| Literature DB >> 28387233 |
Donna Lisa De-Silva1, Luísa L Mota2, Nicolas Chazot1,3, Ricardo Mallarino4, Karina L Silva-Brandão5, Luz Miryam Gómez Piñerez6,7, André V L Freitas2, Gerardo Lamas8, Mathieu Joron9, James Mallet4, Carlos E Giraldo6,10, Sandra Uribe6, Tiina Särkinen11, Sandra Knapp12, Chris D Jiggins13, Keith R Willmott14, Marianne Elias1.
Abstract
The Neotropics harbour the most diverse flora and fauna on Earth. The Andes are a major centre of diversification and source of diversity for adjacent areas in plants and vertebrates, but studies on insects remain scarce, even though they constitute the largest fraction of terrestrial biodiversity. Here, we combine molecular and morphological characters to generate a dated phylogeny of the butterfly genus Pteronymia (Nymphalidae: Danainae), which we use to infer spatial, elevational and temporal diversification patterns. We first propose six taxonomic changes that raise the generic species total to 53, making Pteronymia the most diverse genus of the tribe Ithomiini. Our biogeographic reconstruction shows that Pteronymia originated in the Northern Andes, where it diversified extensively. Some lineages colonized lowlands and adjacent montane areas, but diversification in those areas remained scarce. The recent colonization of lowland areas was reflected by an increase in the rate of evolution of species' elevational ranges towards present. By contrast, speciation rate decelerated with time, with no extinction. The geological history of the Andes and adjacent regions have likely contributed to Pteronymia diversification by providing compartmentalized habitats and an array of biotic and abiotic conditions, and by limiting dispersal between some areas while promoting interchange across others.Entities:
Mesh:
Year: 2017 PMID: 28387233 PMCID: PMC5384087 DOI: 10.1038/srep45966
Source DB: PubMed Journal: Sci Rep ISSN: 2045-2322 Impact factor: 4.379
List of the species in the genus Pteronymia, including revised status.
| Previous name | Molecular data | Morphological data | Biogeographical area | Mean elevation [95% range] (m) | |
|---|---|---|---|---|---|
| x | A | 1100 [1050–1200] | |||
| x | x | ABCE | 693 [50–1450] | ||
| x | I | 1235 [1100–1490] | |||
| x | x | CDE | 1933 [800–3000] | ||
| x | x | CDI | 1337 [750–1860] | ||
| x | x | CE | 1227 [300–2000] | ||
| x | x | ACDE | 1365 [900–2060] | ||
| x | D | 1719 [1300–2970] | |||
| x | x | H | 910 [100–1700] | ||
| x | x | AE | 776 [80–1455] | ||
| x | x | AB | 386 [20–825] | ||
| x | x | H | 553 [30–1250] | ||
| x | x | F | 632 [182–1350] | ||
| x | x | A | 1455 [1110–2060] | ||
| x | AC | 870 [450–1000] | |||
| x | x | C | 950 [500–1000] | ||
| x | C | 1230 [800–1400] | |||
| x | x | C | 1929 [1500–2250] | ||
| x | x | ACDE | 1474 [600–2400] | ||
| x | x | CE | 1659 [1200–2100] | ||
| x | x | ACE | 1012 [170–1925] | ||
| x | x | CE | 1088 [800–1400] | ||
| x | x | A | 1198 [500–1575] | ||
| x | x | C | 1707 [1380–2000] | ||
| x | x | AB | 257 [30–700] | ||
| x | x | D | 1403 [1000–1525] | ||
| x | x | CE | 1992 [1250–2650] | ||
| x | x | E | 900 [900–900] | ||
| x | x | CDE | 1446 [600–2500] | ||
| x | x | A | 842 [200–2060] | ||
| x | I | 1040 [1040–1040] | |||
| x | x | ACE | 1104 [350–2060] | ||
| x | C | 1500 [1300–1800] | |||
| x | x | BFG | 389 [65–1050] | ||
| x | x | A | 998 [210–1500] | ||
| x | x | FG | 332 [100–800] | ||
| x | x | CD | 2091 [1700–2300] | ||
| x | x | D | 1265 [635–1500] | ||
| x | x | A | 1544 [1100–2300] | ||
| x | x | CD | 1667 [800–2075] | ||
| x | x | CDE | 1670 [790–2400] | ||
| x | x | C | 1184 [1000–1350] | ||
| x | x | CDE | 1784 [1200–2400] | ||
| x | x | F | 777 [100–1350] | ||
| x | x | CE | 1662 [1000–2400] | ||
| x | x | C | 1729 [1300–2150] | ||
| x | x | F | 398 [100–900] | ||
| x | x | CD | 1784 [700–2500] | ||
| x | x | CE | 1473 [635–2000] | ||
| x | x | E | 1730 [1730–1730] | ||
| x | x | C | 1765 [850–2530] | ||
| x | x | C | 1898 [1700–2030] | ||
| x | x | A | 656 [500–700] |
Availability of molecular and morphological data, distribution area and elevation mean and 95% range are reported for each species.
Comparison of our estimates of ages of Solanaceae lineages with those of Särkinen et al. 43.
| Solanaceae clades | Age estimates This study | Age estimates Särkinen |
|---|---|---|
| Stem of Solanaceae* | 64.0 my [48–83] | 49my [46–54] |
| Crown of Solanaceae | 42.2 my [26.8–55.2] | 30.3 my [26.3–34.0] |
| Crown of “x = 12” clade (MRCA | 39.5 my [21.9–44.4] | 23.7 my [23.0–25.7] |
| Crown of | 20.9 my [14.5–29.5] | 15.6 my [13.1–17.5] |
| Stem of | 19.0 my [11.5–25] | 13 my [10–16] |
| Stem of | 17.0 my [7–24] | 13 my [9–19] |
| Stem of | 10.5 my [5–14] | 7 my [4–10] |
*Ages used as calibration in the Pteronymia phylogeny.
Figure 1BEAST dated species-level phylogeny of the genus Pteronymia and outgroups, based on molecular and morphological characters.
Main clades and secondary calibration points based on butterfly (red circles) and host-plant ages (green circles) are indicated and corresponding age priors are shown in the table inserted in the figure. The figure was generated with FigTree (http://tree.bio.ed.ac.uk/software/figtree/) and edited with Adobe Illustrator 4 (http://www.adobe.com/uk/products/illustrator.html). Butterfly pictures were taken by Keith Willmott and edited in Adobe Photoshop CS4 (www.adobe.com/products/photoshop/) and correspond to butterfly names in red in adjacent phylogeny.
Figure 2Biogeographical regions used in the DEC and SDEC models for reconstruction of ancestral areas and the dispersal probability matrices for the different time slices.
Species richness in each areas are shown in the circles. The map was generated using ArcGIS 9.3 (http://www.edit.com/software/arcgis/), and edited with Adobe Illustrator 4 (http://www.adobe.com/uk/products/illustrator.html).
Figure 3RASP historical biogeography inference (best maximum likelihood estimates on the MCC tree).
Major paleoenvironmental events are indicated by large coloured rectangles (light pink: drainage of the Pebas system; light yellow: hypothesized closure of the Isthmus of Panama). Colours of the little squares at the node and tips of the tree correspond to colours of the biogeographical areas, as indicated in the map inserted (taken from Fig. 2). The figure was generated with R (https://cran.r-project.org/) and edited with Adobe Illustrator 4 (http://www.adobe.com/uk/products/illustrator.html).
Maximum likelihood estimates of δ for the mean and boundaries of the 95% elevational range, for the 100-tree posterior distribution (average values ± standard deviation), and for the MCC tree.
| Trees | Mean Elevation | 95% lower boundary | 95% upper boundary | |
|---|---|---|---|---|
| δ | 1.85 ± 0.60 | 2.96 ± 0.17 | 2.89 ± 0.23 | |
| Posterior | LRT | 1.36 ± 1.63 | 5.72 ± 1.89 | 5.26 ± 2.62 |
| distribution | p-value | 0.377 ± 0.250 | ||
| % trees p-value < 0.05 | 4 | 87 | 70 | |
| δ | 1.55 | 2.99 | 2.86 | |
| MCC | LRT | 0.625 | 5.16 | 3.10 |
| P-value | 0.429 | 0.078 |
Likelihood Ratio Tests values when compared with the null model (δ = 1), corresponding p-values and fraction of trees for which δ is significantly different from 1 are reported.
Figure 4Ancestral reconstruction of the mean and boundaries of the 95% elevational range (left: lower boundary, middle: upper boundary, right: mean).
For the lower and upper boundaries of the elevational range, trees were rescaled according to the δ value inferred (Table 2). The figure was generated with R (https://cran.r-project.org/).
Models of time-dependent diversification fitted on 100 trees from the posterior distribution, ranked by increasing AIC score.
| Model | Par | logL | AIC | ΔAIC | λ | α | μ | ß |
|---|---|---|---|---|---|---|---|---|
| BVAR - DCST | 3 | 251.86 (0.571) | 2.00 | 0.161 (0.001) | 0.110 (0.003) | 5.00E-08 (5.00E-08) | ||
| BCST | 1 | 252.79 (0.516) | 2.93 | 0.233 (0.001) | ||||
| BVAR - DVAR | 4 | 253.86 (0.571) | 4.00 | 0.161 (0.001) | 0.110 (0.003) | 5.00E-08 (5.00E-08) | ||
| BCST - DCST | 2 | 254.79 (0.516) | 4.93 | 0.233 (0.001) | <1.00E-08 (<1.00E-08) | |||
| BCST - DVAR | 3 | 256.79 (0.516) | 6.93 | 0.233 (0.001) | <1.00E-08 (<1.00E-08) | 0.005 (2.00E-04) |
Mean values of parameters are indicated followed by the standard deviation in brackets. BCST = constant speciation, BVAR = time-dependent speciation, DCST = constant extinction, DVAR time-dependent extinction. logL = likelihood of the model, AIC = AIC score, ΔAIC = difference of AIC between the each model and the best fitting model, λ = speciation rate at present, α = coefficient of time variation of the speciation rate, μ = extinction rate at present, ß = coefficient of time variation of the extinction rate.
Figure 5Speciation rate through time estimated by the best fitting model of diversification (Table 4).
The model was fitted on the MCC tree and on 100 trees. The dotted line corresponds to the speciation rate of the MCC tree. The plain line corresponds to the mean speciation rate from the 100 trees, and dashed lines correspond to the 95% confidence interval. The figure was generated with R (https://cran.r-project.org/).