Abstract
The coastal South American species Cyprinodon dearborni contains two lineages distinct at both mitochondrial and nuclear loci. One appears to be a long-term South American endemic, whereas the other is a more recent colonizer related to the widespread Cyprinodon variegatus.
Keywords: Cyprinodon, mitochondrial DNA, nuclear DNA, phylogenetics, phylogeography, pupfish
Exceptions to well-marked biogeographic patterns can provide insights into factors that may have played an important role in the diversification of a group of organisms. The pupfish Cyprinodon dearborni Meek is a conspicuous exception to a very strong north–south complementary pattern: the oviparous killifishes of North and South America are sharply distinctive, and there is almost no overlap between them. Originally described from the island of Curaçao, off the western Venezuelan coast (Meek, 1909), C. dearborni is not a well-studied species. Its reported coastal distribution extends from the Guajira Peninsula (12° 25′ N; 71° 30′ W) in Colombia to Isla de Margarita, Venezuela (11° 00′ N; 64° 00′ W), and includes Lago Maracaibo and environs, the islands of Curacao, Aruba, Bonaire and Los Roques, and several interior Venezuelan lakes. Unconfirmed records from northwest Colombia, Trinidad and Guyana (Wildekamp, 1995) suggest the possibility of an even more extensive distribution along the South American coast. Besides C. dearborni, and the endemic genus Orestias of the Andean altiplano, all other pupfishes (including all other species of Cyprinodon) and related genera (e.g. Jordanella) are nearctic or Caribbean in distribution (Nirchio et al., 2003). In fact, most South American killifishes are rivulids (Rivulus, Cynolebias and allied genera) and are more closely related to the aplocheilid killifishes of Africa and Asia than to any nearctic group (Parenti, 1981).
Intuitively, its novel distribution relative to its congeners implicitly suggests that C. dearborni probably stems from a single colonization of the South American coast by some ancestral (Caribbean) pupfish. Previous molecular data (Echelle et al., 2005, 2006), derived from a specimen from Bonaire, were consistent with a single, recent colonization event, for they placed the species within a well-resolved ‘maritime clade’ of North American coastal and Caribbean forms related to Cyprinodon variegatus (Lacépède) in the broadest sense. This colonization event would seemingly have occurred across a gap in the current distribution of the maritime clade in the Southern Caribbean, as Cyprinodon artifrons Hubbs, a coastal species with an intervening distribution, is far more divergent from members of the maritime clade (Echelle et al., 2005). As sampling to date, however, has been limited, diversity in Cyprinodon along the South American coastline may have been underestimated.
In this study, both mitochondrial and nuclear sequence data were used to extend knowledge of South American diversity in Cyprinodon. Specifically, these were used to test for the presence of additional lineages of Cyprinodon on the South American coastline and to explore their position within the phylogeny of the genus. Furthermore, the monophyly of C. dearborni was tested and biogeographic scenarios revised for the origins of South American populations of Cyprinodon.
Cyprinodon artifrons was sampled from Carrie Bow Cay, Belize (16° 50′ N; 88° 05′ W). Cyprinodon dearborni was sampled from Laguna de Restinga on Isla de Margarita in eastern Venezuela and from Bonaire (12° 10′ N; 68° 15′ W). Samples of C. variegatus from two nominal subspecies (C. v. ovinus and C. v. variegatus) were collected at four locations [Tuckerton, NJ (39° 36′ N; 74° 19′ W); Georgetown, SC (33° 17′ N; 79° 14′ W); Sapelo Island, GA (31° 23′ N; 81° 17′ W); Port Fourchon, LA (29° 06′ N; 90° 12′ W)] along the Atlantic and Gulf coasts of the United States (Haney et al., 2007).
A fragment of the mitochondrial NADH dehydrogenase subunit 2 (ND2) locus was amplified from 16 individuals of C. dearborni from Isla de Margarita, one individual of C. dearborni from Bonaire and 18 C. artifrons, using primers L4633 and H5334 from Miya & Nishida (1999). A fragment of the mitochondrial control region was amplified from these individuals using primers A and B from Lee et al. (1995). Mitochondrial amplicons were sequenced in the forward direction. Composite mitochondrial haplotypes were constructed for each individual. Composite haplotypes from C. variegatus and other species of Cyprinodon, including a single mitochondrial haplotype from the Bonaire sample C. dearborni, were derived from previous studies (Echelle et al., 2005, 2006; Haney et al., 2007). A fragment of the recombination activating gene 1 (RAG1) locus was amplified using the primers RAGB and RAGCpup (Carson & Dowling, 2006) from 10 individuals of C. dearborni from Isla de Margarita, two individuals of C. dearborni from Bonaire, 11 of C. artifrons and 38 individuals from four populations of C. variegatus (two from each subspecies: C. v. ovinus and C. v. variegatus). RAG1 was sequenced in both directions. Only high quality reads (phred score of 30 or above) as defined by default settings in Sequencher 4·5 (GeneCodes Corporation, Ann Arbor, MI, U.S.A.) were used, and were identified as heterozygous when multiple peaks were apparent in both directions, with secondary peaks at least 60% of primary. Most heterozygous individuals were only so at a single site, making determination of the phase of the two alleles present unambiguous. For two multiple heterozygotes, PHASE 2·1·1 (Stephens et al., 2001) was used to resolve the phase of each allele. This programme implements a Markovchain Monte-Carlo method to estimate the phase of haplotypes in the sample from unphased genotypic data. Homozygous individuals were identified as ‘known phase’ to improve resolution.
Recombination in the nuclear sequence data was tested for by estimating the minimum number of recombination events using the four-gamete test of Hudson & Kaplan (1985) in DnaSP 4·0 (Rozas & Rozas, 1999).
Best-fit models of nucleotide substitution for sequence data were determined using Modeltest 3·5 (Posada & Crandall, 1998) and the Akaike information criterion (AIC). Neighbor-joining (NJ) trees were assembled in MEGA4 (Tamura et al., 2007), maximum-likelihood (ML) phylogenies were constructed using PhyML 2·4·4 (Guindon & Gascuel, 2003) and Bayesian analysis was performed using MrBayes 3·1 (Ronquist & Huelsenbeck, 2003). Nodal support was estimated with 5000 bootstrap pseudoreplicates for the NJ phylogeny, with 1000 bootstrap pseudoreplicates for the ML tree and via posterior probability values in the Bayesian analysis.
Phylogenetic reconstruction was performed with mitochondrial data obtained for this study together with a subset of 24 two-loci haplotypes from previous studies representing all known major clades of Cyprinodon (Echelle et al., 2005). Analysis with nuclear sequences used all distinct alleles identified in this study, in addition to RAG1 sequences from the species Cyprinodon bifasciatus Miller and Cyprinodon atrorus Miller from a previous study (Carson & Dowling, 2006).
The significance of the difference in likelihood between the ML and C. dearborni monophyly constraint trees was assessed with the Shimodaira–Hasegawa (SH) test (Shimodaira & Hasegawa, 1999) implemented in PAUP* 4·04b10 (Swofford, 1998).
The mitochondrial alignment was 1013 base pairs (bp) and consisted of sequence from two loci (control region: 353 or 354 bp; ND2: 651 bp) that defined 51 distinct composite haplotypes from 51 individuals of Cyprinodon. Thirteen distinct control region haplotypes and 10 distinct ND2 haplotypes from C. dearborni and C. artifrons were newly obtained and were deposited in Genbank under accession numbers GQ180997-GQ181008 for the control region and GQ181009-GQ181018 for ND2.
This dataset had 329 variable and 252 parsimony-informative sites. The mtDNA tree indicates two distinct lineages occurring within C. dearborni, hereafter referred to as lineage 1 and lineage 2. Lineage 1 contains sequences from both Bonaire individuals and receives strong support from both NJ and ML bootstrap values and from Bayesian posterior probability (Fig. 1). This distinct lineage clearly falls within the strongly supported maritime clade, together with Atlantic and Gulf coast populations of the wide-ranging C. variegatus and several endemic species of the West Indies (Echelle et al., 2005). The net Tamura–Nei gamma-corrected distance between lineage 1 and C. variegatus (not including sequences of C. v. ovinus) is 2·4%. A second strongly supported clade (100% NJ bootstrap, 100% ML bootstrap and 1·00 posterior probability), however, is found within C. dearborni and includes all haplotypes sampled from Isla de Margarita. This lineage (lineage 2) clearly falls outside the maritime clade. The net mean distance between the two clades of C. dearborni under a Tamura–Nei nucleotide substitution model with rate variation among sites was 10·21%. A deeper clade containing Lineage 2, along with the maritime and Great Plains clades (2A and 2B) of Echelle et al. (2005), is strongly supported by all three phylogenetic methods.
The fit of the recovered ML topology was compared to a tree with C. dearborni constrained to be monophyletic. The result was a significantly lower likelihood for the constraint tree and a rejection of C. dearborni monophyly (SH-test, P < 0·001).
Considering the RAG1 nuclear locus, 294 bp of sequence from 61 individuals yielded seven distinct alleles of the 122 total sampled. All distinct nuclear alleles obtained for this study were deposited in Genbank under accession numbers GQ180990-GQ180996. No recombination is inferred in the nuclear sequence data, as the estimate of the minimum number of recombination events is zero. There were four alleles identified in C. variegatus, two in C. artifrons and three in C. dearborni. One of the three alleles found in C. dearborni was identical to a common allele in C. variegatus. This allele, however, was only sampled in two individuals at the Bonaire site, in individuals with maritime clade mitochondrial DNA. Similarly, two different alleles were sampled from C. artifrons, but one was identical to a second common allele in C. variegatus. Although Lineage 1 of C. dearborni appeared fixed for one allele that was common in all sampled populations of C. variegatus, both alleles found in 10 individuals of Lineage 2 had a fixed nucleotide difference from all C. variegatus alleles.
In the alignment of the seven distinct alleles, there were six variable and two parsimony-informative sites. When three alleles from C. bifasciatus and C. atrorus from a previous study (Carson & Dowling, 2006) were aligned, there were 11 variable and four parsimony-informative sites in the alignment.
Three nodes receive marginal to solid support in phylogenetic analysis of the nuclear RAG1 locus (Fig. 2). The node joining the two alleles from C. dearborni lineage 2 is supported by a bootstrap value of 67% from NJ bootstrap analysis, 67% from ML bootstrap and a posterior probability of 0·99.
The monophyly of C. dearborni, as currently described, is clearly rejected by molecular data. First, two divergent mitochondrial lineages occur within this species. One of these lineages falls within the maritime clade of Echelle et al. (2005) and is closely related to C. variegatus. A second, previously unrecognized lineage, however, also occurs within C. dearborni and falls outside the maritime clade, occurring as a basal branch within clade 2 of Echelle et al. (2005). Second, sequence data from the nuclear RAG1 locus also support a distinction between lineage 1 and lineage 2 of C. dearborni. The molecular evidence, from independent loci, suggests long-term isolation of the two lineages within C. dearborni and indicates that the South American lineage identified in this study may represent a previously unrecognized species distinct from the previously recognized lineage of C. dearborni and all other taxa that comprise the maritime clade of Cyprinodon. Further data from other sources, however, are necessary to confirm the status of this newly recognized lineage. Interestingly, an earlier allozyme study (Alfonsi et al., 2003) identified two genetically distinct populations from two sites in eastern Venezuela, which also showed morphological differentiation. It is tempting to speculate that these populations might represent the same lineages recognized from the sequence data presented here, but a lack of overlap of either molecular markers or sampling localities precludes firm conclusions. This newly identified lineage is also clearly divergent from C. artifrons, whose distribution is closest geographically to that of C. dearborni. Although the phylogenetic relationships within this genus have been investigated by molecular methods in previous studies (Echelle et al., 2005; 2006; Haney et al., 2007), this result suggests that further diversity may remain to be discovered, particularly in tropical regions. It also highlights the need for taxonomic revision, as the current taxonomy within the genus Cyprinodon in many cases, particularly within the maritime clade, does not appear to reflect evolutionary history, as pointed out by Echelle et al. (2006).
Resolution of the zoogeographic and population-level relationships of the two lineages within nominal Cyprinodon dearborni must await more extensive sampling, but it seems clear that there were at least two successful colonizations of coastal South America by ancestral cyprinodontids, and that one of these occurred much earlier than the other. Divergence of the maritime and Great Plains clades (2A and 2B; see Fig. 1) within clade 2 occurred between three and six million years ago (Echelle et al., 2005). The position of lineage 2 of C. dearborni within the phylogeny suggests that it diverged from the other lineages within clade 2 on a similar time frame. The more recent colonization of South America by a maritime clade lineage apparently occurred during Pleistocene diversification within this clade (Echelle et al., 2006). These colonization events have contributed to the extensive diversity occurring within Cyprinodon.
Acknowledgments
We thank J. Scanlan and M. Nirchio for specimens of C. dearborni from Bonaire and the Isla de Margarita, respectively, and B. Silliman for specimens of C. variegatus. This work was supported by NOAA-NERRS and Rhode Island EPSCoR fellowships to R.A.H. and NSF (DEB 0108500 and 0343464) to D.M.R.
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