Received: 13 June 2018
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Revised: 4 January 2019
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Accepted: 13 January 2019
DOI: 10.1111/jbi.13531
RESEARCH PAPER
Understanding the origin of the most isolated endemic reef
fish fauna of the Indo‐Pacific: Coral reef fishes of Rapa Nui
Erwan Delrieu-Trottin1
| Laura Brosseau-Acquaviva1 | Stefano Mona2,3 |
Valentina Neglia1 | Emily C. Giles1 | Cristian Rapu-Edmunds4 | Pablo Saenz-Agudelo1
1
Instituto de Ciencias Ambientales y
Evolutivas, Universidad Austral de Chile,
Valdivia, Chile
Abstract
Aim: To understand the origin of the most isolated endemic fish fauna of the Indo‐
2
Institut de Systématique, Evolution,
Biodiversité (ISYEB), UMR 7205 - CNRS,
MNHN, UPMC, EPHE, Ecole Pratique des
Hautes Etudes, Paris Sorbonne Universités,
Paris, France
3
EPHE, PSL Research University, Paris,
France
4
Mike Rapu Diving Center, Caleta Hanga
Roa O'tai, Isla de Pascua, Chile
Pacific, Easter Island (Rapa Nui), and to infer divergence times and colonization
routes of the endemic coral reef fish fauna from their closest relatives.
Location: Easter Island, Pacific Ocean.
Methods: Samples of ten species were used: six small‐range species endemic to
Rapa Nui and Motu Motiro Hiva (Salas y Gómez) (i.e. small‐range endemic species)
and four large‐range species endemic to the southern subtropical Pacific (i.e. large‐
range endemic species). We present phylogenetic reconstruction results based on
Correspondence
Erwan Delrieu-Trottin, Instituto de Ciencias
Ambientales y Evolutivas, Universidad
Austral de Chile, Valdivia, Chile.
Email: erwan.delrieu.trottin@gmail.com
mitochondrial (1 to 5) and nuclear (1 to 6) loci to place these endemic species in
their respective family phylogenies (8). Using these newly calibrated phylogenetic
trees, information of species distributions and geological data, we inferred the divergence times from the closest relatives of these ten endemic fishes, compared bio-
Funding information
Fondo Nacional de Desarrollo Científico y
Tecnológico, Grant/Award Number:
11140121, 3160692
geographical history estimation models to reconstruct their ancestral geographic
Editor: Cynthia Riginos
of the small‐range endemics studied were more recent than the age of Rapa Nui and
ranges, colonization routes and underlying mechanisms of speciation.
Results: The divergence times (i.e. divergence times from the closest relatives) of all
Motu Motiro Hiva; thus, these species can be considered as neoendemics. Biogeographical history estimation models indicated that speciation following a founder‐
event is the most likely scenario. In contrast, the divergence estimates of the large‐
range endemic species were highly variable. This being said, the divergence times of
all species were more recent than the age of the oldest islands within their distributions.
Main conclusions: Taken together, these results demonstrate that Rapa Nui acts as
a cradle of coral reef biodiversity, being responsible for the emergence of small‐
range endemic fish species, but also a route of dispersion for several large‐range
endemics and as a stepping stone in the diversification of the Myripristis and Pseudolabrus genera. While no common divergence time was recovered for all of the ten
endemic species studied here, the common mechanism of speciation following a
founder event was recovered for most of the small‐range endemic species.
KEYWORDS
coral reef fishes, Easter Island, endemism, neoendemism, phylogeny
Journal of Biogeography. 2019;1–11.
wileyonlinelibrary.com/journal/jbi
© 2019 John Wiley & Sons Ltd
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1 | INTRODUCTION
DELRIEU‐TROTTIN
ET AL.
as ecological conditions evolve through space and time (Anderson,
1994; Kruckeberg & Rabinovitz, 1985; Pigot, Owens, & Orme,
One of the most striking aspects of coral reef fishes is their particu-
2012). In practical terms, palaeoendemic species should be distin-
larly uneven geographic distributions where species diversity is high-
guishable from neo or ecological endemics as these should display
est in the Indo‐Australian Archipelago (IAA) and tends to decline
deep divergence times with signals of contraction. In contrast,
with latitude and longitude (Bellwood & Meyer, 2009; Bellwood &
neoendemics and ecological endemics are more challenging to tell
Wainwright, 2002; Mora et al., 2003; Reaka, Rodgers, & Kudla,
apart (Cowman, Parravicini, Kulbicki, & Floeter, 2017), and are not
2008). Of particular interest are endemism hotspots, which are geo-
necessarily mutually exclusive. A species could be young and
graphic regions that harbor an unusually high number of species that
restricted to a specific geographic area because it arose as the pro-
have restricted geographic distributions (Anderson, 1994) and that
duct of local adaptation to particular environmental conditions.
are found in the periphery of the IAA (Allen, 2008; Bellwood &
Overall and despite the complexity of how endemic species origi-
Wainwright, 2002; Hughes, Bellwood, & Connolly, 2002). For
nate, understanding whether endemic species are the product of
instance, despite their relatively low species diversity, the Hawai'ian
recent speciation or ancestral extinctions is of great importance to
archipelago, Rapa Nui (Easter Island), the Marquesas Islands and the
assess their likelihood of extinction (Myers, Mittermeier, Mittermeier,
Red Sea have an unusually high proportion of endemic species with
da Fonseca, & Kent, 2000). For instance, small‐range size is one of
14%–25% of their fish communities being endemics (Delrieu‐Trottin
the characteristics that defines endemics and is also used to deter-
et al., 2015; Randall, 2005, 2007; Randall & Cea, 2011). These par-
mine if a species is likely to be threatened or to become extinct (Pin-
ticular regions constitute centres of endemism in the Indo‐Pacific
heiro et al., 2017). In addition, regions that have unusual proportions
region and have been an important part in a long‐standing debate
of endemic species (centres of endemism) have been proposed as
regarding the origin and current patterns of the biodiversity of Indo‐
conservation priorities (Roberts et al., 2002) because they can harbor
Pacific coral reefs. From this debate, two major hypotheses have
both genetic novelty (neoendemics) and genetic history (paeloen-
emerged to explain the current distribution of coral reef biodiversity.
demics). Thus, despite the fact that elucidating how a species origi-
One proposes the IAA as a Centre‐of‐Origin, a cradle of tropical mar-
nates remains challenging, elucidating their time of origin and their
ine biodiversity where lineages originate, and the other suggests that
demographic history is a first step towards this end. It can also help
the IAA is rather a Centre‐of‐Accumulation where distinct faunas the
to evaluate their risk of extinction and help to design and implement
Pacific and Indian Oceans overlap (Connolly, Bellwood, & Hughes,
conservation strategies accordingly (Foote et al., 2007).
2003; Hughes et al., 2002; Mora et al., 2003; Reaka et al., 2008).
In general, little information is available regarding the evolution-
Understanding the evolutionary history of endemic species from
ary processes that have shaped the histories of endemic fish species
peripheral centres of endemism can thus contribute to this ongoing
and thus the distribution of fish fauna in and among centres of
debate.
Endemism by definition should be described within a specific
endemism. From an evolutionary point of view, these centres have
spatial and temporal framework (Anderson, 1994). Spatially, this is
graveyards (palaeoendemism) of tropical marine biodiversity (Bowen,
done by defining the geographic boundaries or ecological character-
Rocha, Toonen, & Karl, 2013). However, the mechanisms by which
istics of the area that encompass a specific species distribution. Tem-
these reservoirs of endemic fish species have been generated are
porally, endemic species have long been classified as either old or
not well characterized. Only a handful of studies have analysed
new endemics (Engler, 1882) and alternative hypothesis have been
divergence times and distribution of coral reef fishes to infer
proposed to explain their current endemic status. One of these
whether areas were hosting neoendemics or palaeoendemics (e.g.
hypotheses suggests that endemic species occupy a restricted geo-
Cowman et al., 2017; Hodge, van Herwerden, & Bellwood, 2014;
graphic area because they are young and newly established species
Pinheiro et al., 2017). These studies have found that endemic spe-
(neoendemic species) (Willis, 1922). The alternative hypothesis sug-
cies display a wide range of divergence times and so far support
gests that endemic species are the remnants of an ancestral wide-
both the palaeo and neoendemism hypothesis. However, whether
spread species (palaeoendemic species) (Stebbins & Major, 1965).
these emerging patterns can be generalized remains an open ques-
Both of these hypotheses imply changes in the demographic history
tion as divergence times for most endemic species still remain
of the species that in turn should leave detectable genetic footprints
unknown.
been proposed to be either evolutionary cradles (neoendemism) or
(signals of expansion or contraction). These hypotheses are thus
Rapa Nui (Easter Island, Chile) is among the most remote islands
compatible with classical neutral models of speciation (allopatric,
on Earth and is the most isolated tropical island of the Pacific Ocean.
parapatric and peripatric speciation). However, it has also been sug-
Located at 27°07′10 S and 109°21′17 W in the Pacific, Rapa Nui
gested that endemic species can arise by ecological speciation via
lies 3,700 km from South America and 2,100 km east of the Pitcairn
local adaptation (“Gene pool—Ecological niche interaction hypothe-
Islands. This small triangular island (166 km2) and the islet Motu
sis” sensu Stebbins (1980)). Under this hypothesis, the distribution of
Motiro Hiva (Salas y Gómez, 0.15 km2), located 400 km further east,
endemic species is restrained by the availability of specific ecological
are the easternmost islands of Polynesia. Rapa Nui and Motu Motiro
conditions. Endemics arising from ecological speciation could main-
Hiva constitute the only two emerged islands of the Easter Chain
tain or expand their range size throughout their evolutionary history
that also includes dozens of seamounts extending 2,232 km east
DELRIEU‐TROTTIN
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ET AL.
3
until the Nazca seamount (23°360 S et 83°300 W) (Clouard & Bon-
at the origins of new genetically isolated lineages. Alternatively,
neville, 2005; Ray et al., 2012). Due to a subtropical gyre, the mean
finding divergence times for Rapa Nui endemic species older than
current field in the Rapa Nui region is to the east, favouring the trans-
the age of this island and no historical biogeographical support for
portation of waters from southern Pacific islands to Rapa Nui (Marti-
founder‐event speciation would indicate that the island represents
nez, Maamaatuaiahutapu, & Taillandier, 2009) and more locally from
a refuge of biodiversity that originated elsewhere. In the following
Rapa Nui to Motu Motiro Hiva (Andrade, Hormazabal, & Correa
sections, we test these predictions to resolve the evolutionary his-
Ramirez, 2014). The two islands are relatively young. Vezzoli and Aco-
tories of ten endemic species from eight different families. We
cella (2009) date Rapa Nui as being 0.8 My while Clouard and Bon-
place these species with their presumed sister species within cur-
neville (2005) date Rapa Nui as being 2.5 My and Motu Motiro Hiva
rently available phylogenies constructed using mitochondrial and
as being 1.7 My. The fish fauna of these two islands, which mainly
nuclear loci and reconstruct their biogeographical history. We dis-
consists of coral reef fishes, is notable for its low diversity and high
cuss the potential underlying evolutionary processes that led to
proportion of endemic species. Randall and Cea (2011) have identified
present‐day patterns.
a total of 169 fish species (139 shore fishes), this being an order of
magnitude lower than that found in the Hawai'ian Islands (1,250 species) or in Indonesia (3,000) (Allen & Erdmann, 2012). Of the fish species, 21.7% found in Rapa Nui are endemic to this island (Cea, 2016;
Randall & Cea, 2011). Overall, little is known regarding the evolution-
2 | MATERIALS AND METHODS
2.1 | Selection of taxa and specimen collection
ary history of the island's fish fauna though three of the 30 endemic
Randall and Cea (2011) have reported 30 fish species as endemic to
species of Rapa Nui are estimated to have diverged from their closest
Rapa Nui and 17 fish species as southern subtropical species. The
relatives 2.6 > Mya (Cowman et al., 2017).
defined Rapa Nui endemics are only present around Rapa Nui and
This study aims to shed light on the evolutionary history of the
Motu Motiro Hiva and have small ranges (<500 km in linear dis-
endemic reef fish fauna of Rapa Nui. In this context, we refer to
tance, see Delrieu‐Trottin, Maynard, & Planes, 2014). The southern
neoendemic species as those species with divergence times post‐
subtropical species or regional endemics (see Friedlander et al.,
dating the origin of the island of Rapa Nui (this means that most
2013) have large ranges (1,000–8,000 km in linear distance, see Del-
likely they originated on the island during or after its appearance;
rieu‐Trottin et al., 2014) and are usually distributed from Southern
2.5 My). We refer to palaeoendemics as those species with diver-
Polynesia to Rapa Nui. We referenced all of the presumed sister
gence times that pre‐date the formation of Rapa Nui (meaning that
species of the 47 species of these two groups using species descrip-
most likely they originated elsewhere, colonized the island and
tions of endemic species and books of reference (Randall, 2005,
went extinct everywhere else). We anticipated that if Rapa Nui
2007; Randall & Cea, 2011). To avoid overestimating divergence
constitutes a cradle of coral reef biodiversity, a) divergence times
dates, it was essential that the phylogenies contained all the pre-
for endemic species should post‐date the formation of Rapa Nui; b)
sumed sister species of each endemic species. Of the 47 species
we should find historical biogeographical evidence that supports
investigated, complete information was only available for nine spe-
founder‐event speciation models, that is, rare jump dispersal events
cies; four large‐range endemic species: Centropyge hotumatua
T A B L E 1 Distribution of the endemic species (Rapa Nui name) under study and of their presumed sister species based on morphology
Species & Distribution
Sister species
Cantherhines rapanui (koreva) RN + MMH
Species complex with C. fronticictus (East coast of Africa to the Marshall Is.), C. verecundus
(Hawai'ian Is.), C. longicaudus (Cook Is. and Society Is.) (Randall, 2005; Siu et al., 2017)
Chromis randalli (mamata) RN + MMH
Chromis pamae (Austral Is., and RI, Gambier Is., Pitcairn) (Randall, 2005)
Chaetodon litus (tipi tipi ‘uri) RN + MMH
C. smithi (RI and Pitcairn) (Randall & Caldwell, 1973)
Coris debueni (teteme) RN + MMH
Species complex with C. caudimaculata (Indian Ocean), C. dorsomaculata (western Pacific), C.
roseoviridis (Cook Is. to Pitcairn), C. venusta (Hawai'ian Is.) (Randall & Cea, 2011)
Kuhlia nutabunda (mahore) RN + MMH
K. sandvicensis (Pacific Ocean) (Randall & Cea, 2011)
Chrysiptera rapanui (mamata) RN + MMH
Chrystiptera galba (Austral Is., Gambier Is. and Pitcairn) (Randall, 2005)
Centropyge hotumatua (kototi para) RN+
MMH + Pitcairn + RI+ Australs
Species complex with C. multicolor (Central Pacific), C. interrupta (Japan and Hawai'ian Is.), C.
joculator (Coco & Christmas Is.), C. nahackyi (Johnston atoll), C. debelius (Mauritius) (Pyle, 2003)
Cheilodactylus plessisi (ra'ea) RN + MMH + RI
C. zebra (Japon), C. francisi (Lord Howe Is. to New Caledonia) & C. vittatus (Hawai'ian Is.) Burridge,
2004)
Myripristis tiki (marau) RN + MMI + Pitcairn + RI
M. amaena (Japan to Pitcairn) (Greenfield, 1974)
Pseudolabrus fuentesis (kotea) RN +
MMH+ Pitcairn + RI+ Australs
Pseudolabrus gayi (Juan Fernandez Is. and Desventudaras Is.) (Russell & Randall, 1980)
RN: Rapa Nui; MMH: Motu Motiro Hiva; RI: Rapa Iti.
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DELRIEU‐TROTTIN
ET AL.
(Pomacanthidae), Cheilodactylus plessisi (Cheilodactylidae) Myripristis
Randall and Cea (2011). Upon collection, a small piece of fin tissue
tiki (Holocentridae), Pseudolabrus fuentesi (Labridae) and five small‐
was preserved in 96% EtOH.
range endemic species: Cantherhines rapanui (Monacanthidae), Chromis randalli, Chrysiptera rapanui (Pomacentridae), Coris debueni (Labridae) and Kuhlia nutabunda (Kuhliidae). We added a tenth species, the
2.2 | Laboratory procedures
small‐range endemic Chaetodon litus (Chaetodontidae), albeit no
Whole genomic DNA was extracted from fin tissue preserved in
genetic data are available for one of its presumed sister species to
96% EtOH at ambient temperature. DNA extraction was performed
obtain preliminary results regarding its evolutionary history (Table 1,
using the GeneJet Genomic DNA purification kit according to the
Figure 1). Sampling was performed using pole‐spears or an anaes-
manufacturer's protocols (Thermo Fisher Scientific). For each species,
thetic (clove oil) while SCUBA diving around Rapa Nui in October
we amplified the same gene fragments using the corresponding pri-
2016. Identification of collected specimens was done according to
mers as used in previously generated phylogenies. It is worth noting
(a)
(b)
(c)
F I G U R E 1 Geographic distribution of the species under study and divergence times from their closest relatives. (a) Geographic distributions
of large‐range endemic species and of (b) small‐range endemic species in this study. The large‐range endemics have larger distributions while
the small‐range endemics are only present around Rapa Nui and Motu Motiro Hiva (MMH) (see Table 1 for detailed distributions). The map
was generated using the R package ggplot2 (Wickham, 2009) and drawn with rectangular projection (c) Divergence times of species endemic
to Rapa Nui from their closest relatives. Median (dot) and 95 % HPD (lines) are represented. Colors denote the distribution. Vertical dotted
lines represent the age of the oldest emerged island of the archipelago (Austral Islands: 12 Ma, Gambier Islands: 8 Ma and Pitcairn: 1 Ma
Clouard and Bonneville (2005); Vezzoli and Acocella (2009)). An asterix next to the species name indicates that there was strong statistical
support for jump dispersal according to the Biogeographical history estimation models
DELRIEU‐TROTTIN
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ET AL.
that we also generated molecular data for three presumed sister spe-
5
& Gibson, 1994) or MAFFT (Katoh & Standley, 2013) and edited
cies, Chrysiptera galba (presumed sister species of C. rapanui), Chro-
using
mis pamae (presumed sister species of C. randalli) and Coris roseovidis
(2012)).
GENEIOUS
9.0.5
(http://www.geneious.com,
Kearse
et al.
(presumed sister species of C. debueni) to complete the dataset (see
Maximum Likelihood (ML) analyses were performed for all of the
Table 2 for details). Fragments were amplified using PCR protocols
families under study using the online version of IQ‐TREE (Minh,
and sequencing as described by Williams, Delrieu‐Trottin, and Planes
Nguyen, & von Haeseler, 2013; Nguyen, Schmidt, Von Haeseler, &
(2012).
Minh, 2015) available at http://iqtree.cibiv.univie.ac.at (Trifinopoulos,
Nguyen, von Haeseler, & Minh, 2016). The best model of evolution
2.3 | Phylogeny
of each gene was retrieved with ModelFinder (Kalyaanamoorthy,
All generated sequences were desposited in GenBank (Accession
TREE using the Bayesian Information Criterion (BIC) prior to the
numbers: MK100716‐MK100761). Species were placed in the phylo-
construction of the ML trees (see Appendix S1 in Supporting Infor-
Minh, Wong, Von Haeseler, & Jermiin, 2017) implemented in IQ‐
genies of cheilodactylids (Burridge & Smolenski, 2004), holocentrids
mation Table S1). To assess branch support, all IQ‐TREE analyses
(Dornburg et al., 2012), kuhliids (Feutry et al., 2013), monacanthids
included the ultrafast bootstrap approximation (UFboot) with 1000
(Santini, Sorenson, & Alfaro, 2013), pomacanthids (Gaither et al.,
replicates (Minh et al., 2013) and the SH‐like approximate likelihood
2014) and pomancentrids (Frédérich, Sorenson, Santini, Slater, &
ratio test (SH‐aLRT) also with 1,000 bootstrap replicates (Guindon et
Alfaro, 2013) while several phylogenies were used to compose the
al., 2010). The time‐calibrated phylogenies (BI) were constructed
dataset of chaetodontids (Cowman and Bellwood (2011) for eight of
with the software BEAST2 2.4.6 (Bouckaert et al., 2014) using the
the nine genes and Gaboriau, Leprieur, Mouillot, and Hubert (2018)
fossil calibrations of each phylogeny. We used secondary calibration
for COI). For labrids, we used the 12S, 16S, Tmo‐4C4, RAG2, S7 and
points from the Actinopterigian super‐phylogeny (Near et al., 2013)
COI genes as described in Aiello, Westneat, and Hale (2017) and fol-
when studies did not include time‐trees (Table S2). In the same way,
lowed the methodology of Wainwright et al. (2018): we included
we used tree priors (Yule model for all the analyses except for
only a few representatives of all genuses other than that of the tar-
pomacentrids (Birth‐Death model)) and partitioning (by individual
get species (Table 2). This strategy allowed us to optimize computa-
molecular markers for all analysis except for pomacentrids (all genes
tion time without compromising the accuracy of divergence date
concatenated)) according to the reference phylogenies while the sub-
estimates.
stitution models were selected according to the ModelFinder results
We accessed sequence data stored in GenBank (https://www.
using the SSM 1.1.0 package in BEAUti (Bouckaert & Xie, 2017)
ncbi.nlm.nih.gov/genbank/) for each coral reef fish family using the R
Table S1). We used a relaxed log normal clock model as the molecu-
package seqinr (Charif & Lobry, 2007). The endemic species Kuhlia
lar clock. The number of generations was set to reach analysis con-
nutabunda and Cheilodactylus plessisi were already present in the
vergence (Table S2). We assessed the convergence and appropriate
phylogenies of their genera, so we did not add sequences for these
burn‐in of each analysis using TRACER 1.5 (Drummond & Rambaut,
species. Sequences were aligned with Clustal W (Thompson, Higgins,
2007). Three independent analyses were run to ensure convergence.
T A B L E 2 Loci used and total number of species included in each phylogeny to place endemic species in their respective phylogenies. In
bold are loci that amplified successfully (Accession numbers MK100716‐MK100761). In italics are loci that were already published.
Phylogenies of Cowman and Bellwood (2011)1; Gaboriau et al. (2018)2; Burridge and Smolenski (2004)3; Dornburg et al. (2012)4; Feutry et al.
(2013)5; Westneat and Alfaro (2005)6; Aiello et al. (2017)7; Santini et al. (2013)8; Gaither et al. (2014)9; Frédérich et al. (2013)10
Family
Chaetodon litus
1,2
Cheilodactylus plessisi3
Myripristis tiki
4
Kuhlia nutabunda5
Coris debueni
6,7
Coris roseoviridis6,7
Pseudolabrus fuentesi
6,7
Cantherhines rapanui8
Genes
Nb of sp included
12S, 16S, COI, Cytb, ETS2, ND3, Rag2, S7, TMO4C4
122
COI, Cytb
30
COI, ENC1, Glyt, Myh6, Ptr, Rag1, Sreb
42
COI, Rh, 16S, Tmo4c4, IRBP
37
12S, 16S, Rag2, COI, Tmo4c4
105
12S, 16S, Rag2, COI, Tmo4c4
105
12S, 16S, Rag2, COI, Tmo4c4
105
COI, Cytb, Myh6, Rag1, Rh
9
94
Centropyge hotumatua
COI, Cytb, Rag2, S7, Tmo4C4
121
Chromis randalli10
COI, Cytb, 12S, 16S, Bmp4, Nd3, Rag1, Rag2
163
Chrysiptera rapanui10
COI, Cytb, 12S, 16S, Bmp4, Nd3, Rag1, Rag2
163
Chrysiptera galba
COI, Cytb, 12S, 16S, Bmp4, Nd3, Rag1, Rag2
163
Chromis pamae10
COI, Cytb, 12S, 16S, Bmp4, Nd3, Rag1, Rag2
163
10
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DELRIEU‐TROTTIN
ET AL.
We constructed a maximum clade credibility tree using TREEANNOTA-
colonization of the Juan Fernandez Islands by Pseudolabrus fuentesis
1.8.1 (Drummond & Rambaut, 2007) to get median ages and
(2 Ma, Clouard & Bonneville, 2005) and of the Marquesas Islands by
95% highest posterior density (HPD) intervals for each node. The
Cantherhines, Kuhlia and Myripristis (5.5 Ma, Clouard & Bonneville,
95% HPD represents the smallest interval that contains 95% of the
2005). For each analysis, we set the maximum number of ancestral
posterior probability and can be loosely thought of as a Bayesian
areas to the maximum number of areas inhabited by a single species.
TOR
analogue to a confidence interval (Gelman, Carlin, Stern, & Rubin,
2004).
3 | RESULTS
2.4 | Phylogeography
3.1 | Phylogenetic analysis
We used the R package BioGeoBEARS (Matzke, 2013) in R (R Core
We worked on aligned sequence matrices including 31 to 232 spe-
Team, 2017) to estimate the ancestral geographic ranges and to
cies per phylogeny and consisting of two to nine genes (932 to
investigate the biogeographical history of the endemic species. This
7157 base pairs per matrix) (Table 2).The ML analyses consistently
package includes three of the most common biogeographical history
returned the same tree topology across all runs with strong boot-
estimation models in a likelihood framework, that is, the Dispersal‐
strap support at most nodes (Figures S1–S8). Similarly, the Bayesian
Extinction‐Cladogenesis model (DEC; (Ree, Moore, Webb, & Dono-
analyses produced the same tree topology across all three runs with
ghue, 2005), DIspersal Vicariance Analysis (DIVA; (Ronquist, 1997)
high posterior probabilities (PP, Figures S9–S16). For all analyses
and the BayArea model (Landis, Matzke, Moore, & Huelsenbeck,
except those of Labridae and Pomacanthidae, parameters reached
2013). All of these models allow for anagenetic processes (range
effective sample sizes higher than 200 in the Bayesian inferences.
expansion and/or range contraction), but differ in the range of clado-
For Labridae and Pomacanthidae, most parameters reached effective
genetic processes that are permitted (vicariance/sympatry) among/
sample sizes higher than 200 and only few parameters had ESS
within‐areas or single areas. As an example, all models allow for a
within 100 and 200.
sympatry event within one area, but only the DEC model allows for
For all eight families under study, we found topologies congruent
sympatry event within a subset of the range of a species. In the
with those of the published reference phylogenies. For eight of the
same manner, only the DEC and the DIVA models allow for a vicari-
ten endemic species of this study, the Maximum Likelihood analysis
ance event within a subset of the range of a species, and only the
and the Bayesian analysis retrieved the same topology. Differences
DIVA model allows for a vicariance event resulting in the existence
among the ML and BI topologies were observed between Cantherhi-
of species with multiple areas; but see the supermodel figure of
nes rapanui and Coris debueni and their closest relatives.
Matzke for more details (2015). Here, we assessed the fit of each of
Large‐range endemic species were found among species‐rich
the different models using the corrected Akaike information criterion
clades (Cheilodactylus plessisi and Pseudolabrus fuentesi) but also
(AICc). The three models were tested including or not a “jump dis-
among species poor clades (Centropyge hotumatua and Myripristis tiki)
persal” parameter J that permits founder‐event speciation in the spe-
while all small‐range endemic species were part of species‐rich
cies's history (Paulay & Meyer, 2002; Templeton, 2008). Founder‐
clades. Several of the species presumed to be sister species based
event speciation is the result of a long‐distance colonization event of
on morphology were confirmed by the molecular analysis (Chromis
a small number of individuals founding a population that is then
randalli / C. pamae; Chrysiptera rapanui / C. galba; Kuhlia nutabunda /
genetically isolated from the ancestral population; these events have
K. sandvichensis; Pseudolabrus fuentesi / P. gayi).
been shown to be common in island systems (Matzke, 2014). Bio-
Our molecular analysis helped to resolve five species complexes
GeoBEARS requires a clade including the endemic species and all of
that to date are recognized as polytomies. First, our results clearly
its closely related species as an input. We used the maximum clade
show that Coris debueni is closely related to Coris roseoviridis, a
credibility tree from BEAST2 that we obtained for each family and
Southern endemic species distributed from the Cook Islands to Pit-
extracted the clade of interest using the R package ape 5.0 (Paradis,
cairn (Table 1). Second, Cantherhines rapanui is part of a four‐species
Claude, & Strimmer, 2004). The geographic ranges of each species
complex that was poorly resolved by the ML analysis, yet the BI
were coded with one or more areas.
showed that C. rapanui is closely related to C. longicaudus (Cook Is.
Finally, given that the colonization of an island before its exis-
and Society Is.). Third, for Cheilodactylus plessisi, both the BI and ML
tence is technically impossible, and before its emergence is unlikely,
analyses placed it as the closest relative to C. vittatus from Hawai'i.
we constrained the timing of dispersal as 1.7 Ma and 2.5 Ma for
Fourth, by adding Centropyge hotumatua to the phylogeny of
Motu Motiro Hiva and Rapa Nui respectively (“area allowed” param-
Pomacanthidae, we show that the position of Centropyge hotumatua
eter in BioGeoBEARS). Thus, this resulted in the removal of those
is not within the “multicolour” complex as previously thought. Both
areas in the ancestral range estimation of nodes that were older than
the ML and BI placed C. hotumatua at the base of the “multicolour”
the ages of these islands. We chose to implement the oldest age
and “bispinosa” complexes. The BI indicated that C. hotumatua is the
estimate for Rapa Nui to try to balance the fact that BioGeoBEARS
closest relative of the Hawai'ian endemic C. potteri. Fifth and last,
cannot take into account the 95% highest posterior density (HPD)
Myripristis tiki was not recovered as the closest relative of M.
intervals of each node. We also constrained the timings of
amaena. Instead both our BI and ML analyses provided strong
DELRIEU‐TROTTIN
|
ET AL.
7
support for M. tiki as the closest relative of M. leiognathus, a species
Australian species and a Juan‐Fernandez endemic species. Cheilo-
distributed in the Eastern Tropical Pacific (from Gulf of California to
dactylus plessisi, Chaetodon litus and Centropyge hotumatua were
Ecuador).
recovered as part of an antitropical clade with a close relative from
Finally,
acknowledging
that
the
current
available
Chaetodontidae phylogeny does not include Chaetodon smithi, our
Hawai'i. Finally, Kuhlia nutabunda was closely related to a species lar-
results indicate that Chaetodon litus is the closest relative to the
gely distributed in the Pacific while Myripristis tiki likely emerged
Hawai'ian endemic C. miliaris in a clade that also includes the West
from a founder‐event and was found to be related to an East Tropi-
Pacific species C. guentheri.
cal Pacific species.
3.2 | Dating divergence time between endemic
species and their closest relatives
4 | DISCUSSION
We generated time‐trees for the eight families studied here, and these
This study represents the first attempt to better understand the ori-
include the first‐ever generated time‐trees for Cheilodactylidae, Kuhli-
gin of Rapa Nui endemic reef fishes including all their presumed sis-
idae and Holocentridae. For chaetodontids, labrids, monacanthids,
ter species using newly computed time calibrated phylogenic data
pomacanthids and pomancentrids, the divergence times that we
and employing biogeographical analysis. Our results show that the
obtained between species for the internal nodes of the maximum
coral reef fishes endemic to Rapa Nui have diverse evolutionary his-
clade credibility trees were similar to those of the available published
tories and two trends seem to emerge strongly related to the type
phylogenies. Overall, we obtained divergence times between endemic
of range distribution: (a) Species strictly endemic to Rapa Nui (small‐
species and their closest relatives that ranged from 0.54 Ma (0.07–
range endemic species) have divergence dates with their closest rela-
1.3, 95% HPD, Cantherhines rapanui) to 9.52 Ma (6.77–12.4, 95%
tives that are less than the geological age of Motu Motiro Hiva and
HPD, Myripristis tiki) (Figure 1, Figures S9–S16).
Rapa Nui and thus can be considered as neoendemic species that
We observed that all of the divergence estimates for the small‐
likely emerged from a founder‐event. Additionally, these species
range endemic species (Cantherhines rapanui, Chaetodon litus, Chromis
have sister species with restricted distributions only in the central
randalli, Chrysiptera rapanui, Coris debueni, Kuhlia nutabunda) were less
south Pacific Islands (Austral Islands, Gambier Islands, Rapa Iti, Pit-
than the geological ages of Motu Motiro Hiva (1.7 Ma) and Rapa Nui
cairn). (b) Large‐range endemic species have divergence times with
(2.5–0.8 Ma). We observed a wider range of divergence times for the
their closest relatives that differ drastically (up to an order of magni-
large‐range endemic species and species with divergence times older
tude), and their sister species are widely distributed among the
than Rapa Nui and Motu Motiro Hiva include Cheilodactylus plessisi
Hawai'ian Islands, East Pacific and Central Pacific.
with 2.80 Ma (0.88–4.00% HPD), Centropyge hotumatua with 6.29 Ma
The posterior distribution of divergence times (HPD) between
(4.46–8.25 Ma 95% HPD) and Myripristis tiki with 9.52 Ma (6.77–
endemic species and their sister species should be compared to the
12.4 Ma 95% HPD). Despite these results, we also found a large‐
geological ages of the islands where endemic species are found. An
range endemic species with divergence times that were younger than
HPD smaller or containing the values of the geological age of the
the geological ages of Motu Motiro‐Hiva and Rapa Nui (Pseudolabrus
island where the endemic species is found should support neoen-
fuentesi 2.21 Ma (0.88–4.21% HPD)). None of the species under study
demism while HPDs encompassing older ages should support
had divergence times older than the oldest island that it inhabits (Aus-
palaeoendemism. From our phylogenetic reconstruction, we found
tral Islands: 12 Ma, Gambier Islands: 8 Ma, and Pitcairn: 1 Ma).
that most of the endemic species emerged since the Pliocene (5 Ma),
which was a period of high diversification of coral reef fishes in the
3.3 | Phylogeography
Indo‐Australian Archipelago (Alfaro, Santini, & Brock, 2007; Cowman
& Bellwood, 2011; Hodge, Read, van Herwerden, & Bellwood, 2012;
The BioGeoBEARS analyses of the maximum clade credibility trees
Hodge et al., 2014; Klanten, van Herwerden, Choat, & Blair, 2004).
allowed us to estimate the ancestral range and the evolutionary ori-
Geological data suggest that Rapa Nui emerged between 2.5 and
gin of the different endemic species (Figure S17–S25). Interestingly,
0.8 M ago while Motu Motiro Hiva is dated at 1.7 Ma (Clouard &
the majority (7/9) of the best‐fitting models included a founder‐event
Bonneville, 2005; Vezzoli & Acocella, 2009). Based on these dates,
(+J) (BayAreaLike+J for Myripristis tiki and Chrysiptera rapanui; DIVA-
more than half of the species (6 out of 10) are strictly younger than
Like+J for Cantherhines rapanui, Coris debueni and Cheilodactylus ples-
Rapa Nui and most (8 out of 10) have HPDs that encompass the age
sisi; DEC+J for Chromis randalli and Centropyge hotumatua, Table S3).
of Rapa Nui. Additionally, we have found that only Myripristis tiki and
Overall, BioGeoBEARS analyses showed that the best‐fitting
Centropyge hotumatua, two large‐range endemics, are older (both the
model was very often the one including a founder‐event speciation
median and HPD bounds) than Rapa Nui. Overall, the estimated diver-
process. Four of the small‐range endemic species (Chromis randalli,
gence times between the small‐range endemic species and their sister
Chrysiptera rapanui, Coris debueni and Cantherhines rapanui) were clo-
species taken together with the geological data indicate that most of
sely related to species distributed in the South Pacific Islands (Aus-
these species are likely neoendemics.
trals Islands, Gambier Islands, and Pitcairn) and likely emerged from
Founder‐event speciation was expected for neoendemic species
a founder‐event. Pseudolabrus fuentesi was closely related to an East
while range contraction was expected for palaeoendemic species.
8
|
DELRIEU‐TROTTIN
ET AL.
Using phylogenies to disentangle the biogeographical histories of
neoendemism from palaeoendemism in Rapa Nui as contrasting
species is a complex task (Heads, 2009), and estimating the internal
levels of abundance are found even among neoendemics.
nodes of the phylogenies generated here proved difficult. Despite
Taken together, our results indicate that Rapa Nui acts as a cra-
this, the analyses indicated that most of the models selected (7/9
dle of coral reef biodiversity, being responsible of the emergence of
analysis) included a founder‐event, which have been shown to be of
small‐range endemic fish species. We have found a common specia-
prime importance in other island systems (Matzke, 2014; see Litsios,
tion mechanism for the small‐range endemic species, highlighting the
Pearman, Lanterbecq, Tolou, & Salamin, 2014; Pinheiro et al., 2017
importance of founder events. Such results are of high importance
and Wainwright et al., 2018 for examples). Overall, our biogeograph-
from a conservation point of view: Rapa Nui and Motu Motiro‐Hiva
ical analyses show that dispersal and founder‐event speciation
constitute centres of endemism in the Indo‐Pacific region and are
played a major role in the colonization of Rapa Nui. For the small‐
among the most unique marine environments in the Pacific. The cre-
range endemics, two speciation schemes can be recognized. First, a
ation of a Marine Protected Area in 2018 excluding extractive indus-
southern Pacific species diverged from a largely distributed species
tries and industrial fishing is an important first step towards the
and then colonized and diverged in Rapa Nui via a founder event.
conservation of this centre of speciation.
This scenario is likely for Coris debueni, Chrysiptera rapanui and Chromis randalli. All three species have a sister species distributed in several islands of the South Pacific (from Australs to Pitcairn), and the
ACKNOWLEDGEMENTS
emergence of the Rapa Nui archipelago was very likely followed by
We thank Rebeca Tepano, Nina, Taveke Olivares Rapu, Liza Garrido
colonization and divergence. This scenario is also very likely for
Toleado (SERNAPESCA), Ludovic Burns Tuki (Mesa del Mar), and the
Chaetodon litus whose presumed sister species, the Southern ende-
people of the Rapa Nui Island for their kind and generous support.
mic species C. smithi (Randall & Caldwell, 1973), is absent from our
This study was funded by FONDECYT Postdoctorado fellowship
dataset. Second, a largely distributed species colonized and diverged
N°3160692 to E. Delrieu‐Trottin and FONDECYT Iniciación fellow-
in Rapa Nui through a founder event, a scenario that is likely for
ship N°11140121 to P. Saenz‐Agudelo. The authors declare no con-
Kuhlia nutabunda and Cantherhines rapanui. This scenario differs from
flict of interest. All applicable institutional guidelines for the care and
the first in that the largely distributed species (Cantherines longi-
use of animals were followed. Specimens were collected under per-
caudus and Kuhlia sandvicensis) colonized the southern islands of the
mit No. 724, 8 March 2016 obtained from the Chilean Subsecretary
Pacific but not Rapa Nui.
of Fishing. The Universidad Austral de Chile Ethical Care Committee
Finally, given the young age of Rapa Nui compared to the Austral
and Biosecurity Protocol approved our use and handling of animals.
Islands (20 Ma; Clouard & Bonneville, 2005), Rapa Nui has likely rep-
Finally, we thank C. Riginos, H. Pinheiro and three anonymous
resented a new area for the colonization of the large‐range endemic
reviewers for providing constructive reviews of earlier versions of
species included in this study (Myripristis tiki, Pseudolabrus fuentesi,
the manuscript.
Centropyge hotumatua, Cheilodactylus plessisi). Rapa Nui could have
acted as a stepping stone in the diversification of the Myripristis and
Pseudolabrus genera; Myripristis tiki and Pseudolabrus fuentesi are pos-
DATA ACCESSIBILITY
sible links between the fauna of the Tropical Eastern Pacific, of Juan
These sequence data have been submitted to the GenBank data-
Fernandez and of the Desventuradas islands.
bases under accession numbers MK100716‐MK100761. All the .tree
Local abundance and geographical range size are not correlated
files from ML and Bayesian analyses are available on FigShare
in marine fishes (Hobbs, Jones, & Munday, 2011; Hughes, Bellwood,
(https://figshare.com/s/2c45e9f680ddf96632b7;
Connolly, Cornell, & Karlson, 2014). Indeed, many marine endemic
m9.figshare.7643132).
https://10.6084/
reef fish are abundant (Delrieu‐Trottin et al., 2014; Hobbs, Jones,
Munday, Connolly, & Srinivasan, 2012) and the local population size
of small‐range endemics can be an order of magnitude greater than
the population size of widespread species at the same location
ORCID
Erwan Delrieu-Trottin
http://orcid.org/0000-0002-4120-9316
(Hobbs, 2010). Similar to what has been found in Hawai'i (DeMartini
& Friedlander, 2004; Kosaki et al., 2017) and the Marquesas islands
(Delrieu‐Trottin et al., 2015), the endemic fishes of Rapa Nui constitute a major component of the total assemblage. According to Friedlander et al. (2013), the small‐range endemic species Chromis randalli,
Chrysiptera rapanui and Chaetodon litus are among the most abundant species in Rapa Nui, and here we show that all three have
HPDs that are younger or encompassing the geological age of Rapa
Nui and Motu Motiro‐Hiva. In contrast, we found Kuhlia nutabunda
to have a similar HPD, yet it is rather rare on the island. Overall,
abundance does not seem to be a good proxy to differentiate
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https://doi.org/10.5962/bhl.title.70451
BIOSKETCHES
Erwan Delrieu‐Trottin is broadly interested in molecular ecology
and the evolution of fishes.
Stefano Mona and Pablo Saenz‐Agudelo are interested broadly
in population genetics.
Laura Brosseau‐Acquaviva and Cristian Rapu Edmunds are interested in conservation.
Valentina Neglia and Emily Giles are interested in the ecology
and molecular ecology of marine organisms.
Author contributions: E.D.T. and P.S.A. conceived the project;
E.D.T., V.N., C.R.E., E.C.G. and P.S.A. designed and conducted
sampling; E.D.T. and L.B.A. performed molecular experiments;
E.D.T. and L.B.A. analysed and interpreted the data; E.D.T. wrote
the first draft and all co‐authors contributed.
SUPPORTING INFORMATION
Additional supporting information may be found online in the
Supporting Information section at the end of the article.
How to cite this article: Delrieu-Trottin E, BrosseauAcquaviva L, Mona S, et al. Understanding the origin of the
most isolated endemic reef fish fauna of the Indo-Pacific:
Coral reef fishes of Rapa Nui. J Biogeogr. 2019;00:1–11.
https://doi.org/10.1111/jbi.13531