| Literature DB >> 28587661 |
Jennifer L Morrow1, Aidan A G Hall1,2, Markus Riegler3.
Abstract
BACKGROUND: Obligate bacterial primary (P-) endosymbionts that are maternally inherited and codiverge with hosts are widespread across insect lineages with nutritionally restricted diets. Secondary (S-) endosymbionts are mostly facultative, but in some hosts, they complement P-endosymbiont function and therefore become obligate. Phylogenetic evidence exists for host switching and replacement of S-endosymbionts. The community dynamics that precede endosymbiont replacement and complementation have been little studied across host species, yet they are fundamental to the evolution of endosymbiosis.Entities:
Keywords: Arsenophonus; Carsonella; Core microbiota; Endosymbiont replacement; Enterobacteriaceae; Insect; Plant pathogenic bacteria; Psyllid; Sodalis; Symbiosis
Mesh:
Substances:
Year: 2017 PMID: 28587661 PMCID: PMC5461708 DOI: 10.1186/s40168-017-0276-4
Source DB: PubMed Journal: Microbiome ISSN: 2049-2618 Impact factor: 14.650
Experimental aims
| 1. | Ascertain the entire bacterial diversity and community composition of individual psyllid specimens from 25 psyllid species. |
| 2. | Demonstrate the presence of |
| 3. | Identify the dominant S-endosymbionts that may be complementing the role of |
| 4. | Establish the relative bacterial titre relationships of P- and S-endosymbionts across a subset of seven psyllid species. |
| 5. | Test the previously raised hypothesis that gall-forming species contain a lower diversity of endosymbionts because plant galls may be a more stable nutrient source than unmodified leaf tissue and, more generally, the impact of ecological niche on bacterial community structure. |
| 6. | Test if there are differences in S-endosymbiont incidence and prevalence within psyllid species across locations (including between native and invasive ranges). |
| 7. | Detect potential signatures of incipient symbiont complementation or replacement in terms of loss or acquisition of multiple S-endosymbionts. |
| 8. | Detect potential plant pathogens vectored by psyllid species. |
Fig. 1Schematic representation of the psyllid species included in this study. Current taxonomic classification to family level is shown, as are the number of populations collected and the ecological type of each species. Aphalaridae (highlighted in green) included in this study are associated with eucalypts; the species from the other families are not associated with eucalypts
Sampling metadata for the psyllid individuals of 25 species representing four of the eight families within Psylloidea
| Family | Species name | Ecology | Location (collection date) | Host plant | No. of individuals | |||
|---|---|---|---|---|---|---|---|---|
| Niche | Feeding | Female | Male | Nymph | ||||
| Aphalaridae |
| Lerp | Senescence | Mudgee; NSW (2015) |
| 3 | ||
| Black Mountain Road carpark, Canberra; ACT (2013) |
| 3 | ||||||
| Black Mountain Peninsula; ACT (2013) |
| 3 | ||||||
| Bruce Ridge Nature Reserve; ACT (2014) |
| 3 | ||||||
| Western Sydney U, Hawkesbury; NSW (2012) |
| 3 | ||||||
|
| Lerp | Senescence | Battunga Road, Echunga; SA (2013) |
| 3 | |||
| Callington; SA (2013) |
| 3 | ||||||
| Bunbury Road, Tintinara; SA (2013) |
| 3 | ||||||
| Tiver’s Road, Spence; SA (2013) |
| 3 | ||||||
| Hampton Road, Naracoorte; SA (2013) |
| 3 | ||||||
| Nolan’s Road, Naracoorte; SA (2013) |
| 3 | ||||||
| Echunga; SA (2013) |
| 1 | ||||||
|
| Lerp | Senescence | EucFACE, Richmond; NSW (2014) |
| 3 | |||
| Yellowmundee; NSW (2014) |
| 3 | ||||||
| Cronulla; NSW (2014) |
| 2 | 1 | |||||
| Rotary Park, Southwest Rocks; NSW (2013) |
| 3 | ||||||
|
| Lerp | Senescence | Western Sydney U, Hawkesbury; NSW (2014) |
| 3 | |||
| Macquarie Fields; NSW (2014) |
| 3 | ||||||
| Yellowmundee; NSW (2014) |
| 1 | ||||||
|
| Lerp | Senescence | Battunga Road, Echunga; SA (2013) |
| 1 | 2 | 2 | |
|
| Lerp | Senescence | Mary Lawson Wayside Rest, Finley; NSW (2013) |
| 1 | |||
| Bruce Ridge Nature Reserve; ACT (2014) |
| 3 | ||||||
|
| Lerp | Senescence | Doonside; NSW (2012) |
| 3 | |||
| Black Mountain CSIRO, Canberra; ACT (2014) |
| 3 | ||||||
| Western Sydney; NSW (2012) |
| 3 | ||||||
| GB | Lerp | Senescence | Rossmore Park; NSW (2013) |
| 3 | |||
| Western Sydney U, Hawkesbury; NSW (2014) |
| 3 | 2 | |||||
| Nurragingy Reserve; NSW (2013) |
| 3 | ||||||
| Dr Charles Mckay Reserve Blacktown; NSW (2013) |
| 3 | ||||||
|
| Lerp | Senescence | EucFACE, Richmond; NSW (2015) |
| 3 | |||
| Glen Helen; NT (2012) |
| 3 | ||||||
|
| Lerp | Senescence | EucFACE, Richmond; NSW (2012) |
| 3 | |||
|
| Lerp | Senescence | Ingleburn; NSW (2013) |
| 3 | |||
|
| Free-living | Flush | Tasman Peninsula; Tasmania (2012) |
| 3 | |||
|
| Free-living | Flush | Sao Pedro do Sul; Portugal (2011) |
| 3 | |||
| Oliveira de Azemeis; Portugal (2011) |
| 3 | ||||||
| Ponte de Lima; Portugal (2011) |
| 3 | ||||||
| Gois; Portugal (2011) |
| 3 | ||||||
| Tasman Peninsula; Tasmania (2012) |
| 3 | ||||||
| Western Sydney U, Hawkesbury; NSW (2012) |
| 2 | 1 | |||||
|
| Free-living | Flush | Albergaria-a-Velha; Portugal (2011) |
| 1 | 3 | ||
| Ponte de Lima; Portugal (2011) |
| 3 | ||||||
|
| Lerp | Senescence | Bowen Street Bus Terminal, Adelaide; SA (2013) |
| 1 | |||
| Edensor Park; NSW (2012) |
| 2 | 1 | |||||
| Western Sydney U, Hawkesbury; NSW (2015) |
| 3 | 2 | |||||
|
| Lerp | Flush | Mulgrave; NSW (2012) |
| 3 | |||
| East Market Street carpark, Richmond; NSW (2014) |
| 2 | 1 | |||||
| Coimbra; Portugal (2011) |
| 2 | ||||||
| Aveiro; Portugal (2011) |
| 3 | ||||||
| EucFACE, Richmond; NSW (2012) |
| 3 | ||||||
|
| Lerp | Flush | Howlong; NSW (2013) |
| 3 | |||
|
| Lerp | Flush | Mildura; VIC (2015) |
| 2 | |||
| Kinchega; NSW (2015) |
| 3 | ||||||
| Kinchega; NSW (2015) |
| 3 | ||||||
| Carsidaridae |
| Free-living | Senescence | Western Sydney U, Hawkesbury; NSW (2015) |
| 3 | 3 | |
| Psyllidae |
| Free-living | Flush | Yellowmundee; NSW (2015) |
| 3 | ||
| Triozidae |
| Free-living | Senescence | Tasman Peninsula; Tasmania (2012) |
| 1 | ||
| Bundoora; VIC (2012) |
| 3 | ||||||
|
| Gall | n/a | Douglas, Townsville; QLD (2014) |
| 4 | 3 | ||
|
| Gall | n/a | Mount Wilson; NSW (2015) |
| 3 | |||
|
| Gall | n/a | Gordon; NSW (2015) |
| 3 | |||
| Gall | n/a | Western Sydney U, Hawkesbury; NSW (2015) |
| 3 | ||||
|
| Gall | n/a | Kanapaha Plantation Gainesville; Florida (2014) |
| 3 | |||
n/a not available
Bacteria identified by 16S rRNA gene amplicon sequencing
| Species name | P-endosymbiont | Potential S-endosymbiont(s) | Facultative endosymbionts (potential reproductive manipulators) | Potentially transient or pathogenic bacteria |
|---|---|---|---|---|
| Class | Gammaproteobacteria (Halomonadaceae) | Gammaproteobacteria (Enterobacteriaceae + Coxiellaceae) | Alphaproteobacteria + Tenericutes (*) | Gammaproteobacteria + Tenericutes (*) + Firmicutes (#) |
|
| ||||
|
|
| OTU563559 (AN = 99%; full-length AN = 99%) | ||
|
|
| OTU563559 (AN = 99%; full-length AN = 99%) | ||
|
|
| OTU563559 (AN = 99%; full-length AN = 99%) |
| |
|
|
| OTU563559 (AN = 99%) | ||
|
|
| OTU563559 (AN = 99%; full-length AN = 99%) |
| |
|
|
| OTU563559 (AN = 99%) | ||
| GB |
| OTU563559 (AN = 99%; full-length AN = 99%) |
| |
|
|
| OTU16 (AN = 97%) |
| |
|
| ||||
|
|
| OTU86 (SP = 96%; full-length SP = 97%) |
| |
|
|
| OTU106 (SP = 96%) | ||
|
|
| OTU24 (SG = 96%) | ||
|
|
| OTU38 (SG = 95%) |
| |
|
| ||||
|
|
| OTU103 (SG = 93%) |
| |
|
|
| OTU112 (BP = 90%) | ||
|
|
| OTU62 (ME = 93%) |
| |
|
|
| OTU37 (ME = 91%) + OTU13 (ME = 92%) | ||
|
|
| OTU120 (CE = 92%) | ||
|
|
| OTU56 (WG = 87%) |
|
|
|
|
| OTU53 (ME = 92%) |
| |
|
|
| OTU9965 (BA = 89%) |
| |
|
| ||||
|
|
| OTU563559 ( |
| |
|
|
| OTU28 ( | ||
|
|
| OTU96731 ( | ||
|
| ||||
| Native (Tasmania) |
| OTU4333280 (CE = 100%) + OTU261110 ( | ||
| Invasive (Portugal) |
| OTU4333280 (CE = 100%) | ||
|
| ||||
| Native (Mulgrave, NSW) |
| OTU26 (SG = 93%) + OTU563559 (AN = 99%) + OTU49 ( | ||
| Native (Richmond, NSW) |
| OTU26 (SG = 93%) + OTU563559 (AN = 99%) + OTU49 ( |
| |
| Native (EucFACE, NSW) |
| OTU26 (SG = 93%) + OTU563559 (AN = 99%) + OTU49 ( |
| |
| Native (EucFACE, NSW) |
| OTU97 (SG = 92%) + OTU49 ( | ||
| Invasive (Portugal) |
| OTU26 (SG = 93%) + OTU49 ( |
| |
All psyllids harboured Carsonella and fixed S-endosymbionts, and 17% had facultative endosymbionts or transient/potentially pathogenic bacteria. All psyllids harboured abundant S-endosymbionts, many of which were difficult to classify to genus due to the short region of 16S rRNA gene sequenced and the similarity of the sequenced region across several insect endosymbiont taxa. The S-endosymbiont OTUs were grouped into Arsenophonus or Sodalis-like (based on >95% BLAST matches against the NCBI reference genomes database); matches lower than 95% were grouped as ‘unclassified Enterobacteriaceae’ with the closest reference genome BLAST match. NB In the last two columns, numbers in parentheses indicate the fraction of the total individuals that harboured the bacteria
Genome abbreviations: Arsenophonus nilaparvatae NZ_JRLH01000006 (AN), Sodalis glossinidius ‘morsitans’ NC_007712.1 (SG), Sodalis praecaptivus strain HS1 NC_007712.1 (SP), S-endosymbiont of Ctenarytaina eucalypti NC_018419.1 (CE), Candidatus Blochmannia pennsylvanicus str. BPEN NC_007292.1 (BP), Candidatus Moranella endobia PCVAL NC_021057.1 (ME), Buchnera aphidicola (Cinara tujafilina) NC_015662.1 (BA), Wigglesworthia glossinidia NC_016893 (WG), Diplorickettsia massiliensis NZ_AJGC01000002.1 (DM)
Fig. 2Microbial composition of the dominant OTUs detected in 191 individuals of 25 psyllid species (summarised by species). Carsonella (P-endosymbiont), various S-endosymbionts and potential reproductive manipulators were included; others including transient or pathogenic OTUs were grouped into ‘other’. Glycaspis brimblecombei and Ctenarytaina eucalypti were split into native and invasive samples because for these two species individuals from both native and invasive ranges were available
Fig. 3Bayesian phylogenetic tree of 16S rRNA gene sequences, including those acquired from amplicon sequencing of individuals from 25 psyllid species. This tree displays Gammaproteobacteria from the families Halomonadaceae (Carsonella sequences from this study highlighted in purple) and Enterobacteriaceae which includes the S-endosymbionts that were found in all individuals of a species (or in all individuals of the native range for C. eucalypti or G. brimblecombei) highlighted in orange, or not fixed within a species highlighted in green. Posterior probabilities are displayed at the node when >50%. Scale bar shows nucleotide substitutions per site. The complete phylogenetic tree with all 16S rRNA gene sequences of this study (including other Gamma- and Alphaproteobacteria) is shown in Additional file 8
Fig. 4Relative titres of P- and S-endosymbionts in Cardiaspina spp. determined by qPCR. Cq values for Carsonella, Arsenophonus and Sodalis were normalised to the EF1a host gene (see Additional file 8), and species means of endosymbiont copy number were plotted. Tukey’s post hoc tests were performed and the results displayed over each bar, demonstrating no significant difference between the titres of the P- and S-endosymbionts within and between four species, but significantly higher Carsonella titres for C. fiscella and C. maniformis than the other species. Cardiaspina albitextura was included to display relative Carsonella titre only; while Arsenophonus was present in each individual of C. albitextura based on amplicon sequencing data, it was not detected using the atpA qPCR primer set
Fig. 5Heatmap showing relative abundance >1% of OTUs labeled to genus or family level in each species. Each row represents a microbial OTU, and colour shading indicates the relative abundance according to the inset legend on the top right. Columns represent each psyllid species (C. eucalypti and G. brimblecombei samples were also divided into specimens of native and invasive populations) and were ordered by Euclidean hierarchical clustering. Class level designations for the microbial OTUs are presented on the left of the figure. Psyllid families are indicated by the coloured bar: Aphalaridae (green), Carsidaridae (blue), Psyllidae (yellow) and Triozidae (orange)
Fig. 6Principal coordinates analysis (PCoA) of three distance metrics: unweighted UniFrac, weighted UniFrac and Bray-Curtis, based on OTUs calculated at 97% similarity. Microbial communities of 191 psyllid individuals of 25 species are represented. Axes labels denote the percentage of variation that is contained in each principal coordinate; ellipses represent the standard deviation of the cluster centred on each ecological niche