| Literature DB >> 26798320 |
José A Jurado-Rivera1, Eduard Petitpierre2.
Abstract
The taxonomic circumscription of the large and diverse leaf beetle genus Chrysolina Motschulsky is not clear, and its discrimination from the closely related genus Oreina Chevrolat has classically been controversial. In addition, the subgeneric arrangement of the species is unstable, and proposals segregating Chrysolina species into new genera have been recently suggested. In this context, the availability of a phylogenetic framework would provide the basis for a stable taxonomic system, but the existing phylogenies are based on few taxa and have low resolution. In the present study we perform a phylogenetic analysis based on mitochondrial (cox1 and rrnL) and nuclear (H3) DNA sequences from a sample of fifty-two Chrysolina species representing almost half of the subgeneric diversity of the group (thirty out of sixty-five subgenera) and most of the morphological, ecological and karyological variation in the genus. In addition, five Oreina species from two subgenera have also been analysed. The resulting phylogeny is used to evaluate some of the most relevant taxonomic hypotheses for Chrysolina, and also to reconstruct its ancestral host plant associations in a Bayesian framework. Our findings support the paraphyly of Chrysolina as currently defined due to the inclusion of Oreina, the monophyly of the Chrysolina (plus Oreina) species including the divergent Chrysolina (Polysticta) vigintimaculata (Clark, 1864), and enable inferences of deep-level evolutionary relationships among the studied subgenera. The plant family Lamiaceae is inferred as the ancestral host of the study group, whose evolution is characterized by continuous host-shifting among pre-existing host plant families. Some Chrysolina clades include mixtures of species with different levels of diet breadth, indicating that niche width has varied through time.Entities:
Keywords: Chrysolina; Chrysomelidae; Coleoptera; H3; Insect-plant interaction; Oreina; Phylogeny; cox1; rrnL
Year: 2015 PMID: 26798320 PMCID: PMC4714339 DOI: 10.3897/zookeys.547.6018
Source DB: PubMed Journal: Zookeys ISSN: 1313-2970 Impact factor: 1.546
Studied taxa, sources, host plants and GenBank accession numbers. Species groups defined by Bourdonné and Doguet (1991) are also indicated. a: Baselga and Novoa (2006), b: Bieńkowski 2010, c: Bieńkowski 2011, d: Bourdonné 2005, e: Bourdonné and Doguet 1991, f: Cobos 1953, g: Garin et al. 1999, h: Jolivet and Petitpierre 1976, i: Jolivet et al. 1986, j: Koch 1992, k: Lopatin and Mikhailov 2010, l: Mikhailov 2006, m: Petitpierre 1981, n: Rizza and Pecora 1980, o: Vela and Bastazo 1999.
| Species | Source | Host(s) | Host(s) references | cox1 | rrnL | H3 | |
|---|---|---|---|---|---|---|---|
| SE Tuva, Siberia, Russia | b | ||||||
| Murcia, Spain | i | 2 | |||||
| Almuñecar, Spain | b, h | 2 | |||||
| Ticino, Switzerland | b, j | 9 | |||||
| Balearic Islands, Spain | h | 2 | |||||
| Canary Islands, Spain | h | 2 | |||||
| Barcelona, Spain | b | 9 | |||||
| Altai, Siberia, Russia | 2 | ||||||
| Granada, Spain | o | 1 | |||||
| SE Tuva, Siberia, Russia | c | ||||||
| Canary Islands, Spain | e | 2 | |||||
| Granada, Spain | h | 3 | |||||
| Mundybash, Kemerovskaya oblast’, Russia | b | 9 | |||||
| Lleida, Spain | h, i | 2 | |||||
| Girona, Spain | h, i | 2 | |||||
| Lleida, Spain | h | 9 | |||||
| Canary Islands, Spain | h | 2 | |||||
| Lleida, Spain | b | 10 | |||||
| Ust’-Koksa, Altai Republic, Russia | c | ||||||
| La Coruña, Spain | m | 7 | |||||
| Málaga, Spain | h | 4 | |||||
| Teruel, Spain | b, h | 2 | |||||
| Bragança, Portugal | b | 10 | |||||
| Sayan Mts., Tuva, Russia | |||||||
| Murcia, Spain | f | 9 | |||||
| Smimou, Morocco | d | 3 | |||||
| Tejeda, Granada, Spain | b, e | 1 | |||||
| Huéscar, Granada, Spain | e | 9 | |||||
| Almería, Spain | h | 2 | |||||
| Canary Islands, Spain | e | 1 | |||||
| Girona, Spain | b, e, h | 9 | |||||
| Moyen Atlas, Morocco | 2 | ||||||
| Var, France | e | 4 | |||||
| Ivanovsky massif, Kazakhstan | k | ||||||
| Sekisovka, Kazakhstan | c | n.a. | |||||
| Balearic Islands, Spain | g, h | 8 | n.a. | ||||
| Erzin, Russia | c | ||||||
| Lleida, Spain | |||||||
| Girona, Spain | b, h, i | 2 | |||||
| Bragança, Portugal | h | 10 | |||||
| Susuz, Turkey | |||||||
| Torino, Italy | b, n | 1 | |||||
| Zamora, Spain | a, i | 8 | |||||
| Kulumys range, Oisky pass, Russia | |||||||
| Chelyabinsk, Russia | b | n.a. | |||||
| Kulumys range, Oisky pass, Russia | l | ||||||
| Girona, Spain | h | 4 | |||||
| Serebryansky Mount, Russia | c | ||||||
| Lleida, Spain | m | 7 | |||||
| KwaZulu-Natal, South Africa | n.a. | ||||||
| Riofrio, Granada, Spain | h | 2 | |||||
| Canary Islands, Spain | h | 2 | |||||
| Lleida, Spain | i | 6 | |||||
| Lleida, Spain | e | 6 | |||||
| Lleida, Spain | i | 5 | |||||
| Massif des Vosges, Haut-Rhin, France | i | 5 | n.a. | ||||
| Lleida, Spain | i | 6 | |||||
| Mount Keira, NSW, Australia | |||||||
| Molonglo Gorge Nature Reserve, ACT, Australia | |||||||
| Black Mountain, ACT, Australia | |||||||
| Royal National Park, NSW, Australia | |||||||
| Mount Moombil, NSW, Australia | |||||||
| Lleida, Spain |
Optimal partitioning strategy and evolutionary models selected using PartitionFinder under the Bayesian Information Criterion.
| Partition | Model |
|---|---|
| GTR+I+G | |
| HKY+I+G | |
| GTR+G | |
| GTR+I+G | |
| H3 codon pos. 1 | SYM+G |
| H3 codon pos. 2 | JC |
| H3 codon pos. 3 | HKY+I+G |
Figure 1.Bayesian phylogenetic tree obtained from the combined analysis of cox1, rrnL and H3. Node numbers represent Bayesian posterior probability values. Only support values higher than 0.9 are shown. Numbers accompanying the subgeneric classification of the species on the right correspond to the systematic groups defined by Bourdonné and Doguet (1991). Clades mentioned in the text are highlighted.
Figure 2.Maximum likelihood phylogenetic tree obtained from the combined analysis of cox1, rrnL and H3. Node numbers represent bootstrap support values. Only support values higher than 0.7 are shown. Numbers accompanying the subgeneric classification of the species on the right correspond to the systematic groups defined by Bourdonné and Doguet (1991). Clades mentioned in the text are highlighted.
Inferred phylogenetic relationships among and subgenera and their statistical supports. Nodes have been coded according to Figures 1 and 2.
| Node (Bayesian posterior probability; | Subgenera included | |||||
|---|---|---|---|---|---|---|
| B (1.00; 99) | ||||||
| C (1.00; 100) | ||||||
| D (0.97; <70) | ||||||
| E (1.00; 98) | ||||||
| G (0.96; 81) | ||||||
| I (1.00; 97) | ||||||
| K (0.99; <70) | ||||||
| M (1.00; 100) | ||||||
| O (1.00; 100) | ||||||
| P (1.00; 80) | ||||||
| R (1.00; 87) | ||||||
| S’ (<0.9; 74) | ||||||
| T (0.91; <70) | ||||||
| V (1.00; 89) | ||||||
| X (1.00; 88) | ||||||
| Y (0.93; <70) | Y’ (1.00; 98) | |||||
| Y’’ (0.97; 81) | ||||||
| Z (1.00; 90) | ||||||
Results of the Approximately Unbiased test (AU test, Shimodaira 2000). Statistically significant P values are indicated in bold (P < 0.05).
| Hypothesis of monophyly | Authorship | |
|---|---|---|
| 0.198 | ||
| 0.205 | ||
| Species “group 2” | ||
| Species “group 6” | 0.527 | |
| 0.215 | ||
| 0.066 | ||
| 0.212 | ||
| 0.383 | ||
| 0.528 | ||
| 0.165 | ||
| Species feeding on | ||
| Species feeding on | ||
| Species feeding on | ||
| Species feeding on | ||
| Species feeding on | ||
| Species feeding on |
Figure 3.Ancestral reconstruction of host plant affiliations in the studied species of and . Terminal taxa are coded according to the available host plants records from the literature (Table 1). Pie charts at selected nodes show probabilities of each state from the Bayesian analysis in BayesTraits. Clades mentioned in the text are highlighted.
Posterior probability values of ancestral host-plant affiliations calculated in BayesTraits for the selected nodes in the - phylogeny. The highest probability value(s) for each node are highlighted in bold. Ast.=, Api.=, Hyp.=, Lam.=, Plant.=, Scro.=, Ran.=, Apo.=.
| Host-plant family | ||||||||
|---|---|---|---|---|---|---|---|---|
| Node | Ast. | Api. | Hyp. | Lam. | Plant. | Scro. | Ran. | Apo. |
| A | 0.000 | 0.001 | 0.000 | 0.003 | 0.002 | 0.002 | 0.010 | |
| A’ | 0.001 | 0.002 | 0.001 | 0.006 | 0.003 | 0.006 | 0.022 | |
| A’’ | 0.002 | 0.010 | 0.000 | 0.020 | 0.001 | 0.011 | 0.104 | |
| B | 0.002 | 0.006 | 0.002 | 0.011 | 0.010 | 0.008 | 0.024 | |
| C | 0.000 | 0.000 | 0.000 | 0.002 | 0.002 | 0.001 | 0.007 | |
| D | 0.002 | 0.001 | 0.000 | 0.008 | 0.006 | 0.006 | 0.024 | |
| D’ | 0.002 | 0.001 | 0.000 | 0.008 | 0.006 | 0.006 | 0.024 | |
| D’’ | 0.048 | 0.010 | 0.001 | 0.033 | 0.023 | 0.024 | 0.129 | |
| E | 0.022 | 0.005 | 0.006 | 0.008 | 0.036 | 0.008 | 0.006 | |
| G’ | 0.374 | 0.001 | 0.023 | 0.012 | 0.008 | 0.002 | 0.044 | |
| G’’ | 0.300 | 0.001 | 0.027 | 0.029 | 0.015 | 0.009 | 0.089 | |
| I | 0.001 | 0.000 | 0.001 | 0.001 | 0.000 | 0.002 | 0.015 | |
| K | 0.036 | 0.000 | 0.200 | 0.093 | 0.007 | 0.049 | 0.227 | |
| K’ | 0.040 | 0.005 | 0.013 | 0.158 | 0.007 | 0.049 | 0.227 | |
| K’’ | 0.080 | 0.001 | 0.124 | 0.028 | 0.009 | 0.029 | 0.104 | |
| P | 0.262 | 0.005 | 0.019 | 0.064 | 0.039 | 0.047 | 0.053 | |
| Q | 0.001 | 0.002 | 0.001 | 0.003 | 0.008 | 0.008 | 0.010 | |
| R | 0.000 | 0.000 | 0.000 | 0.010 | 0.042 | 0.001 | 0.006 | |
| T | 0.011 | 0.001 | 0.001 | 0.153 | 0.015 | 0.041 | 0.068 | |
| U | 0.001 | 0.001 | 0.001 | 0.039 | 0.004 | 0.034 | 0.031 | |
| V | 0.059 | 0.001 | 0.001 | 0.257 | 0.034 | 0.033 | 0.060 | |
| W | 0.000 | 0.000 | 0.000 | 0.001 | 0.000 | 0.001 | ||
| X | 0.003 | 0.000 | 0.000 | 0.033 | 0.018 | 0.014 | 0.023 | |
| X’ | 0.005 | 0.000 | 0.001 | 0.055 | 0.128 | 0.028 | 0.047 | |
| Y | 0.052 | 0.000 | 0.000 | 0.103 | 0.011 | 0.026 | 0.050 | |
| Y’ | 0.000 | 0.000 | 0.001 | 0.001 | 0.002 | 0.006 | ||
| Z | 0.009 | 0.008 | 0.016 | 0.327 | 0.023 | 0.009 | 0.023 | |
| Z’ | 0.000 | 0.000 | 0.000 | 0.344 | 0.000 | 0.000 | 0.000 | |
Comparing model support with the Bayes factor. Bayes factors were calculated as described in the BayesTraits manual: BF=2(ln LhA−ln LhB), where ln Lhx is the marginal likelihood from the harmonic mean of the post-convergence. The plant family is the most likely ancestral host at the root of the core clade with the highest harmonic mean. The right column indicates the Bayes factor compared against as the favoured ancestral host. * Indicates positive evidence, ** indicates strong evidence, and *** indicates very strong evidence for the favoured hypothesis.
| Host plant family | ln Lh | Bayes Factor |
|---|---|---|
| -62.77 | 5.27** | |
| -63.78 | 7.30** | |
| -65.71 | 11.16*** | |
| -65.59 | 10.92*** | |
| -60.13 | - | |
| -62.44 | 4.61* | |
| -62.57 | 4.86* | |
| -63.24 | 6.20** |