, along with their associated databases, might be a good starting point. Carriço et al.22 provided a detailed overview of the different bioinformatics software and related databases applied for microbial WGS analysis, from raw data preprocessing to phylogenetic inference.
Several studies have demonstrated the broad utility of WGS for genome interrogation regarding antimicrobial resistance attributes, pathogenic potential, and tracking of the emergence and evolutionary relationships of clinically relevant variants of E. coli sourced from diverse origins23,24,25,26. WGS has enabled the identification of molecular mechanisms underlying the phenotypic resistance to antimicrobials, including those rare or complex resistance mechanisms. This is through detecting acquired ARG variants, novel mutations in drug-target genes, or promoter regions27,28. Moreover, WGS offers the potential to infer antimicrobial resistance profiles without requiring prior knowledge about the resistance phenotype of a bacterial strain29. Alternatively, WGS has allowed the characterization of the mobile genetic elements (MGEs) carrying both antimicrobial resistance and virulence features, which has driven the bacterial genome evolution of existing pathogens. For instance, the application of WGS during the investigation of the German E. coli outbreak in 2011 resulted in uncovering the unique genomic features of an apparently novel E. coli pathotype; interestingly, those outbreak strains originated from the enteroaggregative E. coli (EAEC) group, which acquired the prophage encoding the Shiga toxin from the enterohemorrhagic E. coli (EHEC) pathotype30.
This work presents a methodological adaptation of the workflow for bacterial WGS using a benchtop sequencer. Moreover, a bioinformatics pipeline is provided using web-based tools to analyze the resulting sequences and further support researchers with limited or no bioinformatics expertise. The described methods allowed elucidation of the antimicrobial resistance, virulence, and mobilome features of a pathogenic E. coli strain ACM5, isolated in 2011 from inland farmed Oreochromis spp. in Sinaloa, Mexico12.