| Literature DB >> 28458658 |
Emilie Talagrand-Reboul1,2, Frédéric Roger1, Jean-Luc Kimper1, Sophie M Colston3, Joerg Graf3, Fadua Latif-Eugenín4, Maria José Figueras4, Fabienne Petit5,6, Hélène Marchandin1,7, Estelle Jumas-Bilak1,2, Brigitte Lamy1,8.
Abstract
Aeromonas media is an opportunistic pathogen for human and animals mainly found in aquatic habitats and which has been noted for significant genomic and phenotypic heterogeneities. We aimed to better understand the population structure and diversity of strains currently affiliated to A. media and the related species A. rivipollensis. Forty-one strains were included in a population study integrating, multilocus genetics, phylogenetics, comparative genomics, as well as phenotypics, lifestyle, and evolutionary features. Sixteen gene-based multilocus phylogeny delineated three clades. Clades corresponded to different genomic groups or genomospecies defined by phylogenomic metrics ANI (average nucleotide identity) and isDDH (in silico DNA-DNA hybridization) on 14 whole genome sequences. DL-lactate utilization, cefoxitin susceptibility, nucleotide signatures, ribosomal multi-operon diversity, and differences in relative effect of recombination and mutation (i.e., in evolution mode) distinguished the two species Aeromonas media and Aeromonas rivipollensis. The description of these two species was emended accordingly. The genome metrics and comparative genomics suggested that a third clade is a distinct genomospecies. Beside the species delineation, genetic and genomic data analysis provided a more comprehensive knowledge of the cladogenesis determinants at the root and inside A. media species complex among aeromonads. Particular lifestyles and phenotypes as well as major differences in evolution modes may represent putative factors associated with lineage emergence and speciation within the A. media complex. Finally, the integrative and populational approach presented in this study is considered broadly in order to conciliate the delineation of taxonomic species and the population structure in bacterial genera organized in species complexes.Entities:
Keywords: Aeromonas; complex of species; integrative taxonomy; phylogeny; population study; recombination; speciation; taxogenomics
Year: 2017 PMID: 28458658 PMCID: PMC5394120 DOI: 10.3389/fmicb.2017.00621
Source DB: PubMed Journal: Front Microbiol ISSN: 1664-302X Impact factor: 5.640
Characteristics of the 41 strains affiliated to .
| A | River water | Environment | Czech republic (1991) | Sedlácek et al., | ||
| A | River biofilm (output WWTP) | Environment | Spain (2010) | Marti and Balcázar, | ||
| LL6-17C | A | River water (output WWTP) | Environment | Spain (2012) | This study | |
| SS1-15D | A | WWTP | Environment | Spain (2012) | This study | |
| CR4.2-17C | A | River water | Environment | Spain (2012) | This study | |
| A | Raw sewage | Environment | NA (NA) | Gao et al., | ||
| A | Fish (infected) | Animal | France (1967-1974) | Popoff and Véron, | ||
| A | Snail | Animal | France (1995) | Roger et al., | ||
| AK208 | A | Snail | Animal | France (1995) | This study | |
| AK210 | A | Snail | Animal | France (1995) | This study | |
| A | Crab | Animal | Norway (1998) | Granum et al., | ||
| R1 | A | Salmon | Animal | Spain (2007) | This study | |
| R100 | A | Trout | Animal | Spain (2007) | This study | |
| 417-16G | A | Mussel | Animal | Spain (2011) | This study | |
| M2C164 = M2C A28 | A | Copepod | Animal | France (2012) | This study | |
| M2C185 = M2C A42 | A | Copepod | Animal | France (2012) | This study | |
| M2C205 = M2C A47 | A | Copepod | Animal | France (2012) | This study | |
| A | Human diarrheic stool | Clinical | Spain (1992) | Mosser et al., | ||
| BVH17 | A | Human urine (healthy carriage) | Clinical | France (2006) | This study | |
| A | Human stool (healthy carriage) | Clinical | France (2006) | Roger et al., | ||
| ADV137a | A | Human respiratory tract (near-drowning) | Clinical | France (2010) | This study | |
| B | River water (fish farm effluent) | Environment | UK (1980) | Allen et al., | ||
| B | River water (fish farm pond) | Environment | UK (1981) | Allen et al., | ||
| T41-3 | B | Soil | Environment | Spain (2010) | This study | |
| T41-7 | B | Soil | Environment | Spain (2010) | This study | |
| RT10-17Ga | B | River water | Environment | Spain (2012) | This study | |
| RT11-17Ga | B | River water | Environment | Spain (2012) | This study | |
| LL4.4-18D | B | River water (input WWTP) | Environment | Spain (2012) | This study | |
| SEL1-18A | B | WWTP | Environment | Spain (2012) | This study | |
| CR4-18pb | B | River water | Environment | Spain (2012) | This study | |
| B | River water | Environment | Japan (2013) | Kenzaka et al., | ||
| B | River water | Environment | Japan (2013) | Kenzaka et al., | ||
| B | Lake water | Environment | China (2003) | Chai et al., | ||
| B | Fish (infected) | Animal | France (1967-1974) | Popoff and Véron, | ||
| AK207 | B | Snail | Animal | France (1995) | This study | |
| B | Snail | Animal | France (1995) | Roger et al., | ||
| B | Oyster ( | Animal | Spain (2002) | Miñana-Galbis et al., | ||
| BVH83 | B | Human urine (healthy carriage) | Clinical | France (2006) | This study | |
| D84402 | B | Human diarrheic stool | Clinical | Spain (2012) | This study | |
| C | Koi carp | Animal | Australia (2001) | Carson et al., | ||
| 1086C = CECT 8838 = LMG 28708 | C | Human diarrheic stool | Clinical | Spain (2010) | This study |
Several strains were wrongly labeled at the time of their isolation but all the 41 strains belonged to the Media SC on the basis of gyrB sequences that is robust enough for their affiliation within the genus Aeromonas, as explained in the main text.
MLP, Multi-Locus Phylogeny; NA, Not available; WWTP, Waste water treatment plant.
Strains studied only by genetic and genomic analysis.
Obtained from the EMBL Nucleotide Sequence Database.
Obtained from GenBank, National Center for Biotechnology Information.
Figure 1Unrooted Maximum-Likelihood tree based on concatenated sequences of 16 housekeeping gene fragments (9,427 nt.) from 3 MLST schemes. The tree shows the phylogenetic structure of the studied Media species complex population and the relative placement of strains to other recognized species in the genus. The horizontal lines represent genetic distance, with the scale bar indicating the number of substitutions per nucleotide position. The numbers at the nodes are support values estimated with 100 bootstrap replicates. Only bootstrap values ≥70 are indicated. The following characteristics are indicated for strains affiliated to A. media from left to right: (i) DL-lactate utilization, (ii) presence/absence of a 3 amino acid deletion (p.G85_G87del†), corresponding to a deletion of 9 nucleotides (c.3357226_3357234del††), (iii) number of rrn operons, (iv) presence/absence of 16S rRNA gene sequences S15 and/or S21 (corresponding to PCR-TTGE bands No. 15 and/or No. 21) revealed either by analysis of WGS or PCR-TTGE pattern, (v) presence/absence of DNA fragment of about 400 kb in PFGE I-CeuI pattern. The type strain of Aeromonas fluvialis was not included in the phylogenetic tree either because we failed to amplify the locus ppsA. This species did not group with Media complex in a 7 gene (atpD, dnaJ, dnaX, gyrA, gyrB, recA, rpoD)-based tree. *DL-lactate utilization or absence inferred from genomic analysis; +, positive; −, negative; ns, not studied. †position on the chaperone protein DnaJ sequence of A. hydrophila subsp. hydrophila ATCC 7966T (GenBank ABK39448.1). ††position on the circular chromosome sequence of A. hydrophila subsp. hydrophila ATCC 7966T (NCBI Reference Sequence NC_008570.1).
Genetic diversity, phylogenetic discrepancies in single locus phylogeny (SLP) analysis and ClonalFrame analysis of bacteria in the .
| 18 | 7 | 0.9810 | AH31 (clade | 10 | 2 | 0.9020 | − | 30 | 8 | 0.9768 | ||
| 20 | 6 | 0.9952 | − | 13 | 7 | 0.9477 | BVH83, CECT 4232T, RT10-17Ga, CECT 7111, LL4.4-18D (clade A) | 34 | 13 | 0.9866 | ||
| 20 | 5 | 0.9905 | − | 12 | 16 | 0.9739 | − | 34 | 19 | 0.9902 | ||
| 20 | 12 | 0.9952 | AK202 (clade | 12 | 9 | 0.9150 | − | 34 | 16 | 0.9829 | ||
| 19 | 10 | 0.9905 | LMG 26323 (clade B) | 8 | 3 | 0.7516 | − | 29 | 12 | 0.9512 | ||
| 18 | 7 | 0.9810 | − | 12 | 4 | 0.9346 | − | 31 | 11 | 0.9817 | ||
| 8 | 6 | 0.7190 | R100 (clade | 12 | 3 | 0.9346 | − | 22 | 8 | 0.9159 | ||
| 21 | 7 | 1.0000 | − | 12 | 6 | 0.9346 | − | 35 | 12 | 0.9878 | ||
| 21 | 7 | 1.0000 | − | 10 | 8 | 0.8954 | − | 33 | 12 | 0.9805 | ||
| 21 | 14 | 1.0000 | − | 12 | 11 | 0.9346 | − | 35 | 19 | 0.9878 | ||
| 20 | 12 | 0.9952 | AK202 (clade B) | 10 | 3 | 0.9150 | − | 32 | 14 | 0.9829 | ||
| 19 | 7 | 0.9905 | − | 10 | 6 | 0.9216 | LL4.4-18D (clade A) | 31 | 11 | 0.9829 | ||
| 16 | 3 | 0.9667 | − | 8 | 4 | 0.8301 | − | 23 | 6 | 0.9415 | ||
| 19 | 8 | 0.9905 | − | 11 | 5 | 0.9085 | − | 32 | 12 | 0.9805 | ||
| 14 | 4 | 0.9381 | AK202, BVH17 (clade B) | 9 | 4 | 0.8889 | RT10-17Ga | 24 | 7 | 0.9512 | ||
| 19 | 29 | 0.9905 | ADV137a (clade | 12 | 22 | 0.9477 | LL4.4-18D | 33 | 34 | 0.9878 | ||
| Mutation events | 55 | 3 | 9 | |||||||||
| Recombination events | 10 | 33 | 56 | |||||||||
| Substitutions introduced by recombination | 95 | 126 | 216 | |||||||||
| No of sites without recombination | 7364 (83.1% of the sequence length) | 2880 (32.5% of the sequence length) | 1744 (19.7% of the sequence length) | |||||||||
| ρ/θ | 0.097 (0.094–0.099) | 9.4 (9.4–9.4) | 6.5 (6.5–6.5) | |||||||||
| r/m | 0.89 (0.87–0.90) | 37 (36–40) | 23 (23–24) | |||||||||
ρ/θ, relative rate of recombination and mutation;
r/m, relative effect of recombination and mutation;
Phylogenetic discrepancy without horizontal gene transfer event detected by RDP software.
Measured between each isolate of each lineage (or the whole population) and their most recent common ancestor.
The numbers in brackets are 95% confidence intervals.
Figure 2Neighbor-networks graph based on the concatenated sequences of the 16 housekeeping gene fragments (8,865 nucleotides), showing putative recombination events between 41 strains affiliated to . A network-like graph indicates recombination events.
Average Nucleotide Identity (ANI) and .
| 1- | 61.7% | 79.2 | 73.2 | 77.4 | 68.0 | 53.7 | 56.6 | 54.3 | 53.6 | 54.1 | 52.9 | 52.9 | 60.6 | 60.1 | ||
| 2- BVH40 | 61.4% | 74.1 | 78.4 | 68.2 | 54.1 | 56.9 | 54.6 | 54.2 | 54.6 | 53.0 | 53.0 | 61.2 | 61.1 | |||
| 3- AK202 | 61.3% | 73.6 | 65.1 | 57.4 | 60.5 | 57.8 | 57.0 | 57.5 | 56.5 | 56.5 | 60.0 | 60.5 | ||||
| 4- | 61.3% | 67.5 | 54.5 | 57.2 | 55.2 | 54.2 | 54.9 | 53.3 | 53.3 | 60.5 | 60.2 | |||||
| 5- | 62.0% | 53.7 | 55.3 | 53.9 | 53.2 | 54.0 | 53.3 | 53.3 | 61.0 | 60.6 | ||||||
| 6- | 61.3% | 74.9 | 78.9 | 80.3 | 79.6 | 78.8 | 78.7 | 57.2 | 57.0 | |||||||
| 7- AK211 | 61.1% | 74.9 | 74.9 | 76.7 | 74.7 | 74.6 | 57.9 | 57.5 | ||||||||
| 8- | 61.1% | 77.9 | 83.8 | 79.2 | 79.2 | 57.5 | 57.0 | |||||||||
| 9- | 61.6% | 78.6 | 78.5 | 78.5 | 57.0 | 56.8 | ||||||||||
| 10- | 60.7% | 79.5 | 79.4 | 57.4 | 57.2 | |||||||||||
| 11– | 61.0% | 100.0 | 57.4 | 56.8 | ||||||||||||
| 12– | 61.0% | 57.3 | 56.7 | |||||||||||||
| 13- 1086C | 62.2% | 81.9 | ||||||||||||||
| 14- | 61.8% | |||||||||||||||
ANI values are displayed in bold in the lower triangle and isDDH values in the upper triangle. The isDDH values displayed are the upper limits of the 95% confidence intervals. Guanine + cytosine content is indicated for each genome (G + C content %).
Figure 3Venn diagram representing the core-genome of . The conserved specific genes are indicated for each lineages, and genes likely associated to environmental adaptation and/or change are colored.