Abstract
Aeromonas hydrophila is a ubiquitous fish pathogen and an opportunistic human pathogen. It is mostly found in aquatic habitats, but it has also been isolated from food and bottled mineral waters. It causes hemorrhagic septicemia, ulcerative disease, and motile Aeromonas septicemia (MAS) in fish and other aquatic animals. Moreover, it might cause gastroenteritis, wound infections, and septicemia in humans. Different variables influence A. hydrophila virulence, including the virulence genes expressed, host susceptibility, and environmental stresses. The identification of virulence factors for a bacterial pathogen will help in the development of preventive and control measures. 95 Aeromonas spp. genomes were examined in the current study, and 53 strains were determined to be valid A. hydrophila. These genomes were examined for pan- and core-genomes using a comparative genomics technique. A. hydrophila has an open pan-genome with 18,306 total genes and 1620 genes in its core-genome. In the pan-genome, 312 virulence genes have been detected. The effector delivery system category had the largest number of virulence genes (87), followed by immunological modulation and motility genes (69 and 46, respectively). This provides new insight into the pathogenicity of A. hydrophila. In the pan-genome, a few distinctive single-nucleotide polymorphisms (SNPs) have been identified in four genes, namely: d-glycero-beta-d-manno-heptose-1,7-bisphosphate 7-phosphatase, chemoreceptor glutamine deamidase, Spermidine N (1)-acetyltransferase, and maleylpyruvate isomerase, which are present in all A. hydrophila genomes, which make them molecular marker candidates for precise identification of A. hydrophila. Therefore, for precise diagnostic and discrimination results, we suggest these genes be considered when designing primers and probes for sequencing, multiplex-PCR, or real-time PCR.
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Introduction
Aquaculture is one of the fastest-growing food industries that supplies the world with high-quality proteins. In 2020, 122.6 million metric tonnes of aquaculture products were produced globally, with a market value of USD 281.5 billion1. The increase in aquaculture production helps in minimizing the gap formed due to the food shortage, which is caused by overpopulation. Therefore, the quantity of farmed fish from both marine and freshwater farms has expanded considerably during the last five decades2. In the last 20 years, world aquaculture's yearly production increased by 609% between 1990 and 2020, with an average annual growth rate of 6.7%1. One of the successful freshwater aquaculture candidates is the Nile tilapia (Oreochromis niloticus), which is cultivated in several regions of the world, including China, Indonesia, and Egypt as the top three producing countries3. The increasing output necessitates the efficient use of water resources, which has been achieved through intensive aquaculture systems; however, it is a very stressful environment for cultivated animals and has intensified the development and spread of bacterial infections4. Freshwater bodies have been found as reservoirs of Aeromonas hydrophila, which may infect fish, reptiles, amphibians, bivalves, and humans5,6,7,8. It has been proven to be the causative agent of numerous disease outbreaks in fish, including septicemia, ulcerative and hemorrhagic diseases2,9.
Aeromonas hydrophila is also a public health concern because of its ability to transfer illness to humans since it has been isolated from a variety of sources, including food, animals, groundwater, and wastewater, in different stages of treatment10,11,12. Therefore, it is crucial to precisely diagnose and identify bacterial strains belonging to that species. However, phenotypic methodologies were applied for the characterization of Aeromonas spp. resulted in erroneous and inconsistent results13. For instance, after preliminary phenotypic identification of 119 strains isolated from sick fish, only 35.5% were verified to the species level as A. hydrophila using 16S rRNA-RFLP and rpoD sequences14. Although 16S rRNA gene sequencing is frequently applied for bacterial classification, it has limited discriminatory power at the species level13. On the other hand, several distinct virulence genes have been identified so far as sharp molecular chronometers applicable for diagnostic purposes15. However, to the best of our knowledge, there are a few earlier studies concerned with virulence gene-based typing of A. hydrophila.
Practically, A. hydrophila identification is mostly based on the presence of virulence genes such as cytotoxic enterotoxin gene (act), aerolysin gene (aer), hemolysin A gene (hylA), and enterotoxin gene (ast)16. However, some of these genes are present in non-A. hydrophila strains, and it is not necessary to detect all virulence genes in a single pathogenic strain; as evidenced by several investigations employing either fish or clinical samples17,18,19. Therefore, and because of the limitations inherent in such methods, both the 16S rRNA sequence and the PCR detection virulence genes may misidentify novel isolates.
For infection control in fish farms, the perfect vaccine is not yet available due to the genetic diversity of Aeromonas strains as well as the lack of a universal biomarker gene that could be used for molecular typing or as a vaccine target. Many approaches have been applied for infection control, including the use of antibiotics which has the drawback of increasing antimicrobial resistance17,20,21. In other words, due to a shortage of understanding of the genetic diversity of Aeromonas, vaccines can only provide limited protection17. The lack of cross-protection against various isolates may be the reason why a commercial vaccine against A. hydrophila infection hasn’t yet been developed. Serotypes are also imperfectly defined, which can cause mutants to escape and reinfect animals who have received vaccinations. Moreover, effective diagnostic tests that accurately distinguish between “target” and “non-target” pathogens might facilitate their infection control22.
It is also important to highlight that the virulence factors mentioned in the literature were mostly based on investigations conducted on A. hydrophila SSU, which was later reclassified as Aeromonas dhakensis19. For molecular typing of bacterial species, multi-locus sequence typing (MLST) has proven its reliability in strain identification, by using housekeeping genes such as rpoD in combination with 16S rDNA-RFLP14. However, those methods still have considerable limitations, such as the cost and computing resources needed.
Recently, complete genome sequencing technologies have greatly improved phylogenetic analysis, genotyping and bacterial identification, antibiotic genes assessment, and disease surveillance. In an attempt to validate the publicly available genomes of A. hydrophila and to identify the total virulence factors they carry, 14 full A. hydrophila genomes and 51 draft genomes were investigated in 201823. However, the number of full genomes has now grown more than thrice, and it is critical to shed more light on the virulence potential of A. hydrophila to remove the current ambiguities in its classification and purpose new effective molecular markers for correct identification.
It is known that virulence factor acquisition and antibiotic resistance genes are mainly happening through horizontal gene transfers rather than vertical transmission22,24,25. Such markers are useless on certain occasions and cannot reflect exact taxonomic relationships. Therefore, it is critical to update our knowledge of the virulence factor profile in A. hydrophila based on precisely named strains by considering the maximum number of available genotypes. In the present study, 95 complete genomes of the genus Aeromonas were analyzed using a comparative genomics approach. Thereafter, the pan-genome and core-genome were built, and the average nucleotide identity (ANI) was calculated. These findings supplied substantially comprehensive genetic diversity of A. hydrophila, offering critical information on the species genomic makeup and virulence factors. The pathogenicity potential of A. hydrophila strains was investigated, and new SNPs markers for A. hydrophila differentiation were explored.
Materials and methods
Genomic dataset of Aeromonas spp.
A total of 95 full genome sequences of the Aeromonas genus were retrieved from the National Center for Biotechnology Information (NCBI). Genome completeness, strains recognized as Aeromonas hydrophila and Aeromonas sp., and accessible complete genomes from other Aeromonas species were employed as inclusion criteria. All complete genomes identified as A. hydrophila (n = 54), Aeromonas spp. (n = 27), and representatives of other Aeromonas species (n = 14) were obtained from GenBank during October 2022. Each genome's information and BioSample records were also collected. The supplementary Table S1 lists detailed information on the 95 Aeromonas spp. strains used in this study, including the accession number of each data set and the download link. Only complete genomes were considered to provide the most realistic picture of the strain’s virulence gene diversity and potential identification biomarkers.
Average nucleotide identity and digital DNA-DNA hybridization
For the confirmation of species affiliations, nucleotide-level comparisons of each pairwise combination of genomes were conducted using average nucleotide identity (ANI). The Python script PyANI v0.2.722 was used to compute pairwise ANI values using two different methods, the MUMmer26 and the BLAST+ method27 employing the ANIm and ANIb options, respectively. The valid members of A. hydrophila have been selected for further analysis, and the misidentified strains were excluded. This was based on the threshold value that indicates the presence of the same species of ANI being greater than 94%22,28. For confirmation of ANI results, the recommended BLAST+ method was utilized to create digital DNA-DNA hybridization (dDDH) values for DNA-DNA hybridization using the Genome-to-Genome Distance Calculator online server (GGDC v3)29. To complete this stage, all genome sequences were presented as queries against all other sequences that had been analyzed. Formula 2 had been used to calculate the DNA-DNA hybridization scores. Formula 2 was used because of its tolerance to genome size. The cut-off value for dDDH was 70% for species discrimination.
Core- and Pan-genome construction
To preserve consistency and uniformity, all genomes of the examined Aeromonas spp. strains were functionally re-annotated using the Prokka suite, version 1.14.6. The following settings were used to predict the protein-coding genes: -genus Aeromonas -species hydrophila -evalue 1e−09 -coverage 80 -mincontiglen 200) according to Podrzaj et al.28. Roary30 was then used to build the core- and pan-genome of Aeromonas spp. using a default identity threshold of 95%. Briefly, the genes have been categorized into four groups: core genes, which are present in more than 99% of genomes. Soft core genes, which are present in more than 95% but less than 99% of the strain. Shell genes, which are present in 15% to less than 95% of the strains, and cloud genes, which are present in less than 15 percent of the total number of strains. PanGP31 tool was used to visualize both the core and pangenomes, by using a gene presence/absence matrix generated from Roary as an input. In brief, pan-genome curve-fitting was achieved using Heaps' law, as described by Podrzaj et al.28. The curve equation was (ypan = Apan xBpan + Cpan), where y is the size of the pan-genome, x is the number of genomes, while A, B, and C are the curve-fitting parameters. When the Bpan value falls between 0 and 1, with the progressive addition of more genomes, the size of the pan-genome grows indefinitely, suggesting an open pan-genome.
Genes encoding virulence factors
A custom bash script was used to determine the virulence-encoding genes in A. hydrophila strains. Based on the virulence factor genes obtained from the virulence factor database (VFDB), the virulence factor was filtered and determined32. All genes that were observed only in A. hydrophila were identified using a dataset generated by the Roary tool’s integrated function query_pan_genome with the difference option. Following that, the virulence genes present in all valid A. hydrophila strains were identified. Then the differential virulence genes were found based on the presence only in valid A. hydrophila strains or it has similarity lower than 95% as a cut-off value of the Roary tool.
Phylogenetic analysis and SNPs identification
Phylogenetic trees were reconstructed using 16S rRNA and uniquely determined genes. After obtaining multiple sequence alignments using MUSCLE (defaults values: Gap Open Penalties = − 400.00 /Gap Extend Penalties = 0.00) and the proper evolutionary model was chosen, MEGA-X33 was used for phylogenetic tree reconstruction. The trees were reconstructed using the maximum likelihood method and the most proper substitution model. All positions with coverage of less than 95% were eliminated. The bootstrap value was assigned to 500. The multiple sequence alignment CLUSTALW format was constructed using T-Coffee tools to find relevant SNPs that could be used for genotyping or molecular identification, and a customized Python script msa2snp.py (https://github.com/pinbo/msa2snp) was then used to find all SNPs in the genes of interest. The output of SNPs detection was subjected to manual curation to select the most informative one which is present only in 100% of A. hydrophila genomes.
Results
General genomic features of Aeromonas spp.
The overall genomic characteristics of the Aeromonas strains used in this investigation are shown in Supplementary Table S1. Aeromonas simiae A6 and Aeromonas sp. ASNIH4 had the smallest and largest genome sizes, respectively, and the whole genome sizes varied between 3.97 and 5.48 Mbp. The genomes that have been confirmed to be A. hydrophila showed genome sizes within the range of 4.30–5.45 Mbp, with A. hydrophila WCX23 and A. hydrophila KAM330 having the smallest and largest genome sizes, respectively. The number of coding sequences (CDSs) in these genomes also differed among the complete genomes of all Aeromonas strains (range: 3782–5161 with an overall 36.46% difference) and within the A. hydrophila genomes (range: 4091–5134 with an overall 25.49% difference). The total guanine and cytosine content (G + C content) of the genomes of Aeromonas spp. ranged between 57.9% and 62.9%, while within A. hydrophila, the range was 60.4–62.0%, with relatively small variations across strains. Considerable variation was also seen in the tRNA numbers among all genomes (Supplementary Table S1).
ANI and dDDH analysis of Aeromonas spp.
According to the result of the ANI analysis presented in Fig. 1, all strains were divided into two big clades, one of which holds most species that are known to be A. hydrophila. Only 53 genotypes were found and classified as A. hydrophila strains. This resulted from the exclusion of four strains previously classified as A. hydrophila and the inclusion of three strains without taxonomic species status. These include the strains NEB724, 4AK4, B11, and YL17, which are eliminated, while Aeromonas sp. 2692-1, Aeromonas sp. 1805, and Aeromonas sp. ASNIH4 were included and identified as A. hydrophila genotypes. The inclusion and exclusion were observed and consistent with both the ANI, MUMmer and BLAST+ methods. The ANIm value for excluded strains was less than 0.95 compared to the strains valid as A. hydrophila. While the newly included strains showed ANIm values greater than 0.95. This similarity was also confirmed by the dDDH as the excluded strains showed dDDH values of less than 70%. The included strains have values greater than 70%.
Only 12 strains showed ANIm greater than 0.99 to each other (ML09-119, PC-104A, AL09-71, JBN2301, D4, LHW39, Ah27, ZYAH72, GYK1, NJ-35, AC133, and J-1) (supplementary Table S2). ANI reveals divergence and genetic heterogeneity among A. hydrophila members. Consequently, it will be considerably more challenging to identify a target sequence that may be employed for diagnostic purposes. All the strains that were clustered together as A. hydrophila scored higher than 70%, according to the dDDH results (supplementary Table S3).
Core- and Pan-genome analysis
A pan-genome study was undertaken to better understand the differences in virulence genes across A. hydrophila strains (Fig. 2). The figure was constructed based on the presence and absence of genes in all valid strains (n = 53). The estimated number of genes in the pan-genome was 18,306 genes. The increase and decrease of gene numbers in pan and core-genomes, respectively, are presented in Fig. 3. The analysis revealed that both the pan-genome and core-genome are open. The “B” values for the curve-fitting equations for A. hydrophila and Aeromonas spp. are 0.55 and 0.57, respectively. A. hydrophila has 1620 genes in its core-genome and 18,306 total genes, according to the pan-genome analysis. The number of genes in the pan-genome and core-genome was drastically altered by the addition of strains belonging to Aeromonas spp. The Aeromonas spp. When all strains were considered, the pan-genome and core genome had 59559 and 79 genes, respectively. According to the estimates, the pan-genome of A. hydrophila is 4.0 times greater than the average genome size of each strain (average genes number = 4577; Fig. 3a); this represents more than two folds when the entire number of strains is taken into consideration (Fig. 3b). Only 1620 genes, or 8.84% of genes, were shared by A. hydrophila, while only 79 genes, or 0.13%, were shared by all Aeromonas spp. Figure 3.
The increase and decrease of gene number in pan (blue) and core (green) genomes, respectively. (a) = gnomes identified as A. hydrophila (n = 53), (b): genomes of all Aeromonas spp. strains under investigation (n = 95). The gene accumulation curves for the power-law regression model are shown as a function of the number of consecutively added genomes.
Genes encoding virulence factors
For the determination of virulence genes in A. hydrophila, the Roary output was screened based on the comparison with VFDB-indexed genes. The detected genes are listed in Table 1 along with their functional categories. It is worth mentioning that most of the virulence genes are not common in all strains. For instance, the aerolysin (aerA) gene is detected in only 40 out of the 53 valid strains tested. Likewise, hemolysin (hylA) genes were found in only 48 strains. If such genes are used to name unknown strains, there would be high false negative rates of 24.5% and 9.4% for aerA and hylA, respectively. Therefore, for fast PCR detection, it is essential to name genes whose presence is restricted to A. hydrophila and are absent in other species. A total of 312 genes representing virulence factors in the pan-genome were found (Table 1). Overall, the effector delivery system has the largest number of genes (87) and is followed by the immune modulation factor which has 69 genes. Remarkably, only virulence genes, namely, gmhB, and cheD, besides speG, and nagL, have been commonly recognized in all A. hydrophila genotypes.
Phylogenetic analysis and SNPs identification
To investigate the capability of the four remarkable genes to distinguish A. hydrophila from other members of the genus Aeromonas, phylogenetic analysis was performed and compared to the tree generated using the 16S rRNA sequences. Figure 4 shows that 16S rRNA sequencing is unreliable for discrimination between A. hydrophila strains and members of other Aeromonas spp. It has clubbed mislabeled and non-A. hydrophila aeromonads (colored yellow and red respectively) among the valid A. hydrophila strains. However, when the Roary output was applied to find the differential genes. The phylogenetic tree perfectly aligned with the categorization generated from the ANI analysis based on the whole genome study.
Reconstructed Phylogenetic tree based on 16S rRNA gene (n = 95). The tree was constructed by using the maximum likelihood method and Kimura 2-parameter model34 as a best-fit model. All positions with less than 95% site coverage were eliminated. There was a total of 543 positions in the final dataset. Evolutionary analyses were conducted using MEGA-X. Green, valid A. hydrophila strains; yellow, strains misidentified as A. hydrophila; red, not A. hydrophila strains. The tree was visualized using the online iTOL tool35.
Accordingly, we propose these four genes as powerful discrimination tools capable of differentiating between A. hydrophila and non-A. hydrophila aeromonads as ANI value did. Figure 5 shows an example of using one of these genes phylogeny which is perfectly aligned with ANI results.
Reconstructed Phylogenetic tree based on the gmhB gene (n = 95). The tree was constructed by using the maximum likelihood method and Kimura 2-parameter model34 as a best-fit model. All positions with less than 95% site coverage were eliminated. There was a total of 543 positions in the final dataset. Evolutionary analyses were conducted using MEGA-X. Green, valid A. hydrophila strains; yellow, strains misidentified as A. hydrophila; red, not A. hydrophila strains. The tree was visualized using the online iTOL tool35.
The name of the proposed genes, as well as the functional annotation of each gene, are listed in Table 2. When categorized phenotypically, they express the functions of immune modulation (gmhB), motility (cheD), as well as spermidine N(1)-acetyltransferase (speG), and maleylpyruvate isomerase (nagL). Table 2 also includes a list of the unique SNPs seen in each gene, which could be used to distinguish between A. hydrophila and non-A. hydrophila aeromonads. Only speG was found to have the highest SNP records as it has seven distinct SNPs while each of the other genes has only one unique SNP.
Discussion
The nature of the genus Aeromonas which comprises serious pathogens is complex and it is difficult to be identified at the species level through phenotypic characterization13. Therefore, it is crucial to explore innovative approaches for the correct taxonomic characterization of its members. The pathogenic species, A. hydrophila, is ubiquitous in aquatic environments and is associated with diseases that affect humans and many fish species36. The employing of comparative genomics could aid in guidance to detect new biomarkers for identification. Additionally, in silico technologies have made it possible to distinguish between strains thanks to DNA sequences and helped in the development of new molecular markers for the detection and identification of epidemiologically significant microbes37. For instance, comparative genomics can reveal insights into evolutionary relationships, gene functions, and molecular mechanisms. However, it has limitations, such as the quality and completeness of genome sequences, which vary between species and databases. Moreover, the annotation and interpretation of genome features vary according to the technology and software used. Furthermore, the evolutionary history and divergence of genomes, and the functional significance and biological relevance of genomic variations might add to its limitations.
The identification of this pathogen can be challenging due to its phenotypic and genotypic diversity and its similarity to other Aeromonas species. Misidentification of A. hydrophila can lead to incorrect diagnosis, inappropriate treatment, and increased mortality in fish. For human infection, it can be confused with other Aeromonas species or other gram-negative bacteria such as Vibrio, Pseudomonas, or Escherichia coli38. It can result in increased morbidity and mortality, increased antibiotic resistance, increased healthcare costs, and an increased risk of outbreaks. Therefore, it is important to use reliable and correct methods for the detection and identification of A. hydrophila, such as molecular techniques, biochemical tests, and serological assays.
The comparative genomic approach was employed on Aeromonas in 2018 by Awan et al.39. Even though there were not enough complete genomes available at that time and most were still in the draft stage, they proved that some strains had been incorrectly classified as Aeromonas hydrophila. This might be because of using the 16S rRNA as a marker, which can still align the 4AK4 strain to the A. hydrophila clade in phylogeny. This incident supplies unequivocal proof that the 16S rRNA sequence cannot be used to name A. hydrophila or discriminate it from other species. In addition, the current study revealed that the strains NEB724, B11, and YL17 had previously been mistakenly recognized as A. hydrophila. The strain YL17's genome was published in 201640 while, the genomic sequences for NEB724 and B11 were both released in 2020 according to NCBI records. On the other hand, Aeromonas sp. 2692-1, 1805, and ASNIH4 were assigned to a particular species, namely, A. hydrophila.
Strain misidentification may have a significant impact on the results of diagnostic investigations concerned with microbial pathogens. In a previous study carried out by da Silva Filho et al.41 four misidentified A. hydrophila strains were eliminated from their analysis. Continuous updating of the NCBI database would reflect these rearrangements to avoid any ambiguity during routine BLAST searches, as well as primer or probe design for diagnostics or epidemiological applications.
Pathogenomics is a field of science that uses genomics research to assess the pathogenicity potential of bacteria. However, most of the published epidemiological studies consider only a few genes13,18,42. In the current study, 312 virulence genes were detected in the A. hydrophila pan-genome. The existence of these genes in A. hydrophile’s pan-genomes adds to the complexity of this significant disease-causing organism and makes it crucial to accurately diagnose the etiological agent. This all, in light of most of the virulence genes identified in the literature, was carried out on a former A. hydrophila SSU strain, which has been reclassified later as Aeromonas dhakensis19. The present investigation explored four genes (gmhB, cheD, speG, and nagL) in all strains of A. hydrophila. These genes show great similarity among the recognized A. hydrophila strains and significant dissimilarity among other genomes. Consequently, these uncovered genes may provide a potential genotyping tool for distinguishing A. hydrophila strains from other aeromonads.
The phylogenetic analysis of these genes has shown the same trend as ANI, suggesting a straightforward strategy for A. hydrophila based on single gene sequences rather than the MLST approach, or MLST combined with other methods as recommended by Beaz-Hidalgo et. al.14. Using a single, properly chosen gene for microbial typing has the advantages of being fast, cheap, and efficient. Furthermore, SNPs were proposed for accurate identification of Bacillus spp. responsible for food poisoning43. Similarly, the distinct SNPs discovered in the current study are suggested as a good starting point to develop a novel molecular typing method that precisely names A. hydrophila strains. Similar methods have been successfully applied for Salmonella investigations since some genes have been discovered as markers present in certain serovars44,45.
Conclusion
This work presents a recent comparative study of the accessible genomes of A. hydrophila. Using the most recent genomes and virulence factor databases. The study was expanded to find the pan-virulence genes and assess the pathogenic potential of A. hydrophila. Four distinct genes that could be used as molecular markers for A. hydrophila identification were discovered. These findings broaden our knowledge and serve as a starting point for an in-depth investigation of the pathogenicity and virulence of A. hydrophila. Most of the discovered genes engage in immune system modulation, microbe motility, or microbial secretion systems, which raises questions about their role in the pathogenesis of A. hydrophila in fish and human hosts.
Data availability
The datasets used in the investigation are accessible from the NCBI, and complete information, including the accession number and download links, is included in the supplementary Table S1. Any additional information requested is available upon request from the corresponding author.
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Acknowledgements
The authors want to thank the Faculty of Science at Alexandria University for the support and for using the institute's resources to conduct this work.
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Open access funding provided by The Science, Technology & Innovation Funding Authority (STDF) in cooperation with The Egyptian Knowledge Bank (EKB). No direct funding was received for this work.
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BA designed and planned the study. NAA and NMS helped in the initial stage of the work; BA conducted the analysis and wrote the first draft. RAM helped in the manuscript writing and reviewing. BA and ERE completed and finalised the manuscript. All authors read and approved the final manuscript.
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Abdella, B., Abozahra, N.A., Shokrak, N.M. et al. Whole spectrum of Aeromonas hydrophila virulence determinants and the identification of novel SNPs using comparative pathogenomics. Sci Rep 13, 7712 (2023). https://doi.org/10.1038/s41598-023-34887-1
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DOI: https://doi.org/10.1038/s41598-023-34887-1
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