| Literature DB >> 33315074 |
Anabela Cardoso1, Jesús Gómez-Zurita1.
Abstract
Recent studies suggest that endosymbionts of herbivore insects can be horizontally transferred to other herbivores feeding on the same host plants, whereby the plant acts as an intermediate stage in the chain of transmission. If this mechanism operates, it is also expected that insect communities sharing the same host plant will have higher chances to share their endosymbionts. In this study, we use a high-throughput 16S rRNA metabarcoding approach to investigate the presence, diversity, and potential sharing of endosymbionts in several species of leaf beetles (Coleoptera: Chrysomelidae) of a local community specialized on an alder diet in North America. Rickettsia and Wolbachia were predominant in the sample, with strong evidence for each species having their own dominant infection, of either or both types of bacteria. However, all species shared a much lower proportion of a particular Wolbachia type, compatible with the same strain dominant in one of the species of leaf beetles. Crucially, the same 16S rRNA haplotype of Wolbachia was found on alder leaf extracts. The combined evidence and the absence of this strain in a syntopic species of leaf beetle feeding on a different host plant support the hypothesis that at least the initial stages of the mechanism that would allow horizontal transmission of endosymbionts across species feeding on the same plant is possible. The accessibility and characteristics of endosymbiont associations of this system make it suitable for deeper analyses of their diversity and transmission in natural conditions.Entities:
Keywords: zzm321990 Rickettsiazzm321990 ; zzm321990 Wolbachiazzm321990 ; biodiversity; natural transmission; trophic network
Mesh:
Substances:
Year: 2020 PMID: 33315074 PMCID: PMC7734963 DOI: 10.1093/ee/nvaa111
Source DB: PubMed Journal: Environ Entomol ISSN: 0046-225X Impact factor: 2.377
Fig. 1.Geographic location of the study sites. Locality codes and collection data are the same given in Table 1.
Sampling localities, species studied, and number of individuals
| Code | Locality | Species |
|
|---|---|---|---|
| A | Franklin Co., Hough Brook, 44.43498N 73.95645W, 462 m, 26.vi.2015 |
| 1 |
| B | Essex Co., Frenchs Brook, 44.42424N 73.91965W, 519 m, 2.vii.2015 |
| 2 |
|
| 2 | ||
|
| 3 | ||
|
| 1 | ||
|
| 3 | ||
| C | Essex Co., Ausable River, Flume Trail system, 44.36617N 73.84258W, 344 m, 2.vii.2015 |
| 1 |
|
| 1 | ||
|
| 2 | ||
|
| 1 | ||
|
| 2 |
Parameters of 16S rDNA library synthesis based on the Bioanalyzer results and of the sequence-filtering procedure with DADA2 (Callahan et al. 2016)
| Species | Ind./Loc. | Size (bp) | Conc. (ng/μl) | Input | Filtered | denoisedF | denoisedR | merged | nochim | contamination | useful |
|---|---|---|---|---|---|---|---|---|---|---|---|
|
| Ai07/B | 602 | 6.23 | 1056929 | 678331 | 678209 | 678263 | 677441 | 676501 | 676152 | 349 |
| Ai15/B | 606 | 9.81 | 1081656 | 725776 | 725673 | 725690 | 725386 | 724458 | 724443 | 15 | |
| Ai25/C | 595 | 10.72 | 951669 | 614157 | 613996 | 614064 | 613605 | 612590 | 612488 | 102 | |
|
| Aa03/B | 603 | 7.29 | 826142 | 501981 | 501795 | 501188 | 497217 | 474478 | 28477 | 446001 |
| Aa09/B | 596 | 4.70 | 1024015 | 598344 | 598131 | 598230 | 591208 | 565220 | 58850 | 506370 | |
|
| Ca01/B | 607 | 12.11 | 564561 | 382351 | 382290 | 382284 | 382220 | 381635 | 381620 | 15 |
| Ca02/B | 601 | 11.44 | 964454 | 656655 | 656515 | 656593 | 656429 | 655748 | 655669 | 79 | |
| Ca12/B | 598 | 10.02 | 965457 | 553102 | 553038 | 553039 | 552928 | 552377 | 552299 | 78 | |
| Cc18/C | 599 | 15.88 | 672008 | 427249 | 427158 | 427176 | 426938 | 426468 | 426348 | 120 | |
|
| Cc11/A | 599 | 14.87 | 936424 | 615162 | 614991 | 614941 | 613746 | 610359 | 610221 | 138 |
| Cc05/B | 603 | 13.70 | 715138 | 452144 | 452059 | 452106 | 451978 | 450965 | 450362 | 603 | |
| Cc16/C | 599 | 16.31 | 762414 | 500996 | 500665 | 500817 | 499557 | 498435 | 498286 | 149 | |
| Cc17/C | 599 | 15.81 | 812653 | 534961 | 534884 | 534925 | 534765 | 534192 | 534142 | 50 | |
|
| Cp23/C | 598 | 14.51 | 1167727 | 778026 | 776950 | 777918 | 776362 | 771435 | 770544 | 891 |
|
| Cm04/B | 597 | 9.80 | 587430 | 336105 | 335993 | 336048 | 334912 | 333480 | 222473 | 111007 |
| Cm10/B | 592 | 11.53 | 1102771 | 649385 | 649024 | 649258 | 647791 | 645460 | 1540 | 643920 | |
| Cm13/B | 596 | 10.46 | 907151 | 548158 | 548077 | 548052 | 547922 | 547054 | 546840 | 214 | |
| Cm19/C | 593 | 6.99 | 881222 | 489797 | 489600 | 489743 | 386794 | 382157 | 1892 | 380265 | |
| Cm20/C | 592 | 2.74 | 1112097 | 643667 | 643533 | 643596 | 533831 | 496570 | 89243 | 407327 |
Fig. 2.Taxonomic diversity and abundance of nonendosymbiotic bacteria deduced from 16S rRNA haplotypes from the libraries of four species of the study. The samples of Calligrapha alni and Ca. philadelphica only yielded sequences of Rickettsia and Wolbachia and are not shown here. Frequency axes apply to Chrysomela mainensis and Altica ambiens (left) and to Ca. confluens and Alnus incana (right).
Fig. 3.Unrooted statistic parsimony networks of 16S rRNA haplotypes of Rickettsia (a) and Wolbachia (b) obtained for four species of alder specialists of the Chrysomelidae. Each colored node represents an observed haplotype and its code and absolute frequency are given, and the size of the node is proportional to the order of magnitude of this frequency. Edges represent mutational steps and small black circles missing intermediate states.
Fig. 4.Schematic representation of endosymbiont diversity and shared associations of Rickettsia (R haplotypes) and Wolbachia (W haplotypes) among alder specialists of the study. Haplotype W1 of Wolbachia is shared among all species, including samples of the host plant, Alnus incana, and haplotype R1 of Rickettsia was detected in the three of the studied genera of Chrysomelidae. [Pictures used with permission from the authors: see Acknowledgments.]