| Literature DB >> 27066226 |
Yi-Ming Weng1, Man-Miao Yang1, Wen-Bin Yeh1.
Abstract
Taiwan, an island with three major mountain ranges, provides an ideal topography to study mountain-island effect on organisms that would be diversified in the isolation areas. Glaciations, however, might drive these organisms to lower elevations, causing gene flow among previously isolated populations. Two hypotheses have been proposed to depict the possible refugia for alpine organisms during glaciations. Nunatak hypothesis suggests that alpine species might have stayed in situ in high mountain areas during glaciations. Massif de refuge, on the other hand, proposes that alpine species might have migrated to lower ice-free areas. By sampling five sympatric carabid species of Nebria and Leistus, and using two mitochondrial genes and two nuclear genes, we evaluated the mountain-island effect on alpine carabids and tested the two proposed hypotheses with comparative phylogeographic method. Results from the phylogenetic relationships, network analysis, lineage calibration, and genetic structure indicate that the deep divergence among populations in all L. smetanai, N. formosana, and N. niitakana was subjected to long-term isolation, a phenomenon in agreement with the nunatak hypothesis. However, genetic admixture among populations of N. uenoiana and some populations of L. nokoensis complex suggests that gene flow occurred during glaciations, as a massif de refuge depicts. The speciation event in N. niitakana is estimated to have occurred before 1.89 million years ago (Mya), while differentiation among isolated populations in N. niitakana, N. formosana, L. smetanai, and L. nokoensis complex might have taken place during 0.65-1.65 Mya. While each of the alpine carabids arriving in Taiwan during different glaciation events acquired its evolutionary history, all of them had confronted the existing mountain ranges.Entities:
Keywords: Glacial refugia; Leistus; Nebria; massif de refuge; nunatak hypothesis
Year: 2016 PMID: 27066226 PMCID: PMC4768753 DOI: 10.1002/ece3.2006
Source DB: PubMed Journal: Ecol Evol ISSN: 2045-7758 Impact factor: 2.912
Figure 1Sampling locations of alpine carabids. Xueshan and Daxueshan are in Xueshan range; Nanhudashan, Hehuanshan, Guanyuan, and Tianchi are in central mountain range; Yushan is in Yushan range. Area in elevation above 2000 m is shaded.
Gene diversity and neutrality test of each carabid population (asterisk means the value statistically significant)
| Species | Population | Genes | N | Nh | Hd | 100 × | Tajima's D | Fu's Fs |
|---|---|---|---|---|---|---|---|---|
|
| Xueshan | COI | 12 | 7 | 0.86 | 0.53 | 1.15 | −1.02 |
| Complex | 16S | 11 | 1 | 0.00 | 0.00 | 0.00 | – | |
| Wingless | 11 | 1 | 0.00 | 0.00 | 0.00 | – | ||
| Hehuanshan | COI | 13 | 6 | 0.64 | 1.03 | −0.27 | 2.14 | |
| 16S | 11 | 2 | 0.33 | 0.06 | −0.10 | 0.36 | ||
| Wingless | 10 | 2 | 0.47 | 0.11 | 0.82 | 0.82 | ||
| Nanhudashan | COI | 4 | 2 | 0.50 | 0.23 | −0.75 | 1.71 | |
| 16S | 4 | 1 | 0.00 | 0.00 | 0.00 | – | ||
| Wingless | 4 | 1 | 0.00 | 0.00 | 0.00 | – | ||
| Daxueshan | COI | 5 | 4 | 0.90 | 0.22 | −0.17 | −1.65* | |
| 16S | 5 | 1 | 0.00 | 0.00 | 0.00 | – | ||
| Wingless | 5 | 2 | 0.60 | 0.14 | 1.22 | 0.63 | ||
| Yushan | COI | 12 | 11 | 0.98 | 1.01 | −0.08 | −4.40* | |
| 16S | 12 | 2 | 0.17 | 0.03 | −1.14 | −0.48 | ||
| Wingless | 12 | 2 | 0.30 | 0.07 | −0.19 | 0.30 | ||
|
| Xueshan | COI | 5 | 4 | 0.90 | 0.47 | −0.75 | −0.33 |
| 16S | 5 | 1 | 0.00 | 0.00 | 0.00 | – | ||
| Wingless | 4 | 1 | 0.00 | 0.00 | 0.00 | – | ||
| Nanhudashan | COI | 3 | 2 | 0.67 | 0.31 | 0.00 | 1.61 | |
| 16S | 3 | 2 | 0.67 | 0.26 | 0.00 | 1.06 | ||
| Wingless | 3 | 3 | 1.00 | 0.48 | 0.00 | −0.69 | ||
|
| Xueshan | COI | 10 | 4 | 0.53 | 0.12 | −1.67* | −1.34* |
| 16S | 10 | 1 | 0.00 | 0.00 | 0.00 | – | ||
| Wingless | 10 | 1 | 0.00 | 0.00 | 0.00 | – | ||
| Hehuanshan | COI | 7 | 2 | 0.29 | 0.04 | −1.01 | −0.09 | |
| 16S | 10 | 1 | 0.00 | 0.00 | 0.00 | – | ||
| Wingless | 6 | 2 | 0.53 | 0.38 | 1.12 | 2.50 | ||
| Yushan | COI | 10 | 3 | 0.51 | 0.09 | −0.69 | −0.59 | |
| 16S | 10 | 2 | 0.20 | 0.04 | −1.11 | −0.34 | ||
| Wingless | 10 | 2 | 0.20 | 0.05 | −1.11 | −0.34 | ||
|
| Xueshan | COI | 8 | 4 | 0.79 | 0.17 | −0.30 | −1.10 |
| 16S | 14 | 1 | 0.00 | 0.00 | 0.00 | – | ||
| Wingless | 13 | 4 | 0.62 | 0.23 | −0.06 | −0.63 | ||
| Nanhudashan | COI | 14 | 12 | 0.98 | 0.66 | 0.13 | −6.46* | |
| 16S | 15 | 2 | 0.13 | 0.03 | −1.16 | −0.65 | ||
| Wingless | 15 | 7 | 0.78 | 0.40 | 0.96 | −2.60* | ||
|
| Xueshan | COI | 2 | 2 | 1.00 | 0.47 | 0.00 | 1.10 |
| 16S | 1 | 1 | – | – | – | – | ||
| Wingless | 1 | 1 | – | – | – | – | ||
| Hehuanshan | COI | 12 | 6 | 0.82 | 0.30 | −0.21 | ||
| 16S | 12 | 1 | 0.00 | 0.00 | 0.00 | – | ||
| Wingless | 11 | 4 | 0.80 | 0.31 | 0.95 | −0.17 | ||
| Guanyuan | COI | 9 | 4 | 0.80 | 0.30 | 0.24 | 0.33 | |
| 16S | 9 | 1 | 0.00 | 0.00 | 0.00 | – | ||
| Wingless | 9 | 6 | 0.89 | 0.48 | 1.15 | −2.33* | ||
| Nanhudashan | COI | 9 | 2 | 0.22 | 0.10 | −1.51 | 1.32 | |
| 16S | 9 | 1 | 0.00 | 0.00 | 0.00 | – | ||
| Wingless | 9 | 4 | 0.69 | 0.25 | −0.36 | −1.04 | ||
| Yushan | COI | 10 | 4 | 0.64 | 0.31 | −0.77 | 0.62 | |
| 16S | 10 | 1 | 0.00 | 0.00 | 0.00 | – | ||
| Wingless | 7 | 5 | 0.90 | 0.55 | 0.13 | −1.45 | ||
| Tianchi | COI | 2 | 1 | 0.00 | 0.00 | 0.00 | – | |
| 16S | 3 | 2 | 0.67 | 0.12 | 0.00 | 0.20 | ||
| Wingless | 3 | 2 | 0.67 | 0.33 | 0.00 | 1.06 |
N, number of individuals; Nh, number of haplotypes; Hd, haplotype diversity. Significant values are indicated with an asterisk
Sequence variation component in each gene of each carabid taxon
| Percentage | Components | COI | 16S rDNA |
| 28S rDNA |
|---|---|---|---|---|---|
|
| Among populations | 0.78 | 0.94 | 0.85 | 0.88 |
| Within populations | 0.22 | 0.06 | 0.15 | 0.12 | |
|
| Among populations | 0.86 | 0.80 | 0.75 | 1.00 |
| Within populations | 0.14 | 0.20 | 0.25 | 0.00 | |
|
| Among populations | 0.91 | 0.98 | 0.69 | 1.00 |
| Within populations | 0.09 | 0.02 | 0.31 | 0.00 | |
|
| Among populations | 0.98 | 0.98 | 0.85 | 0.92 |
| Within populations | 0.02 | 0.02 | 0.15 | 0.08 | |
|
| Among populations | 0.39 | 0.87 | 0.17 | – |
| Within populations | 0.61 | 0.13 | 0.83 | – |
No variation was obtain.
Figure 2Phylogenetic tree and network analysis of each carabid species; (A) Leistus nokoensis complex; (B) L. smetanai; (C) Nebria formosana; (D) N. niitakana; and (E) N. uenoiana. Topology is shown in Bayesian inference with maximum‐parsimony and maximum‐likelihood bootstrap values (>50%) on nods.
Figure 3Strict molecular clock calculation based on mitochondrial genes of COI and 16S rDNA for each carabid species. Inferences were performed for each species independently and arranged based on the same timescale.
Figure 4Coalescent‐based extended Bayesian skyline plot of each carabid species. (A) Leistus nokoensis complex; (B) L. smetanai; (C) Nebria formosana; (D) N. niitakana; and (E) N. uenoiana.