 Methodology article
 Open Access
 Published:
Testing comparative phylogeographic models of marine vicariance and dispersal using a hierarchical Bayesian approach
BMC Evolutionary Biologyvolume 8, Article number: 322 (2008)
Abstract
Background
Marine allopatric speciation is an enigma because pelagic larval dispersal can potentially connect disjunct populations thereby preventing reproductive and morphological divergence. Here we present a new hierarchical approximate Bayesian computation model (HABC) that tests two hypotheses of marine allopatric speciation: 1.) "soft vicariance", where a speciation involves fragmentation of a large widespread ancestral species range that was previously connected by long distance gene flow; and 2.) peripatric colonization, where speciations in peripheral archipelagos emerge from sweepstakes colonizations from central source regions. The HABC approach analyzes all the phylogeographic datasets at once in order to make across taxonpair inferences about biogeographic processes while explicitly allowing for uncertainty in the demographic differences within each taxonpair. Our method uses comparative phylogeographic data that consists of single locus mtDNA sequences from multiple codistributed taxa containing pairs of central and peripheral populations. We use the method on two comparative phylogeographic data sets consisting of cowrie gastropod endemics codistributed in the Hawaiian (11 taxonpairs) and Marquesan archipelagos (7 taxonpairs).
Results
Given the Marquesan data, we find strong evidence of simultaneous colonization across all seven cowrie gastropod endemics codistributed in the Marquesas. In contrast, the lower sample sizes in the Hawaiian data lead to greater uncertainty associated with the Hawaiian estimates. Although, the hyperparameter estimates point to soft vicariance in a subset of the 11 Hawaiian taxonpairs, the hyperprior and hyperposterior are too similar to make a definitive conclusion. Both results are not inconsistent with what is known about the geologic history of the archipelagos. Simulations verify that our method can successfully distinguish these two histories across a wide range of conditions given sufficient sampling.
Conclusion
Although soft vicariance and colonization are likely to produce similar genetic patterns when a single taxonpair is used, our hierarchical Bayesian model can potentially detect if either history is a dominant process across codistributed taxonpairs. As comparative phylogeographic datasets grow to include > 100 codistributed taxonpairs, the HABC approach will be well suited to dissect temporal patterns in community assembly and evolution, thereby providing a bridge linking comparative phylogeography with community ecology.
Background
Allopatric speciation is an enigma in many marine organisms because larval dispersal can potentially connect disjoint populations and thereby prevent the reproductive and morphological divergence that arises from prolonged isolation [1–7]. This is especially enigmatic in the IndoPacific region where many species range freely across this expanse without evidence for barriers to genetic exchange. This marine region harbors the planet's highest species diversity and endemism of marine fauna, and with the absence of explicit barriers, some have pushed controversial models of sympatric speciation to explain this elevated diversity [8, 9]. Even the proposed competing models of geographic speciation in the IndoPacific remain contentious and generally involve different facets of the classic dispersal or vicariance models for speciation. Under the one model (the "soft vicariance" model), speciations in peripheral archipelagoes result from a large widespread patchy ancestral species range connected by long distance gene flow that is eventually interrupted by oceanographic changes in temperature, sea level and/or currents [10–12] which leads to peripheral isolation and endemism. Under a second model (the "colonization" model), speciations in peripheral (i.e peripatric) archipelagoes emerge from sweepstakes centrifugal colonizations from highdiversity central areas followed by prolonged periods of isolation with potential inward range shifts towards the central region [8, 9, 13, 14]. As in the case of terrestrial systems, using genetic data to distinguish these two scenarios is difficult because their expected genetic signatures are often similar, a situation that is exacerbated if demographic changes such as expansions and bottlenecks occur after an isolating event [10, 15–17].
Likewise, discerning the modes of isolation and speciation using phylogenetic and phylogeographic data is often fraught with uncertainty because species can potentially shift their ranges [18] or loose the population genetic patterns associated with colonization >> 2N generations subsequent to isolation. Traditionally, vicariance and dispersal histories have been tested using phylogenetic approaches that use area cladograms [19, 20], consensus methods [21], or parsimony [22] in combination with some method of ancestral character state reconstruction. Although many of these classic methods were biased to find vicariance, recent methods incorporate more complex biogeography histories [23, 24] such as maximum likelihood [25, 26] and Bayesian methods that use both distributional and phylogenetic data [27]. Likewise, empirical studies have increasingly found dispersal/colonization to be a more common force behind allopatric speciation [15, 16, 28–31]. Regardless, such analyses are often circular or ambiguous [32], and ancestral character reconstruction methods are always going to be hindered when elevated homoplasy in biogeographic patterns obscures the inferences in the older parts of a phylogeny [18, 31, 33].
Here we present an entirely different approach to testing for vicariance and dispersal histories. Instead of using phylogenetic comparative methods, we use coalescent population genetics to estimate ancestral demographic patterns across codistributed taxa within a community. While this is in the spirit of previous suggested approaches that blend systematics and population genetics [34], the hierarchical Bayesian approach presented here tests vicariance and dispersal across taxonpairs instead of doing so one at a time. Specifically we extend a hierarchical approximate Bayesian model (HABC) [35, 36] in order to quantify the strength of these two alternative models of allopatric isolation across marine endemic taxa that are codistributed in peripheral archipelagoes.
Using HABC allows sidestepping the requirement of an explicit likelihood function. Instead, it uses a probabilistic simulation model to generate data sets to compare with the empirical data. By using summary statistics, one can easily compare the simulated and empirical data in order to estimate parameters of the simulation model via an approximate sample of the posterior distribution. In HABC we use hyperparameters that describe processes across codistributed taxonpairs as well as subparameters that describe the demographic history of each taxonpair.
First we describe the population genetic models whose hyperparameters we want to estimate, and then we describe HABC. After detailing the HABC model, the summary statistics and the HABC implementation, we test these two biogeographic hypotheses given two comparative phylogeographic datasets: mtDNA CO1 data collected from multiple cowrie gastropod species that are endemic to the Hawaiian and Marquesan archipelagos. Specifically we use HABC to test whether marine vicariance ("soft vicariance") (H_{ 1 }) or colonization (H_{ 2 }) is the dominant isolating mechanism in either of these two marine communities. After using HABC to choose the best model of community isolation, we then use HABC to estimate temporal congruence in soft vicariance and/or colonization. We specifically use mtDNA sequence data collected from each codistributed peripheral endemic taxon as well as each of the respective sister species which are usually more geographically widespread (Additional file 1).
Although this method specifically addresses questions relevant to the species diversity and patterns of endemism in the IndoPacific, it will be broadly applicable to many comparative phylogeographic datasets and biogeographic settings.
Methods description
Soft vicariance and colonization
Rather than classical terrestrial vicariance where a large ancestral population is broken up into two isolated sister populations (Figure 1A), our "soft vicariance" scenario (H_{1}; Figure 1B) has two ancestral populations with effective sizes (θ_{ τ })_{1} and (θ_{ τ })_{2} that are connected by high to moderate gene flow (M_{ 1 }= 1.0 to 100.0 migrants per generation) until τ_{ V }, when M_{ 1 }decreases to 0.0 – 1.0 migrants per generation (M_{ 2 }). If this second period is prolonged, then effective isolation and divergence can occur [37]. At τ_{ V }, the sizes of the two sister populations ((θ_{ τ })_{1} and (θ_{ τ })_{2}) remain the same size or begin to grow exponentially until they reach their present sizes (θ_{ 1 }and θ_{ 2 }) at τ = 0 depending on the draw from the prior (Figure 1B). As in [16, 17], time of vicariance, population sizes and migration rates are all free to vary across taxonpairs according to their prior distributions.
Under the colonization scenario (H_{ 2 }; Figure 1C), one of the sister populations is founded by a very small number of individuals (θ_{ τ })_{2} that come from a larger source population (θ_{ τ })_{1} at the time of colonization, τ_{ C }with subsequent isolation. The small colonizing population (θ_{ τ })_{2}, then grows exponentially until it reaches its present effective size of θ_{2} at τ = 0. The primary parametric expectation that distinguishes marine vicariance (H_{ 1 }) from colonization (H_{ 2 }) is the relatively small effective population size of the colonized population ((θ_{ τ })_{2}) at the putative time of colonization (τ_{ C }). Secondarily, the possibility of gene flow subsequent to the vicariance event τ_{ V }further distinguishes H_{ 1 }and H_{ 2 }, although this assumption can potentially be relaxed. With regards to different patterns in the molecular genetic data under H_{ 1 }and H_{ 2 }, under colonization (H_{ 2 }) samples from peripheral populations will likely accumulate a surplus of rare alleles due to having a current effective population size that greatly expanded from a small size after the colonization time τ_{ C }. In addition, there is likely to be generally more genetic diversity under soft vicariance (H_{ 1 }) due to there being two ancestral populations rather than just one.
To statistically quantify the relative support of these two hypotheses (H_{ 1 }and H_{ 2 }) across Y codistributed peripheral endemics and their sister taxa given DNA sequence data, we extend and modify the hierarchical approximate Bayesian computation (HABC) framework of [35, 36]. We also use this framework to estimate the temporal congruence of both vicariance and colonization across the Y phylogeographic data sets.
Although one could independently estimate (θ_{ τ })_{2} in each of the Y data sets and use all of the independent posterior densities of (θ_{ τ })_{2} to measure the support of H_{ 1 }and H_{ 2 }across the Y pairs, implementation of a hierarchical model accomplishes this from a single analysis and uses more information from the data via "borrowing strength" [38–40].
Hierarchical approximate Bayesian computation
Our implementation of HABC is based on the framework presented in [35, 36, 41], and we review the important features here. In HABC, subparameters (Φ; within taxonpair parameters) are conditional on "hyperparameters" (φ) that quantify the variability of Φ among the Y taxonpairs. Instead of explicitly calculating the likelihood expression P(Dataφ, Φ) to get a posterior distribution, we sample from the posterior distribution P((φ, Φ)Data) by simulating the data K times under a coalescent model using candidate parameters randomly drawn from the joint hyperprior and subprior distribution P(φ, Φ). A summary statistic vector D_{ i }for each simulated dataset is then compared to the observed summary statistic vector D* in order to generate random observations from the joint posterior distribution f(φ_{ i }, Φ_{ i }D_{ i }) by way of a rejection/acceptance algorithm followed by a weighted local linear regression step [42].
The rejection/acceptance algorithm involves calculating a summary statistic vector from the observed data and each of the K simulated data sets. Each simulated data set is generated using parameters that are randomly drawn from the joint prior. Following [35, 42], K Euclidian distances between the normalized observed summary statistic vector D* and each of the K normalized summary statistic vectors are then calculated (D_{ i } D* = d). An arbitrary proportion (tolerance) of the K simulations with the lowest d values are then used to obtain an approximate sample from the joint posterior after weighting and transforming the accepted parameter values using local linear regression [35, 42]. After the local linear regression step, accepted and transformed parameter values that fall outside their respective prior bounds are subsequently transformed to have the values of their respective prior boundaries. For example, if an accepted parameter value with a uniform prior of [0.0,1.0] is transformed by local linear regression to a negative number, it is subsequently transformed to 0.0.
Hierarchical Model of Community Colonization and Vicariance
Model hyperparameters and subparameters are listed and described in Additional file 2. Three hyperparameters are drawn from their respective hyperprior distributions (Additional file 2A), and these include: 1.) Z, the number of descendent populations per Y taxonpairs that arise by colonization at times ${T}_{C}=\{{\tau}_{C}^{1},\mathrm{...},{\tau}_{C}^{Z}\}$; 2.) the number of different vicariance times ${\overline{\Psi}}_{V}=\{{t}_{V}^{1},\mathrm{...},{t}_{V}^{{\Psi}_{V}}\}$ across (YZ) actual vicariance times ${T}_{V}=\{{\tau}_{V}^{1},\mathrm{...},{\tau}_{V}^{(YZ)}\}$ and 3.) Ψ_{ C }, the number of different colonization times ${\overline{\Psi}}_{C}=\{{t}_{C}^{1},\mathrm{...},{t}_{C}^{{\Psi}_{C}}\}$ across Z actual colonization times ${T}_{C}=\{{\tau}_{C}^{1},\mathrm{...},{\tau}_{C}^{Z}\}$.
The Z colonized populations (H_{ 2 }) and remaining (YZ) populationpairs that arise via vicariance (H_{ 1 }) then draw their population mutation subparameters ($\stackrel{\rightharpoonup}{\theta}$ = {θ^{1},..., θ^{Y}}, ${\stackrel{\rightharpoonup}{\theta}}_{1}=\{{\theta}_{1}^{1},\mathrm{...},{\theta}_{1}^{Y}\}$, and ${\stackrel{\rightharpoonup}{\theta}}_{2}=\{{\theta}_{2}^{1},\mathrm{...},{\theta}_{2}^{Y}\}$) from their respective subpriors (Additional file 2C). Each taxonpair's population mutation parameter θ^{i}is equal to the sum of ${\theta}_{1}^{i}$ and ${\theta}_{2}^{i}$, the population mutation parameters of the descendent taxonpairs at τ = 0 (present time). In this case θ = 2Nμ (2N is the sum of the two haploid effective female population sizes of each pair of descendent populations and μ is the per gene per generation mutation rate).
Subsequently, each of the Y taxonpairs draw their remaining subparameters from two different sets of subpriors (Additional file 2D) that differentially characterize the two different histories (H_{ 1 }and H_{ 2 }). Importantly, the uniform subprior for (θ_{ τ })_{2} is [0.0, 0.05] for each of the Z speciespairs that arose via colonization (H_{ 2 }), but (θ_{ τ })_{2} is drawn from the uniform subprior [0.0, 1.0] for each of the other (Y  Z) taxonpairs that arose through vicariance (H_{ 1 }). Additionally, two sets of migration subparameters (${\stackrel{\rightharpoonup}{M}}_{1}=\{{M}_{1}^{1},\mathrm{...},{M}_{1}^{(YZ)}\}$ and ${\stackrel{\rightharpoonup}{M}}_{2}=\{{M}_{2}^{1},\mathrm{...},{M}_{2}^{(YZ)}\}$) are drawn from their respective subpriors for the (Y  Z) taxonpairs that arose through vicariance (H_{ 1 }), whereas there is no migration under the colonization model (Figure 1C; Additional file 2D). In both vicariance and colonization models, the relative effective size of the ancestral central populations (${({\stackrel{\rightharpoonup}{\theta}}_{\tau})}_{1}=\{{({\theta}_{\tau})}_{1}^{1},\mathrm{...},{({\theta}_{\tau})}_{1}^{(YZ)}\}$ and ${({\stackrel{\rightharpoonup}{\theta}}_{\tau})}_{1}=\{{({\theta}_{\tau})}_{1}^{1},\mathrm{...},{({\theta}_{\tau})}_{1}^{Z}\}$) are also drawn from their respective subpriors [0.5, 1.0]. If (Y  Z) ≥ 1, the Ψ_{ V }different vicariance times (${\stackrel{\rightharpoonup}{\Psi}}_{V}=\{{t}_{V}^{1},\mathrm{...},{t}_{V}^{{\Psi}_{V}}\}$) are drawn from the uniform prior [0.0, 5.0]. Likewise, if Z ≥ 1, the Ψ_{ C }different colonization times (${\overline{\Psi}}_{C}=\{{t}_{C}^{1},\mathrm{...},{t}_{C}^{{\Psi}_{C}}\}$) are drawn from the uniform prior [0.0, 5.0]. After the ${\stackrel{\rightharpoonup}{\Psi}}_{V}$different viciarance times are drawn, they are randomly assigned to the (Y  Z) taxonpairs that arose through vicariance, such that the (Y  Z) actual vicariance times are ${T}_{V}=\{{\tau}_{V}^{1},\mathrm{...},{\tau}_{V}^{(YZ)}\}$. Specifically, the Ψ_{ V }different vicariance times (${t}_{V}^{1},\mathrm{...},{t}_{V}^{{\Psi}_{V}}$) are sequentially assigned to the first Ψ_{ V }actual times ${\tau}_{V}^{1},\mathrm{...},{\tau}_{V}^{{\Psi}_{V}}$. The remaining actual times (${\tau}_{V}^{({\Psi}_{V}+1)},\mathrm{...},{\tau}_{V}^{(YZ)}$) are assigned by randomly drawing with replacement from the ${\stackrel{\rightharpoonup}{\Psi}}_{V}$ matrix of different times {${t}_{V}^{1},\mathrm{...},{t}_{V}^{{\Psi}_{V}}$}. Likewise, the actual colonization times (${T}_{C}=\{{\tau}_{C}^{1},\mathrm{...},{\tau}_{C}^{Z}\}$) are drawn using the same method (Additional file 2D). Both sets of actual vicariance and actual colonization times (T_{ V }and T_{ C }) are in units of θ^{i}/μ generations, where θ^{i}is each taxonpair's population mutation parameter and μ is the per gene per generation mutation rate.
In addition to hyperparameter estimation, we also use the HABC algorithm to sample from the posterior distributions of subparameter summaries (Additional file 2E) in order to quantify the support for H_{ 1 }and H_{ 2 }and secondarily estimate levels of temporal congruence in colonization and/or soft vicariance. Namely, we obtain estimates of the arithmetic means of three subparameters (E((θ_{ τ })2), E(τ_{ C }), E(τ_{ V })), as well as the dispersion indexes of τ_{ C }and τ_{ V }(Ω_{ C }and Ω_{ V }respectively). The subparameter summary E((θ_{ τ })_{2}) is expected to be < 0.05 if H_{2} is dominate across the Y taxonpairs (Z = Y). The dispersion indexes Ω_{ C }and Ω_{ V }of the Z colonization times (${\tau}_{C}^{1},\mathrm{...},{\tau}_{V}^{Z}$) and the (Y  Z) vicariance times (${\tau}_{V}^{1},\mathrm{...},{\tau}_{V}^{(YZ)}$) measure the ratio of the variance to the mean of these two sets of times and are therefore expected to be ≈ 0.0 when if there is temporal congruence in colonization or soft vicariance.
Two Stage Model Implementation
We implement the hierarchical analysis in two stages. In stage 1, an unconstrained general model is used to quantify the support for H_{ 1 }and H_{ 2 }across the Y taxon pairs. This first stage is accomplished by simulating K random draws from a general hyperprior and using the HABC algorithm to sample from the posteriors of? Z and E((θ_{ τ })_{2}). Under our hierarchical model, H_{ 1 }and H_{ 2 }are equally probable because Z is a hyperparameter drawn from the discrete uniform hyperprior distribution [0, Y].
In the stage 2 analysis, K random draws are taken from a constrained hyperprior where Z is fixed to be the mode of its posterior distribution obtained in stage 1. There are equal numbers of hyperprior draws (K) obtained in both stages. The stage 2 analysis allows obtaining posterior samples of hyperparameters and subparameter summaries (Additional file 2B &2E) that quantify and summarize the levels of temporal concordance in colonization (${T}_{C}=\{{\tau}_{C}^{1},\mathrm{...},{\tau}_{C}^{Z}\}$) and/or vicariance (${T}_{V}=\{{\tau}_{V}^{1},\mathrm{...},{\tau}_{V}^{(YZ)}\}$). These include: 1.) Ψ_{ C }, the number of different colonization times per Z colonization events; 2.) Ψ_{ V }, the number of different vicariance times per (Y  Z) vicariance events; 3.) Ω_{ C }, the dispersion index of τ_{ C }(the ratio of the variance to the mean in the Z actual colonization times, T_{ C }); and 4.) Ω_{ V }, the dispersion index of τ_{ V }(the ratio of the variance to the mean in (Y  Z) actual vicariance times, T_{ V }).
Summary Statistic Vector for HABC Acceptance/Rejection Algorithm
In order to implement the HABC procedure, we use two modified versions of the summary statistic vector D used in [35]. For the Marquesas summary statistic vector (D_{ Marquesas }), we calculate eight summary statistics collected from each taxonpair (56 total). This includes π_{ b }(average pairwise differences between each central and peripheral Marquasan taxonpair), π (average pairwise differences among all individuals within each taxonpair), π_{ w }(average pairwise differences within descendent populations of each taxonpair), θ_{ W }(Watterson's estimator of θ of each taxonpair), and Var(π  θ_{ W }). For π, θ_{ W }and Var(π  θ_{ W }), each of the Y taxonpairs are treated as a single population sample (${\stackrel{\rightharpoonup}{n}}_{1}+{\stackrel{\rightharpoonup}{n}}_{2}$). The Marquesas summary statistic vector, D_{ Marquesas }also includes calculating π, θ_{ W }, and Var(π  θ_{ W }) in each of the Y peripheral Marquasan samples (${\stackrel{\rightharpoonup}{n}}_{2}$) that are putatively colonized and we denote these as π_{2}, (θ_{ W })_{2}, and Var(π  θ_{ W })_{2}. Under this scheme, the vector D_{ Marquesas }is
where each of the Y rows correspond to the Y taxonpairs (Y = 7) and the eight columns correspond to the eight summary statistic classes. After these 8 × Y summary statistics are calculated, we must choose a way to consistently order the Y rows within D_{ Marquesas }. Instead of consistently ordering the rows by each taxonpair's sample size, we increase the efficiency of our HABC estimator by ordering the rows based on the taxonpair's Tajima's D [43] calculated from the taxonpair's peripheral population sample (${\stackrel{\rightharpoonup}{n}}_{2}$). For example, row 1 would contain the eight summary statistics collected from the taxonpair with the lowest Tajima's D, and the Y^{th}row would contain the eight summary statistics collected from the taxonpair with the highest Tajima's D.
The motive for this ordering procedure is to extract more information from the data with respect to the estimated hyperparameters than would be accomplished by ordering consistently by sample size [35]. For an efficient HABC estimator, there should be a strong correlation between pairwise differences in hyperparameter values (i.e. E(θ_{ τ })_{2} or Z) and Euclidian distances between corresponding pairs of summary statistic vectors from corresponding pairs of simulated data sets. If ordering by sample size rather than ranked values of an informative summary statistic, pairwise values of Z or E(θ_{ τ })_{2} are not predicted to correlate with Euclidian distances of D calculated from corresponding pairwise simulated data sets. This is because sample size has no bearing on how each of the Y taxonpairs are assigned to histories H_{ 1 }and H_{ 2 }when drawing values of Z from the hyperprior. On the other hand, ordering by an informative summary statistic will minimize Euclidian distances among data sets with equal or similar values of Z regardless of which of the Y taxon pairs were assigned histories H_{ 1 }and H_{ 2 }. The consequent improved accuracy in HABC estimation that results from this ordering procedure is based on the exchangeability of the Y rows within D_{ Marquesa }(D_{1},...,D_{ Y }). If Φ_{ i }and D_{ i }are invariant to the permutations of the indexes (1 ,..., Y) and the i^{th}taxonpair's sample size is unrelated to the expectation of its Φ_{ i }or D_{ i }, there is exchangeability in the model [44]. We order by the peripheral Tajima's D because it is a summary statistic that is predicted to be informative with respect to demographic parameter differences between histories H_{ 1 }and H_{ 2 }(i.e. the ratio of each taxonpair's (θ_{ τ })_{2} and θ_{2}).
For the analysis of the 11 Hawaiian taxonpairs, we use a reduced summary statistic vector D_{ Hawaii }to avoid null values that would arise in population samples that only included one individual (Additional file 1B). The vector D_{ Hawaii }in this case is
and the rows were likewise sorted by Tajima's D calculated from the peripheral populations.
Application on real data sets
Two Comparative Phylogeographic Implementations
We use this HABC method on two comparative phylogeographic data sets of Pacific cowrie gastropods (Cypraeidae). The first dataset consists of seven sister taxonpairs of cowries that each consist of a descendent endemic species or subspecies that is distributed within the peripherally located Marquesas archipelago as well each sister taxon that is more geographically widespread (Additional file 1A). The second dataset consists of eleven sister taxonpairs of cowries codistributed within the peripherally located Hawaiian archipelago. Like in the former data set, each pair consists of a Hawaiian endemic and a more widespread sister (Additional file 1B). Both data sets consisted of 614 base pairs of the CO1 mtDNA locus collected from 2–93 individuals per taxonpair (Additional file 1). The HABC procedure was implemented using a modified version of the MSBAYES comparative phylogeographic software pipeline [35, 36] consisting of several C and R programs that are run with a Perl "frontend" and utilizes a finite sites version of Hudson's classic coalescent simulator [45]. For both analyses, 2,000,000 random draws were sampled from the hyperprior and 1,000 – 2,000 accepted draws were used to construct hyperposterior samples (tolerance of 0.0005 and 0.001 respectively) using the HABC acceptance/rejection algorithm.
The prior bounds for hyperparameters and subparameters are given in Additional file 2. To explore the sensitivity of using different prior assumptions, we used two different upper bounds of θ (θ_{ MAX }= 25.0 and 50.0 for the Marquesas data; θ_{ MAX }= 50.0 and 100.0 for the Hawaiian data). These values correspond to 2× to 4× the range of within species θ estimates, where the average number of pairwise differences was used as an estimator of each species specific θ [46]. To further explore how sensitive results are to model assumptions, we alternatively ran the stage 1 analysis with the postcolonization migration prior allowed to be [0.0, 1.0] instead of zero under the colonization model (H_{ 2 }), as well as allowing postisolation migration (M_{2}) to be zero under the soft vicariance model (H_{ 1 }).
We calculate Bayes factors to compare the relative hyperposterior support of either history (soft vicariance and colonization) being dominate across all Y taxon pairs (e.g Z = 0 or Z = Y) against all other scenarios including mixed scenarios. We accomplish this by comparing relative hyperposterior support of these two scenarios while accounting for the relative hyperprior support for these two scenarios [47]. To calculate this Bayes factor, we use an arbitrary partition of hyperparameter space to delineate where H_{ 1 }or H_{ 2 }is dominate across all Y taxonpairs. For example, to evaluate the evidence of colonization being dominate across all Y taxon pairs (Z = Y) against all other scenarios (Z <Y), the approximate Bayes factor B(Z = Y, Z <Y) is the ratio of the two approximate hyperposteriors of these two scenarios divided by the ratio of the two hyperpriors of these two scenarios,
B(Z = Y, Z <Y) = (P(Z = YD = D*)/P(Z <YD = D*))/(P(Z = Y)/P(Z <Y))
Alternately, we examine these two scenarios by using an arbitrary partition of E((θ_{ τ })_{2}) such that E((θ_{ τ })_{2}) = 0.05 represents a scenario where colonization is dominant across all Y taxon pairs, and E((θ_{ τ })_{2}) > 0.05 represents all other scenarios. In this case, the approximate Bayes factor is
Evaluating the evidence of soft vicariance being dominant across all Y taxonpairs (Z = 0) against all other scenarios (Z > 0) is identically accomplished by calculating the two corresponding Bayes factors B(Z = 0, Z > 0) and B(E((θ_{ τ })_{2}) > 0.05, E((θ_{ τ })_{2}) ≤ 0.05). To calculate each Bayes factor, we use the accepted hyperparameter values from the hyperposterior sample and the random draws from the hyperprior.
Marquesas Results
The HABC analysis yielded a hyperposterior that strongly supports H_{ 2 }, where colonization histories (Figures 2A &2B) are inferred across all seven Marquesan endemics. Irrespective of tolerance (0.0005 or 0.001), prior assumptions on the upper bound of θ, (θ_{ MAX }), the hyperparameter mode estimates of Z and E((θ_{ τ })_{2}) were 7.00 and 0.00 – 0.07 respectively (Figures 2A &2B; Additional file 3A &3B). Furthermore, when using the raw untransformed accepted values to obtain our posterior sample of Z, a history of community colonization is also inferred (mode estimate of Z is 7.0) albeit the 95% credibility intervals were wider. This suggests that the dominant mode of speciation has generally been from colonization by a small number of individuals followed by at least a 20fold demographic expansion to current population levels. Both Bayes factors evaluating the evidence for colonization across all Y = 7 taxonpairs against all other histories (Z < 7) indicate moderate support for the former scenario (B(Z = Y, Z <Y) = 6.23; B(E((θ_{ τ })_{2}) > 0.05, E((θ_{ τ })_{2}) ≤ 0.05) = 6.79).
In stage 2, where we constrained the hyperparameter Z to be 7, the hyperposterior best supported temporal concordance in colonization across all seven Marquesas endemics. In this case, estimates of Ψ_{ C }and Ω_{ C }were 1.00 (95% quantiles: 1.00 – 2.14) and 0.00 (95% quantiles: 0.00 – 0.17) respectively (Additional file 3A; Figure 2). The mean time of colonization E(τ_{ C }) was 1.58 My ago if we assume a 1% divergence rate per My (Figure 2D). The Bayes factor evaluating the evidence for simultaneous colonization (Ω_{ C }< 0.05) against nonsimultaneous colonization (Ω_{ C }= 0.05) yielded strong support for simultaneous colonization (B(Ω_{ C }< 0.05, Ω_{ C }= 0.05) = 36.73). In this case the Bayes factor is calculated from an arbitrary partition of hyperposterior space conditional on Z = 7. In this case the arbitrary threshold of simultaneous colonization is Ω_{ C }< 0.05 such that the Bayes factor is
B(Ω_{ C }< 0.05, Ω_{ C }≥ 0.05) = (P(Ω_{ C }< 0.05D = D*)/P(Ω_{ C }≥ 0.05D = D*))/(P(Ω_{ C }< 0.05)/P(Ω_{ C }≥ 0.05)).
Furthermore, the hyperposterior estimates were not sensitive to assumptions about postisolation migration. Under the stage 1 analysis, estimates of Z and E((θ_{ τ })_{2}) were 6.99 and 0.02 (95% credibility intervals of 3.34 – 7.00 and 0.00 – 0.32) when the postcolonization migration prior was [0.0, 1.0] instead of 0.0 under the colonization model (H_{ 2 }).
Hawaii Results
In contrast to the Marquesas analysis, the hyperposteriors were much more similar to the hyperpriors (Figure 3). The less informative posteriors are consistent with the lower Hawaiian sample sizes (Additional file 1B) and consequence of using of a reduced number of summary statistics (D_{ Hawaii }) for the HABC acceptance/rejection algorithm. Although the hyperposterior of Z given the Hawaiian data suggests a mixed history of both colonization and soft vicariance (Figure 3), larger sample sizes will be required to verify this. This weak inference is demonstrated by Bayes factors giving weak support for vicariance or colonization across all 11 Hawaiian endemics. Specifically, the calculated Bayes factors B(Z = 0, Z > 0), B(Z = 11, Z < 11), B(E((θ_{ τ })_{2}) < 0.05, (E((θ_{ τ })_{2}) = 0.05) < 1.0) and B(E((θ_{ τ })_{2}) = 0.05, E((θ_{ τ })_{2}) < 0.05) < 1.0) where all weak (< 1.0). Although the Hawaiian data yielded weak inference, the credibility intervals for Z ranged from 0.00 to 9.22 (Additional file 3C and 3D), suggesting that the history of isolation likely involved both soft vicariance and colonization. Likewise, estimates of Ω_{ C }and Ω_{ V }did not suggest simultaneous vicariance or colonization, and likewise yielded less informative posteriors than obtained in the Marquesas analysis (Figures 3C &3D). As was the case of the Marquesas analysis, hyperposterior estimates were not sensitive to tolerance, prior assumptions on the upper bound of θ, (Additional file 3C &3D), and prior assumptions of postisolation migration. Under the stage 1 analysis using the alternative model assumptions where postvicariance migration (M_{2}) was 0.0 under the soft vicariance model, estimates of Z and E((θ_{ τ })_{2}) were respectively 3.64 and 0.66 (95% credibility intervals 0.00 – 9.74 and 0.35 – 0.97).
Simulation testing
Simulated Data Sets
One of the chief advantages of HABC and ABC methods is the ease at which one can evaluate the performance, bias, and precision of the estimator via simulations. Specifically, we can simulate pseudoobserved data sets with known hyperparameter values and compare estimates with their true values. Even though the most timeconsuming task is to simulate a large enough prior and/or hyperprior in ABC and HABC, once it is produced for the analysis of the real observed data set, it can subsequently be used to quantify bias and precision on the pseudoobserved data sets.
To this end, we simulate pseudoobserved data sets with known values of Z and E((θ_{ τ })_{2}) under the general model (stage 1), and Ψ_{ C }, Ψ_{ V }, E(τ_{ C }), E(τ_{ V }), Ω_{ C }, and Ω_{ V }under the constrained model (stage 2). We repeat this for both sample sizes used in the empirical implementation (D_{ Marquesas }and D_{ Hawaii }). To simulate a data set (pseudoobserved data), all hyperparameters and subparameters were randomly drawn from the prior and a corresponding D_{ Marquesas }or D_{ Hawaii }was subsequently calculated. For each corresponding pseudoobserved D_{ Marquesas }and D_{ Hawaii }, a hyperposterior sample was obtained from the HABC rejectionsampling algorithm given 2,000,000 random draws from the hyperprior. For every pseudoobserved (simulated) data set, an estimate is obtained from the posterior mode. We report estimates using a tolerance of 0.001 corresponding to 2,000 accepted draws from the hyperprior. For both D_{ Marquesas }and D_{ Hawaii }and stage 1 and two, 250 estimates were made from 250 simulated pseudoobserved datasets.
In addition to these evaluations, we assess the ability to distinguish H_{ 1 }and H_{ 2 }when the true history is a special asymmetrical case of soft vicariance (H_{ 1 }). To this end, we obtain HABC estimates of Z and E((θ_{ τ })_{2}) on 250 pseudoobserved datasets of size D_{ Marquesas }simulated under H_{ 1 }where true values of Z and E((θ_{ τ })_{2}) are 0 and 0.0 – 0.05 respectively. Estimates for Z and E((θ_{ τ })_{2}) were obtained using a general prior (stage 1).
Another factor we explored was three other methods of postacceptance transformation other than local linear regression (LLR) for obtaining a sample of the hyperposterior distribution of the Z hyperparameter. Because Z is a discrete integer (ranging from 0 to Y), it might be most appropriate to preserve Z as a discrete integer when using an ABC regression technique that implements polychotomous logit regression (PLR) [48–50]. We therefore used simulations to compare the effectiveness of LLR with: 1. PLR; 2. using the raw accepted values (RAW); and 3. a cumulative logit regression model (CLR). To compare the estimator bias and precision of these four methods, we calculated the root mean square error (RMSE) from 1000 estimates using each of these four methods on 1000 simulated pseudoobserved data sets with parameters randomly drawn from the priors. The methods for CLR and PLR are implemented in the VGAM package distributed by T. Yee under R http://www.stat.aukland.ac.nz/~yee. The LLR method is implemented from R functions made available by M. Beaumont.
Results of Simulation Testing
Our simulations identified conditions under which the HABC estimator is reliable as well as conditions under which it is less reliable. At stage 1 of the HABC analysis, the estimates of E((θ_{ τ })_{2}) were consistently close to the corresponding true values of E((θ_{ τ })_{2}), although the larger sample sizes matching the Marquesas data set (D_{ Marquesas }) yielded more accurate estimates of E((θ_{ τ })_{2}) than using sample sizes matching the smaller Hawaii data set (D_{ Hawaii }; Figures 4A &4B). On the other hand, estimates of Z were less accurate, yet using D_{ Marquesas }resulted in more accurate estimates of Z than when using D_{ Hawaii }(Figures 4C &4D). Additionally, estimates of Z representing colonization across all Y taxonpairs never resulted in false positives given D_{ Marquesas }(Figure 4C). Specifically, when estimates of Z were 6 or 7, true Z values were always 6 or 7. Conversely, lower true values of Z yielded less accurate estimates of Z (Figures 4C &4D). For example, when estimates of Z were 0, true values ranged from 0 – 4 given D_{ Marquesas }(Figure 4C). In general, the simulation analysis verified the statistical confidence in the empirical inference of colonization across all seven Marquesas endemics, yet demonstrated there to be more uncertainty in the inferred history of the 11 Hawaiian endemics.
Under the constrained stage 2 model, the simulations revealed a strategy for estimating the variability in the Z colonization times. Specifically, the best strategy would be to use estimates of Ω_{ C }rather than Ψ_{ C }(Figure 5). However, there was less accuracy and precision in the Ω_{ C }estimates given D_{ Hawaii }(Figure 5E). Unlike estimates of Ω_{ C }, estimates of Ω_{ V }or E(τ_{ V }) were not as reliable (Figure 5H), perhaps due to the very small amount of migration (0 to 1.0 migrants per generation) after each "soft vicariance" event (τ_{ V }) under H_{ 1 }.
The simulations also revealed that we have the ability to distinguish H_{ 1 }and H_{ 2 }when the true history is a special asymmetrical case of vicariance (H_{ 1 }) where Z = 0 and each (θ_{ τ })_{2} ranges from 0.0 to 0.05 under the D_{ Marquesas }sample size configuration (Figure 6). In this case, 63% of the Z estimates were ≤ 1 (Figure 6A &6B). Likewise, estimates of E((θ_{ τ })_{2}) were a reliable indicator of detecting H_{ 1 }under this special asymmetrical case of vicariance (H_{ 1 }). Even though true values of E((θ_{ τ })_{2}) ranged from 0.0 to 0.05, estimates of E((θ_{ τ })_{2}) in this case were upwardly bias, with 90% of the E((θ_{ τ })_{2}) estimates ranging from 0.21 to 0.48 (Figure 6C). Even though the E((θ_{ τ })_{2}) estimator is upwardly biased given this special case, it is upwardly biased in the direction of correct inference of H_{ 1 }if one uses the criterion of E((θ_{ τ })_{2}) >> 0.05 to distinguish H_{ 1 }from H_{ 2 }. In this case, our empirical estimates of Z and E((θ_{ τ })_{2}) given the Marquesas data were not likely the result of extreme asymmetrical soft vicariance.
The root mean square error (RMSE) from the simulation study also revealed local linear regression (LLR) to outperform the three other methods that all keep the accepted values of Z as discrete integers (LLR RMSE = 1.32; RAW RMSE = 1.90; CLR RMSE = 1.95; MPR RMSE = 2.15). However, we use all four methods for the empirical data sets to check for consistency.
Discussion
Model Assumptions and Robustness
While previous studies have used multilocus population genetic data to reconstruct the demography and geography of speciation [51–55], here we use single locus mtDNA data to look at patterns across multiple codistributed taxa. Although single locus inference can be hazardous in the face of coalescent variance and the possibility of selection, our approach offers the possibility to look at patterns of community assembly when the community consists of many nonmodel organisms where only "barcode" DNA sequence data can be feasibly collected. Not only does our model incorporate the stochasticity of singlelocus coalescent variance across taxa, by combining datasets into a hierarchical Bayesian analysis we gain statistical "borrowing strength" [38]. The "borrowing strength" of HABC is achieved by making inferences across groups (i.e. codistributed taxa) by pooling information across the groups without assuming the groups are from the same population [39, 40]. This allows estimating congruence across groups in subparameters while borrowing strength from the full comparative phylogeographic sample. This "borrowing strength" translates into higher sample size depending on the magnitude of the "pooling factor" which represents the degree to which subparameter estimates (Φ) are pooled together from hyperparameter estimates of φ, rather than estimated independently from each phylogeographic dataset [56].
The possibility of selection at the tightly linked mtDNA genome could bias results of our analytical method [57], especially if balancing selection occurred in the mtDNA genome in ancestral or descendent taxa such that coalescent events were much older than neutral expectations. Likewise, if positive selective sweeps occurred on the mtDNA genome after colonization or vicariance, estimates of Z and E((θ_{ τ })_{2}) could be biased to reflect colonization [58, 59]. However, if positive selection only occurred at the mtDNA genome before colonization or vicariance, then the timing of these isolation events could be better estimated due to reduction of ancestral polymorphism. Furthermore, because selection and demography are ultimately confounding, our method will be less reliable if mitochondrial positive selection is prevalent in the comparative phylogeographic sample. This could be especially troublesome if peripatric speciation by colonization or vicariance involves positive selection at mtDNA genes that allow adaptive divergence in novel peripheral habitats [60–62]. Nonetheless, results from our HABC method can be considered conservative with respect to inferring the geographic and demographic history of isolation across a peripheral community. For example, a strong inference of colonization across an entire data set could result from both strong positive selection and/or small effective colonizing population sizes, but it would be extraordinary if strong positive selection occurred at the mtDNA genome of all Y codistributed taxonpairs.
A strong result of temporal concordance in isolation is also conservative with respect to violations from a uniform molecular clock model. If rate variation occurred across the Y taxa, then we would expect an inference in temporal discordance unless rates were inversely proportional with actual isolation times. Nevertheless, this HABC method will be most useful when applied to codistributed taxonpairs that are closely related. Our empirical application was restricted to cowrie gastropods (Cypraeidae) and the COI loci we used only marginally rejected rate constancy [63].
Although Bayesian methods are less robust if results are heavily dependent on prior bounds, results from the empirical data were not sensitive to our exploration of different prior assumptions. The overall inferences and hyperposterior estimates from the empirical data were not sensitive to model assumptions regarding the priors of θ (Additional file 3) or postisolation migration. Additionally, all four methods of postacceptance transformation (LLR, PLR, CLR and RAW) yielded identical mode estimates of Z given the Marquesas data and similar mode estimates of Z given the Hawaii data (ranging from 4 – 5).
Another consideration is how deviations from a panmictic WrightFisher model could have affected our HABC estimates. Although the sampling scale is large in some of the source species (Additional file 1), the cowrie gastropod taxa we included have high dispersal capabilities and are therefore not likely to have elevated within species subdivision [63]. This is confirmed by the relatively low levels of within species average pairwise differences (π_{1} and π_{2}) in both data sets (Additional file 1). If intraspecies migration rates are > 1, our idealized coalescent model assuming intraspecies panmixia is somewhat appropriate (Slatkin 1985). Even with some population some structure, a standard coalescent model can suffice if a species consists of many small demes with at least moderate migration such that number of demes is approximated by a scaled effective population size [64–67]. If ancestral population structure is approximately scaled by ancestral effective population size, then our chosen priors are conservative because we allow for ancestral population sizes that are two to four times as large as the observed pairwise distances of extant population sizes (π_{1} and π_{2}; Additional file 1). However, our method should not be applied to populations that are heavily structured over large geographic scales.
Vicariance and Dispersal in Marine Communities
Vicariance and dispersal speciation could be hugely relevant in the marine realm, especially within the highly diverse IndoPacific region that is dominated by islands rather than long continuous coastlines. Explanations for elevated IndoPacific diversity in the centrally located "coral triangle" portion of this IndoPacific region (Philippines, Malay Peninsula, and New Guinea) usually revolve around sympatric speciation followed by outward range shifts [68] or peripatric speciation followed by inward range shifts [69, 70]. However, the plausibility of the first hypothesis of sympatric speciation is very controversial on theoretical grounds [71, 72] as well as being very difficult to test empirically [18]. On the other hand, the second hypothesis of peripatric speciation is a much more likely force behind IndoPacific diversification if long distance oceanic dispersal to peripheral populations is sufficiently low for isolation and subsequent reproductive or ecological divergence to emerge between central and peripheral archipelagoes [1–7].
Instead of the classic vicariance model, under our marine vicariance model (or "soft vicariance") an ancestral range is interconnected by long distance gene flow that is interrupted by oceanographic changes in temperature, sea level and/or currents [10–12]. In this case we might predict that codistributed peripheral endemics became isolated simultaneously in taxa with lower dispersal capability. On the other hand, our marine colonization model is more similar to the classic dispersal or peripatric model. Here, allopatric isolation arises via sweepstakes colonization where the timing of colonization could be predicted to occur randomly across the codistributed endemics after an archipelago emerges from geological processes.
Hawaiian vs Marquesas Dynamics
Both Hawaii and the Marquesas have some of the highest levels of endemism in all of Oceania [73–75], but HABC analyses support different histories for their endemic species. The Hawaiian archipelago is the most isolated island chain in the IndoWest Pacific and has existed for > 70 My with coral reefs since at least 35 My [76]. It is now well established that terrestrial endemics can be older than the oldest emergent island in the archipelago, a pattern resulting from initial colonization of older, now subsided islands, followed by dispersal to new islands after emergence [77]. Thus, there has been ample opportunity for isolation and speciation, perhaps even more so for marine taxa. Although the lower sample sizes lead to greater uncertainty associated with the Hawaiian estimates (Figure 3), the hyperparameter 95% credibility intervals suggest a strong inference of isolation via soft vicariance in at least a subset of the Hawaiian taxonpairs (Z = 0.0 – 9.22; E((θ_{ τ })_{2}) = 0.30–0.95). If this is the case, then occupation of the Hawaiian archipelago was much older than the Marquesas archipelago, consistent with geologic evidence. Moreover, the inference of soft vicariance in a number of the taxon pairs suggests that there was greater potential for migrants between this archipelago and the central Pacific and IndoPacific triangle regions during older periods. Such connectivity of the Hawaiian chain to the remaining IndoWest Pacific via Johnston Atoll has been suggested in other studies [78–80].
In contrast, we find strong inference of isolation via colonization across all seven cowrie gastropod endemics codistributed in the Marquesas, as well as a strong inference of temporal concordance in this colonization. Unlike other island chains in the Pacific Ocean that have older seamounts and atolls trending away from most recent island (e.g. Hawaii), the Marquesan hotspot is unusual in being quite young. The ages of Marquesan islands range from 1.3 My (Fatu Hiva) to 6.0 My (Eiao) [81]. If we apply a molecular clock of 1% divergence per My [63], the inferred timing of simultaneous colonization of the Marquesas archipelago is from 0.84 – 1.90 My (Additional file 3A), and is consistent with the young origins of the islands. If we accept our strong inference of temporal concordance, it could be argued that this assemblage of cowries colonized via an episodic oceanographic event that caused a surge in gene flow from the central Pacific region. Given that the Marquesas has one of the highest levels of marine endemism in Oceania [73, 74], it will be interesting to see if HABC analyses on other taxonpairs show similarly young divergences and temporal congruence.
Conclusion
Although soft vicariance and colonization are likely to produce relatively similar genetic patterns when only a single taxonpair is considered, our simulation analysis shows that our hierarchical Bayesian model can potentially detect if either history is a dominant process across a marine community. The empirical implementation of our method yields a strong inference of isolation via simultaneous colonization across all seven cowrie gastropod endemics codistributed in the Marquesas. In contrast, our method shows a strong inference of isolation via soft vicariance in at least a subset of the 11 Hawaiian taxonpairs, although the smaller sample size resulted in less certainty in our estimates.
Our HABC method exemplifies the utility in "statistical phylogeographic" approaches [82, 83] rather then qualitative and descriptive approaches that make large inferences from the small details observed from gene trees [84]. The HABC approach accomplishes this by analyzing all the phylogeographic datasets at once in order to make across taxonpair inferences about biogeographic processes while explicitly allowing for uncertainty in the demographic differences within each taxonpair.
Although the approach described here uses HABC to test for two particular biogeographic explanations of allopatric diversification across codistributed taxa, the HABC framework is flexible and therefore can provide a skeleton for testing other biogeographic models from comparative phylogeographic data. Indeed, one of the original objectives of phylogeography comparative was to resolve deepseated questions about how climate change drives community assembly and evolution of whole biotas [85]. However, this goal has so far been unrealized [86–88] because comparative phylogeographic studies rarely involve more than a handful of codistributed species. Comparative phylogeographic datasets are bound to have explosive growth as collecting DNA sequence data across a wide diversity of codistributed taxa scales up to the level of comprehensive ecosystem sampling. Such "communityscale" comparative phylogeographic data sets could potentially test classic biogeographic hypotheses (e.g. vicariance versus dispersal) at the community level [89, 90], as well as test controversial and fundamental hypotheses in community ecology such as Hubbell's Neutral theory [91], Tillman's stochastic competitive assembly model [92], and Diamond's niche assembly rules [93, 94]. As comparative phylogeographic datasets grow to include > 100 codistributed taxonpairs, the HABC approach will be well suited to dissect temporal patterns in community assembly and thereby provide a bridge linking comparative phylogeography with community ecology.
Abbreviations
 HABC:

Hierarchical Approximate Bayesian Computation
 mtDNA:

Mitochondrial DNA
 COI:

Cytochrome oxidase 1.
References
 1.
Mayr E: Geographic speciation in tropical echinoids. Evolution. 1954, 8: 118. 10.2307/2405661.
 2.
Mayr E: Animal species and evolution. 1963, Cambridge, MA: Harvard University Press
 3.
Zigler KS, McCartney MA, Levitan DR, Lessios HA: Sea urchin bindin divergence predicts gamete compatibility. Evolution. 2005, 59: 23992404.
 4.
Palumbi SR: Genetic divergence, reproductive isolation, and marine speciation. Annu Rev Ecol Syst. 1994, 25: 547572. 10.1146/annurev.es.25.110194.002555.
 5.
Palumbi SR, Lessios HA: Evolutionary animation: How do molecular phylogenies compare to Mayr's reconstruction of speciation patterns in the sea?. Proc Natl Acad Sci USA. 2005, 102: 65666572. 10.1073/pnas.0501806102.
 6.
Palumbi S: Marine speciation on a small planet. TREE. 1992, 7 (4): 114118.
 7.
Paulay G, Meyer C: Dispersal and divergence across the greatest ocean region: do larvae matter?. Integr Comp Biol. 2006, 46: 269281. 10.1093/icb/icj027.
 8.
Briggs: Centrifugal speciation and centres of origin. Journal of Biogeography. 2008, 27: 11831188. 10.1046/j.13652699.2000.00459.x.
 9.
Briggs JC: The marine East Indies: diversity and speciation. Journal of Biogeography. 2005, 32: 15171522. 10.1111/j.13652699.2005.01266.x.
 10.
Paulay G, Meyer C: Diversification in the Tropical Pacific: Comparisons Between Marine and Terrestrial Systems and the Importance of Founder Speciation. Integr Comp Biol. 2002, 42: 922934. 10.1093/icb/42.5.922.
 11.
Barber PH, Palumbi SR, Erdmann MV, Moosa MK: Sharp genetic breaks among populations of Haptosquilla pulchella (Stomatopoda) indicate limits to larval transport: patterns, causes, and consequences. Mol Ecol. 2002, 11 (4): 659674. 10.1046/j.1365294X.2002.01468.x.
 12.
Barber PH, Palumbi SR, Erdmann MV: Comparative phylogeography of three codistributed stomatopods: origins and timing of regional lineage diversification in the coral triangle. Evolution. 2006, 60: 18251839.
 13.
Ladd HS: Origin of the Pacific Island molluscan fauna. American Journal of Science. 1960, 258A: 137150.
 14.
Jokiel P, Martinelli FJ: The vortex model of coral reef biogeography. Journal of Biogeography. 1992, 19: 449458. 10.2307/2845572.
 15.
Waters JM, Dijkstra LH, Wallis GP: Biogeography of a southern hemisphere freshwater fish: how important is marine dispersal?. Mol Ecol. 2000, 9: 18151821. 10.1046/j.1365294x.2000.01082.x.
 16.
Yoder AD, Nowak MD: Has Vicariance or Dispersal Been the Predominant Biogeographic Force in Madagascar? Only Time Will Tell. Annual Review of Ecology, Evolution, and Systematics. 2006, 37: 405431. 10.1146/annurev.ecolsys.37.091305.110239.
 17.
Chesser RT, Zink RM: Modes of Speciation in Birds: A Test of Lynch's Method. Evolution. 1994, 48: 490497. 10.2307/2410107.
 18.
Losos JB, Glor RE: Phylogenetic comparative methods and the geography of speciation. Trends Ecol Evol. 2003, 18: 220227. 10.1016/S01695347(03)000375.
 19.
Wiley EO: Vicariance Biogeography. Annu Rev Ecol Syst. 1988, 19: 513542. 10.1146/annurev.es.19.110188.002501.
 20.
Wiley EO: Phylogenetic Systematics and Vicariance Biogeography. Systematic Botany. 1980, 5: 194220. 10.2307/2418625.
 21.
Nelson G, Platnick NI: Systematics and biogeography: cladistics and vicariance. 1981, New York: Columbia University Press
 22.
Brooks DR: Hennigs Parasitological method, a proposed solution. Syst Zool. 1981, 30 (3): 229249. 10.2307/2413247.
 23.
Ronquist F: Dispersalvicariance analysis: a new approach to the quantification of historical biogeography. Syst Biol. 1997, 46: 195203. 10.2307/2413643.
 24.
Zink RM, BlackwellRago RC, Ronquist F: The shifting roles of dispersal and vicariance in biogeography. Proceedings of the Royal Society of London, Series B. 2000, 267: 497503. 10.1098/rspb.2000.1028.
 25.
Ree RH, Moore BR, Webb CO, Donoghue MJ: A likelihood framework for inferring the evolution of geographic range on phylogenetic trees. Evolution. 2005, 59 (11): 22992311.
 26.
Ree RH, Smith SA: Maximumlikelihood inference of geographic range evolution by dispersal, local extinction, and cladogenesis. Syst Biol. 2008, 57: 414. 10.1080/10635150701883881.
 27.
Sanmartín I, Mark van der P, Ronquist F: Inferring dispersal: a Bayesian approach to phylogenybased island biogeography, with special reference to the Canary Islands. Journal of Biogeography. 2007, 35: 428449. 10.1111/j.13652699.2008.01885.x.
 28.
Noonan BP, Chippindale PT: Vicariant origin of Malagasy reptiles supports Late Cretaceous Antarctic landbridge. Am Nat. 2006, 168: 730741. 10.1086/509052.
 29.
de Queiroz K: The resurrection of oceanic dispersal in historical biogeography. Trends Ecol Evol. 2005, 20: 6873. 10.1016/j.tree.2004.11.006.
 30.
Waters JM: Driven by the West Wind Drift? A synthesis of southern temperate marine biogeography, with new directions for dispersalism. Journal of Biogeography. 2008, 35: 417427. 10.1111/j.13652699.2007.01724.x.
 31.
Cunningham CW, Collins TM: Beyond area relationships: Extinction and recolonization in molecular marine biogeography. Molecular Ecology and Evolution: Approaches and Applications. Edited by: Schierwater B, Streit B, Wagner G, DeSalle R. 1998, Basel, Switzerland: Birkhauser Verlag, 297322. 2
 32.
Waters JM, Craw D: Goodbye Gondwana? New Zealand Biogeography, Geology, and the Problem of Circularity. Syst Biol. 2006, 55: 351356. 10.1080/10635150600681659.
 33.
Brumfield RT, Edwards SV: Evolution into and out of the Andes: a Bayesian analysis of historical diversification in Thamnophilus antshrikes. Evolution. 2007, 61 (2): 346367. 10.1111/j.15585646.2007.00039.x.
 34.
Harrison RG: Molecular changes at speciation. Annu Rev Ecol Syst. 1991, 22: 281308. 10.1146/annurev.es.22.110191.001433.
 35.
Hickerson MJ, Stahl E, Lessios HA: Test for simultaneous divergence using approximate Bayesian computation. Evolution. 2006, 60: 24352453.
 36.
Hickerson MJ, Stahl E, Takebayashi N: msBayes: Pipeline for testing comparative phylogeographic histories using hierarchical approximate Bayesian computation. BMC Bioinformatics. 2007, 8: 26810.1186/147121058268.
 37.
Slatkin M: Gene flow in natural populations. Ann Rev Ecol Syst. 1985, 16: 393430. 10.1146/annurev.ecolsys.16.1.393.
 38.
Gelman A, Carlin JB, Stern HS, Rubin DB: Bayesian Data Analysis. 1995, London, UK: Chapman and Hall/CRC
 39.
James W, Stein C: Estimation with quadradic loss. Proceedings of the Fourth Berkeley Symposium on Mathematical Statistics and Probability: 1960. 1960, Berkeley, CA: University of California Press
 40.
Beaumont MA, Rannala B: The Bayesian revolution in genetics. Nat Rev Genet. 2004, 5: 251261. 10.1038/nrg1318.
 41.
Leaché A, Crews SA, Hickerson MJ: Did an ancient seaway across Baja California cause community isolation?. Biology Letters. 2007, 3: 646650. 10.1098/rsbl.2007.0368.
 42.
Beaumont MA, Zhang W, Balding DJ: Approximate Bayesian computation in population genetics. Genetics. 2002, 162: 20252035.
 43.
Tajima F: Statistical method for testing the neutral mutation hypothesis by DNA polymorphism. Genetics. 1989, 123: 585595.
 44.
Gelman A, Carlin JB, Stern HS, Rubin DB: Bayesian Data Analysis. 2004, Boca Raton, FL: Chapman and Hall/CRC
 45.
Hudson RR: Generating samples under a WrightFisher neutral model of genetic variation. Bioinformatics. 2002, 18: 337338. 10.1093/bioinformatics/18.2.337.
 46.
Tajima F: Evolutionary relationship of DNA sequences in finite populations. Genetics. 1983, 105: 437460.
 47.
Kass RE, Raftery A: Bayesian factors. Journal of the American Statistical Association. 1995, 90: 773795. 10.2307/2291091.
 48.
Fagundes NJR, Ray N, Beaumont M, Neuenschwander S, Salzano FM, Bonatto SL, Excoffier L: Statistical evaluation of alternative models of human evolution. Proc Natl Acad Sci USA. 2007, 104: 1761417619. 10.1073/pnas.0708280104.
 49.
François O, Blum MGB, Jakobsson M, Rosenberg NA: Demographic History of European Populations of Arabidopsis thaliana. PLoS Genetics. 2008, 4: e100007510.1371/journal.pgen.1000075.
 50.
Beaumont MA: Joint determination of topology, divergence time and immigration in population trees. Simulations, Genetics and Human Prehistory. Edited by: Matsumura S, Forster P, Renfrew C. 2008, Cambridge: McDonald Institute for Archaeological Research, 135154.
 51.
Rosenblum E, Hickerson MJ, Moritz C: A multilocus perspective on colonization accompanied by selection and gene flow. Evolution. 2007, 61: 29712985. 10.1111/j.15585646.2007.00251.x.
 52.
Machado CA, Kilman RM, Market J, Hey J: Inferring the history of speciation from multilocus DNA sequence data: the case of Drosophila pseudoobscura and close relatives. Mol Biol Evol. 2002, 19: 472488.
 53.
Hey J, Nielsen R: Multilocus methods for estimating population sizes, migration rates and divergence time, with applications to the divergence of Drosophila pseudoobscura and D. persimilis. Genetics. 2004, 167: 747760. 10.1534/genetics.103.024182.
 54.
Osada N, Wu CI: Inferring the mode of speciation with genomic data – Examples from the great apes. Genetics. 2005, 169: 259264. 10.1534/genetics.104.029231.
 55.
Zhou R, Zeng K, Wu W, Chen X, Yang Z, Shi S, Wu CI: Population Genetics of Speciation in Nonmodel Organisms: I. Ancestral Polymorphism in Mangroves. Mol Biol Evol. 2007, 24: 27462754. 10.1093/molbev/msm209.
 56.
Gelman A, Hill J: Data analysis using regression and multilevel/hierarchical models. 2007, New York, NY: Cambridge University Press
 57.
Hahn MW: Towards a selection theory of molecular evolution. Evolution. 2008, 62: 255265. 10.1111/j.15585646.2007.00308.x.
 58.
Gillespie JH: Is the population size of a species relevant to its evolution. Evolution. 2001, 55: 21612169.
 59.
Bazin: Population Size Does Not Influence Mitochondrial Genetic Diversity in Animal. Science. 2006, 312: 570572. 10.1126/science.1122033.
 60.
Hendry AP, Nosil P, Rieseberg LH: The speed of ecological speciation. Functional Ecology. 2007, 21: 455464. 10.1111/j.13652435.2007.01240.x.
 61.
Gavrilets S, Vose A: Dynamic patterns of adaptive radiation. Proc Natl Acad Sci USA. 2005, 13: 1804018045. 10.1073/pnas.0506330102.
 62.
Nosil P, Vines TH, Funk DJ: Reproductive isolation caused by natural selection against immigrants from divergent habitats. Evolution. 2005, 59: 705719.
 63.
Meyer CP, Paulay G: DNA barcoding: Error rates based on comprehensive sampling. PLoS Biol. 2005, 3 (12): e42210.1371/journal.pbio.0030422.
 64.
Wakeley J, Lessard S: Corridors for migration between large subdivided populations, and the structured coalescent. Theor Popul Biol. 2006, 70: 412420. 10.1016/j.tpb.2006.06.001.
 65.
Wakeley J, Takahashi T: The manydemes limit for selection and drift in a subdivided population. Theor Popul Biol. 2004, 66: 8391. 10.1016/j.tpb.2004.04.005.
 66.
Wakeley J: Recent trends in population genetics: More data! More math! Simple models?. Journal of Heredity. 2004, 95: 397405. 10.1093/jhered/esh062.
 67.
Notohara M: The strong migration limit for the genealogical process in geographically structured populations. J Math Biol. 1997, 36 (2): 188200. 10.1007/s002850050097.
 68.
Briggs JC: Marine centres of origin as evolutionary engines. Journal of Biogeography. 2003, 30: 118. 10.1046/j.13652699.2003.00810.x.
 69.
Briggs JC: The marine East Indies: center of origin?. Global Ecology and Biogeography. 1992, 2: 149156. 10.2307/2997803.
 70.
Briggs JC: Modes of speciation: Marine IndoWest Pacific. Bull Mar Sci. 1999, 65: 615656.
 71.
Coyne JA, Orr HA: Speciation. 2004, Sunderland, MA: Sinauer Associates Inc
 72.
Gavrilets S: Fitness landscapes and the origin of species. 2004, Princeton, NJ: Princeton University Press
 73.
Rehder HA: The Marine Molluscan Fauna of the Marquesas Islands. American Malacological Union. 1968, 2932.
 74.
Randall JE: Zoogeography of shore fishes of the IndoPacific region. Zool Stud. 1998, 37: 227268.
 75.
Kay EA, Palumbi SR: Endemism and evolution in Hawaiian, USA marine invertebrates. Trends Ecol Evol. 1987, 2 (7): 183186. 10.1016/01695347(87)900176.
 76.
Grigg RW: Paleoceanography of coral reefs in the HawaiianEmperor Chain – revisted. Coral Reefs. 1997, 16: S33S38. 10.1007/s003380050239.
 77.
Fleischer RC, McIntosh CE, Tarr CL: using phylogeographic reconstructions and KArbased ages of the Hawaiian Islands to estimate molecular evolutionary rates. Mol Ecol. 1998, 7 (4): 533545. 10.1046/j.1365294x.1998.00364.x.
 78.
Kobayashi DR: Colonization of the Hawaiian Archipelago via Johnston Atoll: a characterization of oceanic transport corridors for pelagic larvae using computer simulation. Coral Reefs. 2006, 25: 407417. 10.1007/s0033800601185.
 79.
Rivera MJ, Kelley CD, Roderick GK: Subtle population genetic structure I nthe Hawaiian grouper, Epinephelus quernus (Serranidae) as revealed by mitochondrial DNA analyses. Biol J Linn Soc. 2004, 81: 449468. 10.1111/j.10958312.2003.00304.x.
 80.
Grigg RW: Acropora in Hawaii USA 2. Zoogeography. Pacific Science. 1981, 35: 113.
 81.
McNutt M, Bonneville A: A shallow, chemical origin for the Marquesas Swell. Geochemistry Geophysics Geosystems. 2000, 1:
 82.
Smouse PE: To tree or not to tree. Mol Ecol. 1998, 7: 399412. 10.1046/j.1365294x.1998.00370.x.
 83.
Knowles LL, Maddison WP: Statistical phylogeography. Mol Ecol. 2002, 11 (12): 26232635. 10.1046/j.1365294X.2002.01637.x.
 84.
Panchel M, Beaumont BA: The automation and evaluation of nested clade phylogeographic analysis. Evolution. 2007, 61 (6): 14661480. 10.1111/j.15585646.2007.00124.x.
 85.
Avise JC, Arnold J, Ball RM, Bermingham E, Lamb T, Neigel JE, Reeb CA, Saunders NC: Intraspecific phylogeography: The mitochondrial DNA bridge between population genetics and systematics. Ann Rev Ecol Syst. 1987, 18: 489522.
 86.
Avise JC: Phylogeography: The history and formation of species. 2000, Cambridge: Harvard University Press
 87.
Bermingham E, Moritz C: Comparative phylogeography: concepts and applications. Mol Ecol. 1998, 7: 367369. 10.1046/j.1365294x.1998.00424.x.
 88.
Arbogast BS, Kenagy GJ: Comparative phylogeography as an integrative approach to historical biogeography. Journal of Biogeography. 2001, 28: 819825. 10.1046/j.13652699.2001.00594.x.
 89.
Rosen DE: Vicariant Patterns and Historical Explanation in Biogeography. Systematic Zoology. 1978, 27: 159188. 10.2307/2412970.
 90.
Carlquist C: The biota of longdistance dispersal, I: Principles of dispersal and evolution. Quarterly Review of Biology. 1966, 41: 247270. 10.1086/405054.
 91.
Hubbell SP: The Unified Neutral Theory of Biodiversity and Biogeography. 2001, Princeton, NJ: Princeton University Press
 92.
Tillman D: Niche tradeoffs, neutrality, and community structure: A stochastic theory of resource competition, invasion, and community assembly. Proc Natl Acad Sci USA. 2004, 101: 1085410861. 10.1073/pnas.0403458101.
 93.
Gotelli NJ, McCabe DJ: Species cooccurrence: a metaanalysis of j. M. Diamond's assembly rules model. Ecology. 2002, 83: 20912096.
 94.
Diamond JM: Assembly of Species Communities. Ecology and Evolution of Communities. Edited by: Cody ML, Diamond JM. 1975, Belknap: Harvard, 342444.
Acknowledgements
We thank M. Beaumont for kindly providing R scripts used in the HABC algorithm; W. Huang, E. Stahl and N. Takebayashi for collaboration in the ongoing development of the MSBAYES software pipeline; and the International Biogeography Society for inviting us to participate in the special symposium in marine biogeography at the 2007 meeting. We thank A. Pyron for coining the term "soft vicariance". M. Beals, W. Woodman and D. Watts are gratefully acknowledged for providing key specimens. M. Hickerson was supported by NSF (DEB 073648) and C. Meyer was supported by NSF (DEB9807316 & 0316338, OCE0221382). We also greatly thank the anonymous reviewers and the communicating editor H. Zauner for useful comments and suggestions to improve the manuscript.
Author information
Additional information
Authors' contributions
MH developed, tested, and implemented the HABC model. CM collected and sequenced the cowrie data and provided feedback on model development. Both MH and CM contributed to the writing.
Electronic supplementary material
Authors’ original submitted files for images
Below are the links to the authors’ original submitted files for images.
Rights and permissions
This article is published under license to BioMed Central Ltd. This is an Open Access article distributed under the terms of the Creative Commons Attribution License (http://creativecommons.org/licenses/by/2.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.
About this article
Received
Accepted
Published
DOI
Keywords
 Root Mean Square Error
 Colonization Model
 Local Linear Regression
 Temporal Congruence
 Average Pairwise Difference