Abstract
Hawaiian Melicope are one of the major adaptive radiations of the Hawaiian Islands comprising 54 endemic species. The lineage is monophyletic with an estimated crown age predating the rise of the current high islands. Phylogenetic inference based on Sanger sequencing has not been sufficient to resolve species or deeper level relationships. Here, we apply restriction site-associated DNA sequencing (RAD-seq) to the lineage to infer phylogenetic relationships. We employ Quartet Sampling to assess information content and statistical support, and to quantify discordance as well as partitioned ABBA-BABA tests to uncover evidence of introgression. Our new results drastically improved resolution of relationships within Hawaiian Melicope. The lineage is divided into five fully supported main clades, two of which correspond to morphologically circumscribed infrageneric groups. We provide evidence for both ancestral and current hybridization events. We confirm the necessity for a taxonomic revision of the Melicope section Pelea, as well as a re-evaluation of several species complexes by combining genomic and morphological data.
Introduction
Oceanic islands have long been a focal point of evolutionary studies, as they represent a microcosm for examining the process of speciation. This microcosm is shaped by a combination of factors: (1) islands are geographically small and discrete units, sometimes far removed from continental landmasses; (2) colonizations or secondary arrivals are relatively infrequent, and thus, gene flow between the source areas and island systems is restricted; and (3) islands often have dynamic geological histories that give rise to extensively varying landscapes with numerous ecological niches (; Price and Wagner, 2018). These factors can often lead to high levels of endemism, which is often the result of adaptive radiation of a limited number of colonizers (Price and Wagner, 2004; ; ). Synthesizing the unique aspects of island evolution and extrapolating results to larger scales may allow us to better uncover general patterns and processes in evolution. Such phenomena include identifying factors affecting successful colonization and adaptive radiation (; ; Paetzold et al., 2018), morphological or ecological shifts (e.g., “insular woodiness”; ; ), the spatiotemporal origins of lineages (), reconstructing colonization events (), and studying co-evolution (Roderick, 1997). These insights may result in further questions regarding taxonomy, species richness, medicinal or technical applications, and conservation (e.g., ).
Adaptive radiations on islands are of special interest for connecting changes in morphology and ecology through time () but require well-resolved phylogenies to do so. In the Hawaiian Islands, phylogenetic studies based on morphology and taxonomy have sometimes overestimated the number of colonization events, because high levels of morphological diversity led researchers to overestimate lineage diversity and the number of colonization events (Price and Wagner, 2018). In contrast, molecular phylogenetic studies have revealed that many enigmatic Hawaiian plant radiations colonized the islands only once followed by adaptive radiation: the Hawaiian lobeliads (Campanulaceae; ), Psychotria (Rubiaceae; ), Silene (Caryophyllaceae; ), Touchardia/Urera (Urticaceae; Wu et al., 2013), and Melicope (; ). Polyploidization and hybridization events were also discovered to predate colonization and radiation in several island lineages, including the Hawaiian silverswords (Asteraceae; ; ) and mints (Lamiaceae; Roy et al., 2015) along with the Pan- Pacific sandalwoods (Santalaceae; ), suggesting evolutionary success in young hybrid or polyploid colonists (; Paetzold et al., 2018).
Time-scaled phylogenies have revealed that most Hawaiian radiations are ≤5 Myr old, which corresponds to the age of the oldest current main islands, Kauaʻi and Niʻihau. This suggests a bottleneck for dispersal from older (and now largely submerged) leeward islands to the current main islands. However, there are several known exceptions of lineages older than 5 Myr, including Drosophila, damselflies, lobeliads, Zanthoxylum (Rutaceae), as well as Melicope (Price and Clague, 2002; ; ; ). Most phylogenetic studies of Hawaiian flora, however, have relied on few sequenced loci and have thus lacked sufficient power to resolve recent rapid radiations where hybridization, incomplete lineage sorting (ILS), and polyploidy may be common. Newer genomic tools are likely to provide more accurate estimates that may transform our understanding of island radiations.
The genus Melicope comprises about 235 species of shrubs and trees distributed throughout SE Asia and Australasia, extending to the Mascarene Islands and Madagascar in the West and most of the Pacific Archipelagos in the East (). There are 54 species of Melicope endemic to the Hawaiian Islands (; Wood et al., 2017), 41 of which are single island endemics (Stone et al., 1999). Hawaiian Melicope were initially placed in the genus Pelea together with species from the Marquesas Islands (Stone, 1969; Stone et al., 1999) but later incorporated into Melicope, forming the majority of the section Pelea (). Hawaiian Pelea was divided into four sections based mainly on the grade of carpel connation: Apocarpa, Cubicarpa, Megacarpa, and Pelea. Since the incorporation of the genus Pelea into Melicope, these sections have not been formally recognized within the larger infrageneric taxonomy for Melicope as recognized by but are still being used informally as species groups (), and we refer to them as Stone’s sectional species groups (Stone’s sections) from here on. The most current and comprehensive taxonomic treatment of Hawaiian Melicope was considered “provisional” by the authors (Stone et al., 1999), as species boundaries are difficult to define in some cases. Examples include three described species complexes, where the incorporated species vary from each other primarily in the degree of fruit pubescence; the Melicopeelliptica complex based mainly in Oʻahu (six species), the Hawaiian-based Melicopevolcanica complex (four species), and the Kauaʻi-based Melicopekavaiensis complex (five species) (Stone et al., 1999).
In contrast to other successful island radiations, the colonization of the Hawaiian Archipelago in Melicope was not preceded by a recent polyploidization event. In general, the genus Melicope shows a uniform chromosome number (Paetzold et al., 2018). To date, phylogenetic relationships in Hawaiian Melicope have been investigated in four molecular studies (; ; ; ), with a combination of up to six nuclear and plastid genomic regions amplified using polymerase chain reaction. Hawaiian Melicope was shown to be derived from a single colonization event (). The origin of the lineage was dated to the Mid or Late Miocene (), predating the age of Kauaʻi and Niʻihau (Price and Clague, 2002). In addition, the Hawaiian endemic genus Platydesma is nested within Melicope as a monophyletic sister group to the Hawaiian species and has since been reduced (). Statistically supported incongruences between individual genomic regions were not observed, yet the resolution of relationships within and among the clades was in general medium to poor (; ; ; ). However, two independent Hawaiian origins of the Marquesan Melicope radiation, which encompasses seven species, were inferred (; ; ).
Restriction site-associated DNA sequencing (RAD-seq; ; ) is among the most frequently used reduced representation methods employed in plant systematics. To date, most phylogenetic RAD-seq studies have focused mostly on populations or closely related species (Ree and Hipp, 2015; ; ). However, a simulated RAD investigation in Drosophila revealed the method to be potentially applicable in groups aged up to 60 Myr (Rubin et al., 2012). Since then, application to deeper species-level relationships has increased (e.g., ; ; ), facilitated by the development of RAD-seq assembly pipelines targeted at phylogenetic research ().
Incongruence between datasets has been a long-standing occurrence in molecular phylogenetic inference, traditionally manifesting as incongruences between different gene trees. The advance of next-generation sequencing (NGS) technology has shown that the issue is not solved by merely incorporating more data (). There are three possible categories of confounding information in a phylogenetic study: noise, systematic error, and an underlying biological signal. Noise is an effect of the inherently stochastic nature of sequence evolution and leads to a deterioration of phylogenetic signal over time. As such, noise most heavily impacts very small datasets and deep nodes (). Incongruence may also reflect a true biological signal, for example, the presence of ILS or non-tree-like evolution, i.e. introgression, hybridization, or recombination (; Salichos et al., 2014). Effects of hybridization range from introgression of individual alleles, to organelle capture, to hybrid speciation (; Stegemann et al., 2012; Twyford and Ennos, 2012). Either of these processes will result in discordant gene trees, and several approaches have been proposed to unravel them. Based on the distributions of conflicting phylogenetic patterns in the genome, it is possible to distinguish the more stochastic signal of ILS from the directional and asymmetric signal of hybridization ().
Here, we apply RAD-seq to Hawaiian Melicope, a lineage with a crown age of ca. 10 Myr (). We use RAD-seq to infer species-level relationships in the lineage, in a phylogenetic context of several colonization events of individual islands, multiple possible bottlenecks, and adaptive radiations within a lineage. The taxonomic implications of our phylogenetic results are discussed within the framework of evidence for both ancient and current introgression.
Materials and Methods
Taxon Sampling
Table 1 details the identity and origin of the 101 samples of this study: 6 outgroup and 95 ingroup specimens representing 41 Hawaiian species (81% of the lineage). Two samples represent the two independent colonization events to the Marquesas Islands (28% of Marquesan species). Taxonomic treatment follows species recognized in Wood et al. (2016) plus a recently described species (Wood et al., 2017) and including Platydesma (). Additionally, morphologically divergent specimens of Melicope barbigera (KW16722 and KW16718) and Melicope ovata (KW16762, KW17082, and MA663) were included (Table 1, asterisk) to elucidate whether these might represent separate taxa. We also included two specimens, KW17111 and KW15733, which correspond closely, though not entirely, to the description of Melicope wawraeana as delimited by Stone et al. (1999). Even the Oʻahu populations that were considered the core of M.wawraeana are variable, suggesting that it is a potentially artificial taxon (Stone et al., 1999). Since the morphology of the two specimens did not correspond entirely to the Oʻahu populations considered to be M.wawraeana, we included them here as Melicope sp. (Table 1).
Table 1
| Species | Stone’s section | Collection number, Herbarium voucher | Origin |
|---|---|---|---|
| Melicope adscendens(H. St. John & E. P. Hume) T. G. Hartley & B. C. Stone | Apocarpa | Appelhans MA628 (silica sample only, ORPF) | Maui |
| Melicope anisata (H. Mann) T. G. Hartley & B. C. Stone | Cubicarpa | Appelhans MA665 (GOET, PTBG) | Kauaʻi |
| M. anisata (H. Mann) T. G. Hartley & B. C. Stone | Cubicarpa | Appelhans MA668 (GOET, PTBG, USA) | Kauaʻi |
| Melicope balloui (Rock) T. G. Hartley & B. C. Stone | Megacarpa | Wood KW7685 (PTBG) | Maui |
| Melicope barbigeraA. Gray | Apocarpa | Appelhans MA666 (BISH, GOET, PTBG, USA) | Kauaʻi |
| M. barbigera A. Gray | Apocarpa | Wood KW15333 (PTBG) | Kauaʻi |
| M. barbigera A. Gray | Apocarpa | Wood KW15449 (PTBG) | Kauaʻi |
| M. barbigera A. Gray | Apocarpa | Wood KW15961 (PTBG) | Kauaʻi |
| M. barbigera* A. Gray | Apocarpa | Wood KW16722 (PTBG) | Kauaʻi |
| M. barbigera* A. Gray | Apocarpa | Wood KW16718 (PTBG) | Kauaʻi |
| Melicope christophersenii (H. St. John) T. G. Hartley & B. C. Stone | Megacarpa | Appelhans MA618 (BISH, GOET, PTBG, USA) | Oʻahu |
| Melicope christophersenii (H. St. John) T. G. Hartley & B. C. Stone | Megacarpa | Appelhans MA621 (silica sample only, cultivated at Puʻu Kaʻala) | Oʻahu |
| Melicope clusiifolia (A. Gray) T. G. Hartley & B. C. Stone | Pelea | Appelhans MA615 (GOET, PTBG) | Oʻahu |
| M. clusiifolia (A. Gray) T. G. Hartley & B. C. Stone | Pelea | Appelhans MA617 | Oʻahu |
| M. clusiifolia (A. Gray) T. G. Hartley & B. C. Stone | Pelea | Appelhans MA634 (PTBG) | Maui |
| M. clusiifolia (A. Gray) T. G. Hartley & B. C. Stone | Pelea | Appelhans MA650 (GOET, PTBG, USA) | Maui |
| M. clusiifolia (A. Gray) T. G. Hartley & B. C. Stone | Pelea | Appelhans MA651 (BISH, GOET, PTBG, USA) | Maui |
| M. clusiifolia (A. Gray) T. G. Hartley & B. C. Stone | Pelea | Appelhans MA655 (silica sample only) | Maui |
| M. clusiifolia (A. Gray) T. G. Hartley & B. C. Stone | Pelea | Appelhans MA657 (GOET, PTBG, USA) | Maui |
| M. clusiifolia (A. Gray) T. G. Hartley & B. C. Stone | Pelea | Appelhans MA670 | Kauaʻi |
| M. clusiifolia (A. Gray) T. G. Hartley & B. C. Stone | Pelea | Appelhans MA672 | Kauaʻi |
| M. clusiifolia (A. Gray) T. G. Hartley & B. C. Stone | Pelea | Appelhans MA693 | Hawaiʻi |
| M. clusiifolia (A. Gray) T. G. Hartley & B. C. Stone | Pelea | Appelhans MA695 | Hawaiʻi |
| M. clusiifolia (A. Gray) T. G. Hartley & B. C. Stone | Pelea | Oppenheimer s.n. (silica sample only) | Maui |
| M. clusiifolia(A. Gray) T. G. Hartley & B. C. Stone | Pelea | Oppenheimer H91641 (US) | Lānaʻi |
| M. clusiifolia (A. Gray) T. G. Hartley & B. C. Stone | Pelea | Wood KW16146 (PTBG) | Kauaʻi |
| M. clusiifolia(Gray) T. G. Hartley & B. C. Stone | Pelea | Appelhans MA675 | Kauaʻi |
| Melicope cornuta (Hillebr.) Appelhans, K. R. Wood & W. L. Wagner | Platydesma | Ching s.n. (silica sample only) | Oʻahu |
| M. cornutavar. decurrens(B. C. Stone) Appelhans, K. R. Wood & W. L. Wagner | Platydesma | Takahama s.n. (silica sample only) | Oʻahu |
| Melicope cruciata (A. Heller) T. G. Hartley & B. C. Stone | Megacarpa | Wood KW16251 (PTBG) | Kauaʻi |
| Melicope degeneri (B. C. Stone) T. G. Hartley & B. C. Stone | Cubicarpa | Wood KW15903 (PTBG) | Kauaʻi |
| M. degeneri (B. C. Stone) T. G. Hartley & B. C. Stone | Cubicarpa | Wood KW15984 (PTBG) | Kauaʻi |
| Melicope feddei (H. Lév.) T. G. Hartley & B. C. Stone | Megacarpa | Appelhans MA688 (BISH, GOET, PTBG, USA) | Kauaʻi |
| M. feddei (H. Lév.) T. G. Hartley & B. C. Stone | Megacarpa | Wood KW15844 (PTBG) | Kauaʻi |
| M. haleakalae(B. C. Stone) T. G. Hartley & B. C. Stone | Pelea | Appelhans MA645 (BISH, GOET, PTBG) | Maui |
| M. haleakalae (B. C. Stone) T. G. Hartley & B. C. Stone | Pelea | Appelhans MA646 (BISH, GOET, PTBG, USA) | Maui |
| Melicope haupuensis(H. St. John) T. G. Hartley & B. C. Stone | Apocarpa | Appelhans MA687 (BISH) | Kauaʻi |
| M. haupuensis (H. St. John) T. G. Hartley & B. C. Stone | Apocarpa | Wood KW16791 (PTBG) | Kauaʻi |
| M. haupuensis (H. St. John) T. G. Hartley & B. C. Stone | Apocarpa | Wood KW16794 (PTBG) | Kauaʻi |
| Melicope hawaiensis (Wawra) T. G. Hartley & B. C. Stone | Apocarpa | Appelhans MA633 (BISH, GOET, PTBG, USA) | Maui |
| M. hawaiensis (Wawra) T. G. Hartley & B. C. Stone | Apocarpa | Appelhans MA700 | Hawaiʻi |
| M. hawaiensis (Wawra) T. G. Hartley & B. C. Stone | Apocarpa | Oppenheimer s.n. (silica sample only) | Maui |
| Melicope hiiakae (B. C. Stone) T. G. Hartley & B. C. Stone | Megacarpa | Ching s.n. (silica sample only) | Oʻahu |
| Melicope hivaoaensis J. Florence | Meyer 826 | Hivaoa, Marquesas Islands | |
| Melicope inopinata J. Florence | Meyer 887 | Hivaoa, Marquesas Islands | |
| Melicope kavaiensis(H. Mann) T. G. Hartley & B. C. Stone | Megacarpa | Appelhans MA679 (BISH, GOET, PTBG, USA) | Kauaʻi |
| Melicope knudsenii (Hillebr.) T. G. Hartley & B. C. Stone | Apocarpa | Appelhans MA629 (silica sample only, ORPF) | Maui |
| M. knudsenii(Hillebr.) T. G. Hartley & B. C. Stone | Apocarpa | Oppenheimer H41610 (BISH) | Maui |
| M. knudsenii (Hillebr.) T. G. Hartley & B. C. Stone | Apocarpa | Wood KW17119 (PTBG) | Kauaʻi |
| Melicope lydgatei (Hillebr.) T. G. Hartley & B. C. Stone | Megacarpa | Ching s.n. (silica sample only) | Oʻahu |
| Melicope makahae(B. C. Stone) T. G. Hartley & B. C. Stone | Apocarpa | Takahama s.n. (silica sample only) | Oʻahu |
| M. makahae (B. C. Stone) T. G. Hartley & B. C. Stone (cf.) | Apocarpa | Appelhans MA609 (GOET, PTBG) | Oʻahu |
| Melicope molokaiensis (Hillebr.) T. G. Hartley & B. C. Stone | Megacarpa | Appelhans MA635 (BISH, GOET, PTBG) | Maui |
| M. molokaiensis (Hillebr.) T. G. Hartley & B. C. Stone | Megacarpa | Appelhans MA643 (BISH, GOET, PTBG, USA) | Maui |
| M. molokaiensis(Hillebr.) T. G. Hartley & B. C. Stone | Megacarpa | Oppenheimer s.n. (silica sample only) | Maui |
| Melicope mucronulata (H. St. John) T. G. Hartley & B. C. Stone | Apocarpa | Appelhans MA630 (silica sample only, ORPF) | Maui |
| Melicope munroi (St. John) T. G. Hartley & B. C. Stone | Megacarpa | Oppenheimer s.n. (silica sample only) | Lanaʻi |
| Melicope oahuensis (H. Lév.) T. G. Hartley & B. C. Stone | Cubicarpa | Appelhans MA610 (BISH, GOET, PTBG, USA) | Oʻahu |
| M. oahuensis (H. Lév.) T. G. Hartley & B. C. Stone | Cubicarpa | Ching s.n. (silica sample only) | Oʻahu |
| Melicope oppenheimeriK. R. Wood, Appelhans & W. L. Wagner | Megacarpa | Wood KW7419 (PTBG) | Maui |
| M. oppenheimeri K. R. Wood, Appelhans & W. L. Wagner | Megacarpa | Wood KW7408 (PTBG) | Maui |
| Melicope orbicularis (Hillebr.) T. G. Hartley & B. C. Stone | Megacarpa | Appelhans MA656 (BISH, GOET, PTBG, USA) | Maui |
| M. orbicularis (Hillebr.) T. G. Hartley & B. C. Stone | Megacarpa | Appelhans MA659 (GOET, PTBG) | Maui |
| Melicope ovalis (St. John) T. G. Hartley & B. C. Stone | Cubicarpa | Wood KW13724 (PTBG) | Maui |
| Melicope ovata (H. St. John & E. P. Hume) T. G. Hartley & B. C. Stone | Apocarpa | Appelhans MA662 (GOET, PTBG, USA) | Kauaʻi |
| M. ovata (H. St. John & E. P. Hume) T. G. Hartley & B. C. Stone | Apocarpa | Appelhans MA684 (BISH, GOET) | Kauaʻi |
| M. ovata* (H. St. John & E. P. Hume) T. G. Hartley & B. C. Stone | Apocarpa | Appelhans MA663 (BISH, GOET, PTBG, USA) | Kauaʻi |
| M. ovata* (H. St. John & E. P. Hume) T. G. Hartley & B. C. Stone | Apocarpa | Wood KW17082 (PTBG) | Kauaʻi |
| M. ovata* (H. St. John & E. P. Hume) T. G. Hartley & B. C. Stone | Apocarpa | Wood KW16762 (PTBG) | Kauaʻi |
| Melicope pallida (Hillebr.) T. G. Hartley & B. C. Stone | Apocarpa | Appelhans MA689 (silica sample only) | Kauaʻi |
| M. pallida (Hillebr.) T. G. Hartley & B. C. Stone | Apocarpa | Wood KW16789 (PTBG) | Kauaʻi |
| M. pallida (Hillebr.) T. G. Hartley & B. C. Stone | Apocarpa | Wood KW15571 (PTBG) | Kauaʻi |
| Melicope paniculata (H. St. John) T. G. Hartley & B. C. Stone | Cubicarpa | Perlman 19387 (PTBG) = Appelhans MA660 (silica sample) | Kauaʻi |
| M. paniculata (H. St. John) T. G. Hartley & B. C. Stone | Cubicarpa | Wood KW16155 (PTBG) | Kauaʻi |
| Melicope peduncularis (H. Lév.) T. G. Hartley & B. C. Stone | Cubicarpa | Appelhans MA652 (BISH, GOET, PTBG, USA) | Maui |
| M. peduncularis (H. Lév.) T. G. Hartley & B. C. Stone | Cubicarpa | Appelhans MA653 (BISH, GOET, PTBG, USA) | Maui |
| Melicope pseudoanisata(Rock) T. G. Hartley & B. C. Stone | Megacarpa | Appelhans MA632 (silica sample only, ORPF) | Maui |
| M. pseudoanisata (Rock) T. G. Hartley & B. C. Stone | Megacarpa | Appelhans MA636 (silica sample only) | Maui |
| M. pseudoanisata (Rock) T. G. Hartley & B. C. Stone | Megacarpa | Appelhans MA642 (GOET, PTBG, USA) | Maui |
| Melicope puberula (H. St. John) T. G. Hartley & B. C. Stone | Megacarpa | Appelhans MA680 (GOET, PTBG, USA) | Kauaʻi |
| M. puberula (H. St. John) T. G. Hartley & B. C. Stone | Megacarpa | Wood KW16058 (PTBG) | Kauaʻi |
| Melicope radiata (H. St. John) T. G. Hartley & B. C. Stone | Megacarpa | Appelhans MA696 | Hawaiʻi |
| Melicope rostrata(Hillebr.) Appelhans, K. R. Wood & W. L. Wagner | Platydesma | Appelhans MA683 (BISH, GOET) | Kauaʻi |
| Melicope rotundifolia(A. Gray) T. G. Hartley & B. C. Stone | Megacarpa | Ching s.n. (silica sample only) | Oʻahu |
| Melicope sandwicensis (Hook. & Arn.) T. G. Hartley & B. C. Stone | Apocarpa | Ching s.n. (silica sample only) | Oʻahu |
| Melicope sessilis (H. Lév.) T. G. Hartley & B. C. Stone | Megacarpa | Appelhans MA644 (BISH, GOET, PTBG, USA) | Maui |
| Melicope sp. (Rock) T. G. Hartley & B. C. Stone | Megacarpa | Wood KW17111 (PTBG) | Kauaʻi |
| Melicope sp. (Rock) T. G. Hartley & B. C. Stone | Megacarpa | Wood KW15733 (PTBG) | Kauaʻi |
| Melicope spathulata A. Gray | Platydesma | Appelhans MA697 | Hawaiʻi |
| M. spathulata A. Gray | Platydesma | Wood KW16743 (PTBG) | Kauaʻi |
| M. spathulata A. Gray | Platydesma | Wood KW16836 (PTBG) | Kauaʻi |
| Melicope stonei K. R. Wood, Appelhans & W. L. Wagner | Apocarpa | Appelhans MA691 | Kauaʻi |
| M. stonei K. R. Wood, Appelhans & W. L. Wagner | Apocarpa | Wood KW16727 (PTBG) | Kauaʻi |
| Melicope volcanica (A. Gray) T. G. Hartley & B. C. Stone (cf.) | Megacarpa | Oppenheimer s.n. (silica sample only) | Lānaʻi |
| Melicope waialealae (Wawra) T. G. Hartley `& B. C. Stone | Pelea | Wood KW16015 (PTBG) | Kauaʻi |
| Outgroup | |||
| Melicope aneura (Lauterb.) T. G. Hartley | Appelhans MA418 (LAE, USA) | Papua New Guinea | |
| Melicope durifolia (K. Schum.) T. G. Hartley | Appelhans MA455 (LAE, USA) | Papua New Guinea | |
| Melicope polyadenia Merr. & L. M. Perry | Appelhans MA438 (LAE, USA) | Papua New Guinea | |
| Melicope triphylla Merr. | Appelhans MA394 (GOET) | cultivated Hortus Botanicus Leiden | |
| Melicope brassii T. G. Hartley | Appelhans MA436 (LAE, USA) | Papua New Guinea | |
| M. durifolia (K. Schum.) T. G. Hartley | Appelhans MA465 (LAE, USA) | Papua New Guinea |
Samples within this study including origin, voucher placement, and assignment to Stone’s sections.
Asterisk marks morphologically deviating specimens. Samples in bold were used in parameter optimization. ORPF, cultivated at Olinda Rare Plant Facility.
RAD Library Preparation
DNA was extracted from silica-dried material using the Qiagen DNeasy Plant Mini Kit® (Qiagen, Hilden, Germany) as per the manufacturer’s instructions with incubation in lysis buffer elongated to 2h. DNA concentration was measured using the Qubit® fluorometer and the Qubit® dsDNA BR Assay Kit (Thermo Fisher Scientific, Darmstadt, Germany) and adjusted to 30 ng/µL. Floragenex Inc. (Portland, Oregon, USA) generated RAD libraries using the restriction enzyme SfbI. With a method following being employed, including the use of sample-specific barcodes, the samples were sequenced on an Illumina® GAIIx platform to produce 100-bp single-end reads.
RAD Locus Assembly
Quality of raw reads was checked using FastQC (). The program ipyrad v.0.7.21 was used to demultiplex raw reads allowing a mismatch of 1 bp. Raw reads were trimmed using cutadapt v.1.9.1 () as implemented in ipyrad by removing adapter sequences, trimming bases with Phred scores <30 and removing reads shorter than 35 bp after trimming. Trimmed reads were assembled de novo using the ipyrad pipeline. The software attempts to evaluate orthology by scoring alignments of reads or sequences, as opposed to assessing purely sequence identity (). The alignment score is the user-determined clustering threshold to be met. To reduce the risk of introducing assembly error to our dataset, we performed a modified clustering optimization approach (Paris et al., 2017). We iterated over core clustering parameters and plotted assembly matrices (cluster depth, heterozygosity, number of putatively paralogous loci, number of single-nucleotide polymorphisms (SNPs)) to identify parameters introducing excessive assembly errors (Paetzold et al., unpublished results; Paris et al., 2017). In addition, we optimized the clustering of reads within each individual sample and the clustering of consensus sequences across loci separately, reasoning that the divergence found within each individual genome might be significantly different from the ca. 10 Myr of divergence () within the lineage as a whole. Thus, the assembly was generated using a clustering threshold of 95 for in-sample clustering and 90 for between-sample clustering. The final filtering of loci was performed for values 10, 32, 50, 67, and 85 as the minimum numbers of samples per locus.
Phylogenetic Inference and Quartet Sampling
Phylogenetic inference was performed on all resulting alignments using maximum likelihood (ML) and Bayesian inference (BI). As individual loci are very short and may comprise a high fraction of missing data, a partitioned analysis is neither computationally feasible nor expected to produce reliable results. Thus, all datasets were analyzed solely concatenated. ML was performed using ExaML v3.0.2 () using the new rapid hill-climbing algorithm, a random number seed, the gamma model of rate heterogeneity, and the median for discrete approximation of rate heterogeneity. For datasets containing minimum numbers of 10, 32, and 50 samples, the memory saving option for gappy alignments was activated (-S). Parsimony starting trees were generated using RAxML v8.2.4 (Stamatakis, 2014). RAxML was also used to generate 100 bootstrap replicate alignments and their corresponding parsimony starting trees. ExaML searches were run on every replicate alignment with the above-mentioned settings.
BI was performed using ExaBayes v 1.5 (). Four independent runs were carried out with a convergence stopping criterion (split frequencies average <5% in three subsequent generations) and for a minimum of 100,000 generations sampling every 100th generation under the GTR+I+G model. Majority rule consensus trees were drawn on topologies of all four runs combined after the first 25% was discarded as burn-in.
Analysis of large-scale, concatenated datasets can result in erroneous relationships with high bootstrap support because of a failure to model the effects of ILS (; ; Seo, 2008). These effects can be driven by only a few loci (Shen et al., 2017) and especially pertain to short branches (). On the other hand, a simulation study has shown that concatenated analysis of datasets containing loci with anomalous gene trees will more likely result in unresolved species tree topologies, rather than highly supported false ones ().
Methods implementing the multispecies coalescent (MSC) model explicitly incorporate gene tree conflict into species tree inference and are thus more robust to ILS than concatenation approaches () but are often intractable for large datasets (). Summary methods of species tree inference under the MSC, for example, ASTRAL () or NJst (), are based on the analysis of individual gene trees and have become popular due to their comparative speed and accuracy. However, the limited information content of individual RAD loci often limits their application for gene tree inference, which may negatively impact species tree estimation (Salichos and Rokas, 2013; ). Alternatively, site-based methods avoid estimation of gene trees, instead using SNP data directly, and so are expected to be well suited to short, low-variability loci (). We employed the SVDQuartets method, which infers quartet trees from SNPs using phylogenetic invariant patterns under the coalescent model and then infers the species tree by quartet joining of the subtrees using algebraic statistics (). We converted the SNP datasets into nexus format using the Ruby script convert_vcf_to_nexus.rb (). The SVDQuartets analysis was computed as implemented in the software PAUP*4.0a (Swofford, 2002; Swofford, 2018). We analyzed 250,000 randomly selected quartets and assessed statistical support using 100 nonparametric bootstrap support replicates. For ambiguous positions in the SNP matrix, we chose the “Distribute” option, as these positions represent heterozygous sites.
To estimate the robustness of resolved relationships, we employed the Quartet Sampling method, which aims to measure branch support in large sparse alignments (Pease et al., 2018). As each internal branch divides all samples within a phylogeny into four non-overlapping subsets, the method randomly samples one taxon per subset to produce a quartet phylogeny. The topology of each quartet is either concordant with the tree topology or discordant. Discord is measured and quantified to produce four metrics—quartet concordance (QC), quartet differential (QD), quartet informativeness (QI), and quartet fidelity (QF)—allowing effective assessment of branch-related (QC, QD, and QI) and taxon-related (QF) discordance in the dataset (Pease et al., 2018). The method is implemented in the python script quartet_sampling.py (https://www.github.com/fephyfofum/quartetsampling). We performed Quartet Sampling on all datasets and the respectively resolved topologies using 500 replicates per branch with a minimum required overlap of 300,000 bp in the min10, min32, min50, and min67 concatenated datasets. The minimum overlap was lowered to 140,000 bp in the min85 concatenated dataset, as otherwise five samples would have been excluded from the analysis.
Test for Introgression
The D-statistics () is a site-based test for introgression. In a four-taxon topology (((P1, P2), P3), O), a derived allele in the P3 lineage is expected to occur also in either P1 or P2 with equal frequency, giving rise to either an ABBA or BABA discordant site pattern (). A statistically significant imbalance in these site pattern frequencies provides evidence of introgression, while equal frequencies are associated with neutral processes like ILS. Unfortunately, this test is not well suited for deeper evolutionary timescales, where the P3 lineage has diverged into multiple sub-lineages, and it also does not allow inference of direction of introgression. Partitioned D-statistics is a system of multiple four-taxon D-statistics in a symmetric, five-taxon phylogeny with the ingroup taxa forming two pairs (P1, P2) and (P31, P32) and an outgroup taxon (O) (Figure 1) (). The partitioned D-statistics identifies sites, in which either or both of the P3 lineages share a derived allele with either P1 or P2, but not both (Figure 1) ().
Figure 1
We used partitioned D-statistics to infer whether discordant relationships inferred between major clades (see below) are caused by ILS or introgression. We defined entire clades as lineages and tested all combinations obeying the symmetric topology.
Results
Raw Data and Assembly
Illumina Sequencing yielded an average of 10,439,082 reads per sample (342,914–34,663,109). After quality trimming, an average of 10,327,562 reads per sample (271,257–34,542,777) were left. The assembled dataset contained a total of 786,169 clusters prior to filtering by sample coverage. Filtering reduced the number of loci by over 90% (Table 2). The final datasets contained between 7,266 (min85) and 59,041 (min10) loci. The number of variable sites (SNPs) ranged from 529,045 (min10) to 82,760 (min85) (Table 2).
Table 2
| Total | min10 | min32 | min50 | min67 | min85 | |
|---|---|---|---|---|---|---|
| Number of loci | 786,169 | 59,041 | 36,622 | 30,801 | 23,401 | 7,266 |
| Concatenated length (bp) | NA | 4,800,367 | 2,986,760 | 2,506,242 | 1,892,473 | 584,086 |
| Number of SNPs | NA | 529,045 | 385,871 | 332,935 | 256,276 | 82,760 |
Differences between the number of loci, their concatenated length, and the number of SNPs resulting from filtering by minimum samples per locus (10, 32, 50, 67, and 85).
Phylogenetic Inference
All five final datasets were used for phylogenetic inference in concatenated BI, ML, and SVD Quartets analyses. Statistical support for inferred relationships was assessed using posterior probabilities (PPs), nonparametric bootstrap (NBS) (ML-NBS and SVD-NBS), and Quartet Sampling. Analyses of the five datasets resulted in mostly congruent relationships, with few exceptions (see below). NBS and PP values are very high across the trees. QI values are high for all nodes (>0.9), and QF scores are average between 0.83 and 0.88 across datasets. Figure 2 shows the result of phylogenetic inference in the concatenated min32 dataset.
Figure 2

Phylogeny of Hawaiian Melicope based on the concatenated min32 dataset. Bayesian posterior probability (PP) values are indicated above branches, and maximum likelihood (ML) nonparametric bootstrap support (ML-NBS) below branches. Support values are not shown for maximally supported clades (1.00pp/100BS). A hashtag (#) represents incongruent species relationships between Bayesian and ML analyses. Clade colors and line drawings correspond to morphologically limited Stone’s sections. Bold samples represent Marquesan species. Asterisks mark specimens differing morphologically from the typical representatives of these species. Purple arrows mark putative introgression events.
Hawaiian Melicope are divided into five main clades corresponding to those previously resolved by
Figure 3

Phylogeny of Hawaiian Melicope based on the min32 dataset. Quartet Sampling results (quartet concordance (QC)/quartet differential (QD)/quartet informativeness (QI)) are indicated on branches, and quartet fidelity (QF) values behind samples. Nodes are colored according to QC and QD values. Results are not shown for branches with QC > 0.9. The lowest QF values are highlighted. Outgroup specimens are removed for graphical purposes. All outgroup relationships receive maximum QC values (1/-/1).
The remaining relationships within individual clades are fully resolved, improving resolution to the species and intraspecies levels (Figure 2). The majority of all Hawaiian Melicope are resolved in clade I, and relationships among species show many nodes with notable discord and very short branches (Figure 2). Most of the nodes show low QC and medium-to-low QD values (Figure 3). Three samples show incongruent relationships between datasets. This pertains to the Marquesan Melicope hivaoaensis, which is resolved in clade I as either sister to the remaining species (Supplemental Figures 3–9) within the clade or diverging prior to Melicope lydgatei (Figures 2 and 3, Supplemental Figures 1 and 2) as well as to M. kavaiensis and Melicope sp. KW15773 (Figure 3, Supplemental Figures 1–9). In all datasets, QC values show high discord or even counter-support for the placement of these three specimens. However, while QD and QF values are high for M. hivaoaensis, for both M. kavaiensis and Melicope sp. KW15773, QD values are low and QF scores are below average (0.47–0.6 for M. kavaiensis) (Figure 3, Supplemental Figures 1–9). The remaining relationships in clade I are congruent among all concatenation-based analyses. Site-specific coalescence analysis, however, resolved largely incongruent relationships for taxa in this clade, especially pertaining to the most recent divergences. The inferred relationships receive medium-to-very-low SVD-NBS values and show a high amount of discord in Quartet Sampling (Supplemental Figures 5–9).
Clades III and IV are subdivided into two subclades each. Most species sampled with multiple accessions are resolved as monophyletic with high support and no discord detected in Quartet Sampling. Exceptions are Melicope clusiifolia, Melicope haupuensis, Melicope knudsenii, and Melicope feddei. M. clusiifolia is resolved paraphyletic with respect to Melicope haleakalae, which is nested within clade IVB with high-to-maximum support. Specimens of M. haupuensis are resolved as polyphyletic within clade IIIB. The relationships among the three sampled taxa are not resolved consistently across datasets and poorly supported. Quartet Sampling reveals a high level of discord and below-average QF scores (Figure 3, Supplemental Figures 1–9). M. knudsenii is also resolved as polyphyletic with two Maui specimens (MA629 and H41610) monophyletic in clade IIIA, while the third sample from Kauaʻi (KW17119) is resolved as sister to M. barbigera in clade IIIB (Figure 2). Either relationship is virtually uncontested (Figures 2 and 3, Supplemental Figures 1–9). M. feddei is paraphyletic with respect to one of the Kauaʻi M. wawraeana-like specimens (KW17111). The three individuals form a fully supported, monophyletic unit (Figures 2 and 3, Supplemental Figures 1–9).
None of the three species complexes (M. elliptica, M. kavaiensis, and M. volcanica complexes) are resolved as monophyletic. Species of both the M. kavaiensis and M. volcanica complexes are resolved in clade I (Figure 2) in proximity to each other, but not sister to each other. Species of the M. elliptica complex are resolved in different subclades of clade III (Figure 2). Both M. barbigera and M. ovata were resolved as monophyletic, and the morphologically divergent specimens (Table 1, asterisk) are resolved as sister clades to the samples with the typical morphology of the respective species with high support (Figure 2).
The species from the Marquesas Islands are deeply nested within the Hawaiian clade.Melicope inopinata is resolved in clade III as sister to the rest of subclade IIIA. M. hivaoaensis represents a group of six morphologically similar species that form a highly supported monophyletic clade (
Test for Introgression
The min32 dataset was used for the ABBA-BABA test, since it produced the highest number of fully supported nodes. The tree topology in Figure 2 was chosen to represent the species tree topology, as it was recovered by the majority of analyses. The D-statistics was only used to test the incongruent position of clade III, as for incongruent species within clade I, the sampling of the respective populations is not sufficient to draw reliable conclusions. Samples within clades were pooled, and SNP frequencies were used for D-statistic calculations (
Table 3
| ((P1, P2), (P31, P32), O) | D12 | Z12 | n ABAAA | n BABBA |
|---|---|---|---|---|
| ((I, II), (III, IV), V&O) | 0.020 | 0.95 | 809.84 | 778.1 |
| ((I, II), (IV, III), V&O) | −0.020 | 0.96 | 778.1 | 809.84 |
| ((IV, III), (I, II), V&O) | 0.066 | 3.28 | 1,273.58 | 1,115.49 |
| ((IV, III), (II, I), V&O) | −0.066 | 3.29 | 1,273.58 | 1,115.5 |
| ((P1, P2), (P31, P32), O) | D1 | Z1 | n ABBAA | n BABAA |
| ((I, II), (III, IV), V&O) | 0.276 | 8.48 | 261.01 | 437.67 |
| ((I, II), (IV, III), V&O) | −0.276 | 8.17 | 437.67 | 261.01 |
| ((IV, III), (I, II), V&O) | −0.242 | 7.07 | 403.07 | 222.05 |
| ((IV, III), (II, I), V&O) | 0.290 | 7.61 | 271.16 | 444.45 |
| ((P1, P2), (P31, P32), O) | D2 | Z2 | n ABABA | n BAABA |
| ((I, II), (III, IV), V&O) | −0.253 | 7.08 | 505.48 | 286.73 |
| ((I, II), (IV, III), V&O) | 0.253 | 7.05 | 286.73 | 505.48 |
| ((IV, III), (I, II), V&O) | 0.290 | 7.57 | 271.16 | 444.45 |
| ((IV, III), (II, I), V&O) | −0.242 | 7.24 | 403.06 | 222.05 |
Partitioned D-statistics for introgression involving clades I–IV.
Z scores ≥2.55 represent a significant value for Dx. The respective numbers of concordant and discordant site patterns are listed. Clade numbers refer to those in Figure 2, and the group they are assigned to in the partitioned D-statistics test is indicated (compare Figure 1). O, outgroup.
Discussion
Phylogeny and Introgression
Analysis of ipyrad assemblies consistently resolved five major clades within Hawaiian Melicope (Figure 2). However, the relationships of clade III were incongruent among the five datasets and analysis methods (Figure 2, Supplemental Figures 1–9). Incongruence between datasets may be caused by one of three factors: noise, ILS, or non-tree-like evolution. As noise is expected to impact small datasets and deep nodes most severely (
The QD values of the branch illustrate that one of the discordant topologies is inferred significantly more often (0.0–0.4; Figure 3, Supplemental Figures 1–9), which indicates non-tree-like evolution as the cause for the discord. Thus, we used the partitioned D-statistics to test for signals of ancient introgression between clades I through IV with all clades tested as putative donor (P3) lineages. In all cases, values for D1 and D2 were each significant, yet values for D12 were only significant when clades I and II were defined as P3 (Table 3). Positive values of D1 represent introgression between P2 and P31, while negative values indicate introgression between P1 and P31, and values for D2 represent events analogous for P32 and P2 (
The origin of the Hawaiian Melicope lineage predates the rise of the current high islands (
Bootstrap and PP support values were generally high across trees inferred from different datasets but generally increased with dataset size. Lenient filtering in RAD-seq data is often practiced, as there is a correlation between the size of a data matrix and resolution and support of relationships (Wagner et al., 2013;
We detected some discord between relationships resolved by concatenation and site-specific coalescence-based methods (Figure 2, Supplemental Figures 1–9). The evaluation of the performance of different species-tree inference methods is a matter of ongoing research, especially with regard to genomic datasets. Concatenation-based ML inference can be statistically inconsistent under some conditions in the MSC, that is, ILS causing gene trees to differ from the true species tree (
With respect to species relationships inferred for Hawaiian Melicope and considering the observed lower accuracy of SVDQuartets compared with concatenation-based approaches under conditions typically characterizing RAD datasets, we suggest that the results from concatenated BI and ML are probably more accurate than those based on SVDQuartets and will be discussed below. However, we do stress that none of the approaches have proven to be statistically consistent under conditions observed herein, that is, ILS, GTEE, and horizontal gene transfer (Figure 2).
Taxonomic Implications
The former small genus Platydesma and Stone’s section Pelea are each monophyletic (Figure 2), while the three remaining sections of Stone, comprising the majority of all Hawaiian Melicope species, are not. Apocarpa is divided into two lineages with the majority of species resolved in Apocarpa 1 (Figure 2). The three species of the Apocarpa 2 clade share a number of morphological traits, though none of them is either exclusive or inclusive. All species of Apocarpa 2 occur in mesic forests only and, with the exception of Melicope stonei, share a sprawling, shrubby habit (Stone et al., 1999; Wood et al., 2017). Finally, in all Apocarpa 2 species, both endocarp and exocarp are glabrous and inflorescences are few-flowered, though both of these traits also appear outside of this group (Stone et al., 1999; Wood et al., 2017). In a previous analysis, apocarpous species were resolved in three different clades (
Interspecies relationships within clade I are less well supported than in the remaining clades, and Quartet Sampling reveals measurable discord at nearly every branch in the backbone of this clade. For many of the nodes with low QC values, QD values are high (Figure 3, Supplemental Figures 1–9), which characterizes ILS and corresponds to the shortness of these branches. On the other hand, many branches show low QD values, indicating widespread introgression between these lineages. Unfortunately, sampling herein is not sufficient to test individual relationships.
Of the 24 species represented by multiple accessions, 20 were resolved as monophyletic, while four species were either paraphyletic or polyphyletic. M. clusiifolia is the most widespread and morphologically diverse of all Hawaiian Melicope (Stone et al., 1999), and it is paraphyletic with both of the other species of Stone’s section Pelea, M. haleakalae and Melicope waialealae (clade IV, Figure 2). Several attempts have been made to subdivide M. clusiifolia into varying constellations of subspecies, varieties, and forms (St. John, 1944; Stone, 1969). In the most recent taxonomic treatment, Stone et al. (1999) synonymized all subdivisions of the species, arguing that the variable characters seem to represent a continuum rather than distinguishable, discrete units. However, the authors also issued the recommendation that the overall pattern of variability in M. clusiifolia should be studied in detail (Stone et al., 1999). M. haleakalae is characterized as differing from M. clusiifolia, mainly in its persistent sepals (Stone et al., 1999). Considering that M. haleakalae is nested deeply within M. clusiifolia (Figure 2, clade IV), the two might be regarded as conspecific and included in an overall evaluation of the complex. M. waialealae differs from M. clusiifolia mainly in leaf shape (Stone et al., 1999). However, since the leaf shape of M. clusiifolia is highly variable, M. waialealae might represent one end of a continuum across both taxa rather than one of two distinct states. On the other hand, these three species might represent a case of speciation in progress. In this case, the deep nesting, especially of M. haleakalae, within M. clusiifolia, would represent speciation following a progenitor-derivative scenario (
M. knudsenii, delimited by Stone et al. (1999) as the only species occurring on non-adjacent islands, was resolved as polyphyletic, with three samples resolved as two distinct lineages within clade III.
The three specimens of M. haupuensis included in this study are resolved as paraphyletic. Moreover, they are the only species resolved with incongruent topologies of the individual samples associated with the different datasets (compare Figure 2, Supplemental Figures 1–9). Quartet Sampling shows strong discord for either of the inferred relationships with medium QD values (Figure 3, Supplemental Figures 1–9), indicating the possibility of introgressed sites. Moreover, QF scores for the three specimens are considerably lower than the average, indicating a rogue behavior (
Multiple samples of M. ovata and M. barbigera were included in our analyses, representing both the typical morphology and a deviating morphotype. For either species, the morphologically deviating samples were resolved as the sister group to the samples with the typical habit. Variant morphotypes of M. ovata displayed a pubescent lower leaf surface, whereas leaves are typically glabrous in this species. M. barbigera usually has few-flowered inflorescences (Stone et al., 1999). In contrast, the variant morphotype has inflorescences with a considerably larger number of flowers. Genomic divergence is comparable with that of other species pairs within the lineage. Both groups might be another case of speciation in progress within Hawaiian Melicope. In both cases, detailed morphological studies will be necessary to investigate if the morphologically divergent populations of the two species should be recognized as separate taxa.
The two M. wawraeana-like specimens are resolved in clade I, but not closely related to each other. One specimen (KW17111) is nested within the two samples of M. feddei with high support (Figures 2 and 3). M. wawraeana is very similar to M. feddei and differs mainly in pedicel length (Stone et al., 1999). The present results suggest that some populations might be conspecific with M. feddei, while others (e.g., from the herein unsampled type location) are not. The relationships of the second M. wawraeana-like specimen (KW15733) are resolved incongruently among datasets, as are the relationships of the sampled specimen of M. kavaiensis. The two samples are resolved either as sister groups (Figure 3, Supplemental Figures 1, 4, 5, and 7–9) or as consecutive sister clades within clade I (Supplemental Figures 2, 3, and 6). There is a substantial amount of discord in the dataset for either of the resolved relationships. QD values are low, indicating the possibility of introgression between these morphologically distinct species. Additionally, QF scores for either of the specimens are low corresponding to the rogue behavior of the samples.
The rogue behavior of the aforementioned samples (M. kavaiensis, Melicope sp. KW15733) might also be related to the incongruent placement of M. hivaoaensis, as the three taxa are inferred as closely related, regardless of the relation to the remainder of clade I. For this specimen, QC and QD values are low; however, QF is high (Figure 3, Supplemental Figures 1–9). M. hivaoaensis represents an adaptive radiation of five species endemic to the Marquesas Islands, whose predecessor colonized from the Hawaiian Islands (
We confirm previous results showing that Hawaiian Melicope colonized the Marquesas Islands twice independently, negating the hypothesis that the remote Hawaiian Islands constitute a dispersal sink (
The present study provides unprecedented insight into the relationships of Hawaiian Melicope. Several previous findings could be corroborated and firmly supported by genome-wide data, including the non-monophyly of most of Stone’s sections, which cannot be held up as delimited (Stone, 1969; Stone et al., 1999). The lineage is in need of a taxonomic revision. Understanding the relationships of Hawaiian Melicope would be enhanced by some formal recognition of the subclades with corresponding morphological features. However, the creation of novel formal subgroups within Melicope section Pelea must also include the extra-Hawaiian members of the section. The former genus Platydesma is the most distinctive group within Melicope sect. Pelea and should receive some level of formal recognition. Apocarpa species need to be split into two groups, one of which would include the Marquesan species M. inopinata. However, conclusive treatment of Apocarpa should be adjourned until an improved understanding of the separation within the M. elliptica complex is attained. Delimitations of species within the Pelea group, M. barbigera, M. ovata, and M. haupuensis, may need revision, but levels of hybridization should also be investigated as part of that process. M. wawraeana requires revision as well as a prerequisite to test the putative hybrid character of the Marquesan radiation. Furthermore, the other six Melicope species endemic to the Marquesas Islands would need to be included in a novel taxonomic recognition of Stone’s former sections Megacarpa and Cubicarpa.
Funding
This project was financially supported by the German Science Foundation (DFG; Grant AP 251/3-1 to MA). The funder had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
Statements
Data availability statement
All demultiplexed raw read data were submitted to the NCBI Sequence Read Archive; BioProject number PRJNA559258.
Author contributions
MA, CP, and WW conceived and designed the study. MA, CP, and KW collected the samples. CP carried out the laboratory work and performed all analyses. DE provided valuable input for the analyses. CP drafted the manuscript, and all authors contributed to writing and editing. All authors have read and approved the final manuscript.
Acknowledgments
We are grateful to Charmian Dang for support with collection permits and to H. Alves, R. Belcher, S. Ching, K. Fay, K. Kosaka, S. Marquez, H. Oppenheimer, S. Perlman, J. Price, K. Range, T. Takahama, K. Togikawa, and A. Williams for help in collecting the specimens. We thank the United States Department of Land and Natural Resources (Permits: P-242, KPI2017-102, ODF-051316R, and MDF-092216A) for the permission to collect plants in forest reserves on Kauaʻi, Oʻahu, Maui, and Hawaiʻi (Big Island); the Nature Reserve for the permission to collect plants at the Waikamoi Preserve on Maui; the Puu Kukui Watershed Preserve for the permission to collect along the Puu Kukui Trail; and the United States Fish & Wildlife Service for the permission to export samples (Permit: MA96221B-O). We also thank Alice Tangerini for some pencil drawings of Stone’s sections of Melicope. The remaining drawings were reproduced from Otto Degener’s Flora Hawaiiensis (1960–1970). We thank two anonymous reviewers and Gonzalo N. Feliner for critical reading and suggestions that helped improved an earlier version of the manuscript.
Conflict of interest
The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
Supplementary material
The Supplementary Material for this article can be found online at: https://www.frontiersin.org/articles/10.3389/fpls.2019.01074/full#supplementary-material
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Summary
Keywords
adaptive radiation, D-statistics, Hawaiian flora, introgression, Marquesas Islands, Quartet Sampling, RAD-seq, Rutaceae
Citation
Paetzold C, Wood KR, Eaton DAR, Wagner WL and Appelhans MS (2019) Phylogeny of Hawaiian Melicope (Rutaceae): RAD-seq Resolves Species Relationships and Reveals Ancient Introgression. Front. Plant Sci. 10:1074. doi: 10.3389/fpls.2019.01074
Received
24 April 2019
Accepted
07 August 2019
Published
17 September 2019
Volume
10 - 2019
Edited by
Gonzalo Nieto Feliner, Real Jardín Botánico (RJB), Spain
Reviewed by
Ya Yang, University of Minnesota Twin Cities, United States; Mario Fernández-Mazuecos, Real Jardín Botánico (RJB), Spain
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© 2019 Paetzold, Wood, Eaton, Wagner and Appelhans.
This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.
*Correspondence: Claudia Paetzold, claudia.paetzold@uni-goettingen.de
This article was submitted to Plant Systematics and Evolution, a section of the journal Frontiers in Plant Science
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