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Ecology and Evolution logoLink to Ecology and Evolution
. 2023 Jan 18;13(1):e9673. doi: 10.1002/ece3.9673

Pollinator and host sharing lead to hybridization and introgression in Panamanian free‐standing figs, but not in their pollinator wasps

Jordan D Satler 1,, Edward Allen Herre 2, Tracy A Heath 1, Carlos A Machado 3, Adalberto Gómez Zúñiga 2, K Charlotte Jandér 4, Deren A R Eaton 5, John D Nason 1
PMCID: PMC9848820  PMID: 36699574

Abstract

Obligate pollination mutualisms, in which plant and pollinator lineages depend on each other for reproduction, often exhibit high levels of species specificity. However, cases in which two or more pollinator species share a single host species (host sharing), or two or more host species share a single pollinator species (pollinator sharing), are known to occur in current ecological time. Further, evidence for host switching in evolutionary time is increasingly being recognized in these systems. The degree to which departures from strict specificity differentially affect the potential for hybridization and introgression in the associated host or pollinator is unclear. We addressed this question using genome‐wide sequence data from five sympatric Panamanian free‐standing fig species (Ficus subgenus Pharmacosycea, section Pharmacosycea) and their six associated fig–pollinator wasp species (Tetrapus). Two of the five fig species, F. glabrata and F. maxima, were found to regularly share pollinators. In these species, ongoing hybridization was demonstrated by the detection of several first‐generation (F1) hybrid individuals, and historical introgression was indicated by phylogenetic network analysis. By contrast, although two of the pollinator species regularly share hosts, all six species were genetically distinct and deeply divergent, with no evidence for either hybridization or introgression. This pattern is consistent with results from other obligate pollination mutualisms, suggesting that, in contrast to their host plants, pollinators appear to be reproductively isolated, even when different species of pollinators mate in shared hosts.

Keywords: Ficus, hybridization, introgression, phylogeny, pollination mutualism, Tetrapus


Deviations from strict host specificity in obligate pollination mutualisms provide opportunities for interspecific interactions between plant species, pollinator species, or both. We find fig–pollinator wasps to be well‐delimited species, deeply divergent from one another, with no evidence for hybridization or introgression. By contrast, host fig species demonstrate hybridization in shallow time scales and introgression in deep time scales, suggesting different evolutionary processes shape diversification in the fig and fig wasp mutualism.

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1. INTRODUCTION

Hybridization and introgression have contributed to the evolution of species and clades across the tree of life (Anderson, 1953; Mallet, 2005; Mallet et al., 2016; Stebbins, 1959). Genome‐scale data and advances in analytical techniques, in particular, have enabled the detection and documentation of hybridization and introgression in many groups and suggest that these processes are more widespread than previously thought (Taylor & Larson, 2019). These processes can be important contributors to speciation and adaptive radiations, which can be spurred by the introduction of beneficial alleles and multilocus combinations to a recipient lineage (adaptive introgression; e.g., Edelman & Mallet, 2021; Hedrick, 2013). Adaptive introgression has been documented in a diversity of lineages, including cichlid fishes (Malinsky et al., 2018; Meier et al., 2017; Svardal et al., 2020), butterflies (Edelman et al., 2019; Enciso‐Romero et al., 2017; Pardo‐Diaz et al., 2012), and oaks (Eaton et al., 2015; Leroy et al., 2020; McVay et al., 2017). Interspecific gene flow can also contribute to adaptive responses to rapidly changing environments, such as human‐caused environmental modifications (Hamilton & Miller, 2016). Consequently, there is growing appreciation for the importance of hybridization and introgression in generating and maintaining organismal adaptation and diversity.

Flowering plants and their animal pollinators provide useful case studies for showing how ecological interactions can affect gene flow patterns and evolutionary trajectories (e.g., reproductive isolation or introgression in the associated host and pollinator lineages). Of particular interest, brood pollination mutualisms consist of host and pollinator lineages that obligately depend on each other for reproduction and survival. Examples of these highly specialized interactions include figs and fig wasps, yuccas and yucca moths, leafflowers and leafflower moths, globeflowers and globeflower flies, and palms and weevils (Cruaud et al., 2012; de Medeiros & Farrell, 2020; Hembry & Althoff, 2016; Pellmyr et al., 2020). Brood pollination mutualisms often exhibit strict host specificity (i.e., only one pollinator species is consistently associated with only one host species), which is thought to promote reproductive isolation for both the host and the pollinator.

Several studies, however, have revealed that two or more pollinator species per host (host sharing), or two or more host species per pollinator (pollinator sharing), are not uncommon in some systems (Cornille et al., 2012; McLeish & Van Noort, 2012; Molbo et al., 2003; Starr et al., 2013; Su et al., 2022; Wang et al., 2016; Yang et al., 2015). These reduced specificity ecological interactions, along with accumulating molecular evidence of historical host switching (e.g., Cruaud et al., 2012; Hembry et al., 2013; Satler et al., 2019), are consistent with opportunities for hybridization in either the host, the pollinator, or both (Arteaga et al., 2020; Berg, 1989; Cornille et al., 2012; Leebens‐Mack et al., 1998; Machado et al., 2005; Rentsch & Leebens‐Mack, 2012; Wang et al., 2016; Wang, Zhang, et al., 2021). This raises the more general question of how different patterns of host specificity affect the evolutionary dynamics (e.g., hybrid formation and introgression versus reproductive isolation) for each partner species in obligate plant–pollinator mutualisms. These dynamics, in turn, will affect the processes of speciation and diversification in both taxa.

Figs (Ficus, family Moraceae) and their pollinator wasps (family Agaonidae) represent an ancient (~80 Ma) and diverse (~900 described species of figs) obligate pollination mutualism (Cook & Rasplus, 2003; Cruaud et al., 2012; Janzen, 1979; Machado et al., 2001; Wang, Zhang, et al., 2021; Weiblen, 2002). Pollination in this keystone mutualism results in fruit production that supports diverse frugivores across tropical and subtropical habitats worldwide (Shanahan et al., 2001). When receptive, the enclosed fig inflorescences (syconia) produce volatile chemicals that attract mated pollen‐bearing female fig wasps (Cornille et al., 2012; Grison‐Pigé et al., 2002; Hossaert‐McKey et al., 2010; Van Noort et al., 1989; Wang, Yang, et al., 2021; Ware et al., 1993). These foundress wasps enter the syconia to pollinate flowers and oviposit in a subset of them. The pollinated flowers usually develop as viable seeds, but those flowers that receive wasp eggs usually become galls that support the development of the wasp offspring. After maturing, the pollinator wasp offspring then mate within their natal fig syconia before females collect pollen and disperse—typically several kilometers (Ahmed et al., 2009; Herre, 1989; Nason et al., 1998)—to locate receptive syconia on other fig trees.

Fig‐pollinating wasp species often exhibit high levels of specificity to host fig species (Herre et al., 2008; Weiblen, 2002), which has contributed to the paradigm of one wasp to one fig. However, with increasingly deep spatial and temporal sampling, and the application of more sophisticated genetic techniques, it is increasingly clear that there is often considerable deviation from this paradigm. For example, several studies (based primarily on mitochondrial DNA) suggest some level of pollinator sharing or host sharing, and also imply host switching (e.g., Cornille et al., 2012; Darwell et al., 2014; Machado et al., 2005; Molbo et al., 2003; Wachi et al., 2016; Wang et al., 2016; Yang et al., 2015; Yu et al., 2019). Further, roughly 30% of fig species has been estimated to host multiple pollinator species at either local or regional scales (Yang et al., 2015). This contemporary host sharing is complemented by detailed studies documenting an evolutionary history of host switching (Satler et al., 2019). These departures from strict one wasp species to one fig species interactions can potentially introduce heterospecific pollen to non‐natal host fig species, allow individuals of heterospecific wasps to develop, and potentially mate within the same individual fig syconium, or both. These observations all motivate the question—to what degree are hybridization and introgression observed in host figs or pollinator wasps?

There is morphological and molecular evidence for the existence of successful natural hybridization and introgression among closely‐related fig species within specific fig sections (e.g., Berg, 1989; Jackson et al., 2008; Machado et al., 2005; Wilde et al., 2020). This appears to be the case even among distantly‐related fig species across distinct subgenera (Compton, 1990; Ramírez, 1994; Wang, Zhang, et al., 2021). In contrast to their fig hosts, however, the few studies conducted to date using microsatellites or even deeper genomic tools find little or no evidence of hybridization or successful introgression between co‐occurring pollinator wasp species (Molbo et al., 2003, 2004; Satler et al., 2022; Sutton et al., 2017). Importantly, no study has directly applied genomic tools that can reveal the presence of hybridization and introgression across both the host figs and their associated pollinator species comprising an entire local community. Therefore, it is unclear the degree to which pollinator sharing, host sharing, host switching, or some combination of the three, generate hybridization and introgression in the host figs or pollinator wasps, and what these different ecological interactions mean for the strengthening or weakening of species boundaries.

Here, we use genome‐wide sequence data to test for hybridization and introgression in all species comprising a community of Panamanian free‐standing fig hosts (five species of Ficus subgenus Pharmacosycea, section Pharmacosycea) and their associated pollinating fig wasps (six species of Tetrapus). We ask whether hybridization and introgression have been operating within either the host figs, pollinator wasps, or both, and if so, whether currently observed levels of species specificity (or lack thereof) explain these evolutionary processes. For the pollinating wasps, we find no evidence for hybridization or introgression among any of the Tetrapus species. We do identify, however, at least two pollinator species that are consistently pollinating and reproducing in more than one host fig species. For the host figs, we find that host species that frequently share the same pollinator species exhibit evidence of recent hybridization events (genetically identified F1 hybrids that are morphologically intermediate between parental types), as well as of historical introgression between two host fig species that are currently generating F1 hybrids. We discuss the implications of these findings for the evolutionary dynamics of speciation in the fig hosts and wasp pollinators and discuss how the processes shaping fig and fig wasp evolution are consistent with observations from other obligate pollination mutualisms.

2. MATERIALS AND METHODS

2.1. Wasp sampling and sequencing

We sampled pollinator wasps from the free‐standing fig community located in central Panama in the vicinity of the Barro Colorado Island Nature Monument (BCNM, Table S1). The fig species that comprise this community are F. glabrata, F. insipida, F. maxima, F. tonduzii, and F. yoponensis. These five morphologically distinct species are native to our central Panama study area (Croat, 1978) and comprise roughly one‐quarter of the 22 described species of neotropical free‐standing figs (Berg, 2006). The individual trees sampled were located along the shoreline of the Rio Chagres, Lake Gatun, and adjacent seasonally dry tropical forest, typically a few hundred meters to several kilometers apart. Between March 2015 and February 2019, pollinator wasps were sampled from these five host fig species for genome‐wide sequence analysis.

Mature fig syconia were brought to the lab on Barro Colorado Island where wasps were allowed to emerge in vials. To ensure independence among samples, one pollinator from each fig syconia was sampled and preserved in 95% EtOH or RNALater. Additionally, two wasp samples were also collected from sticky traps located near receptive figs of F. tonduzii. In total, we sampled 57 individual wasps representing six fig pollinator species from this community.

DNA was extracted using a Qiagen DNeasy blood and tissue kit (Qiagen Inc.). Illumina libraries were generated using a KAPA Hyper prep kit with custom indices as described in Glenn et al. (2019). Samples were sheared using a Covaris sonicator to an average size of 400–500 base pairs. Following library prep, we grouped samples into sets of eight and conducted probe hybridization targeting 2590 ultraconserved element (UCE) loci using the hymenopteran probe v2 set of Branstetter et al. (2017). Size distributions were assessed with a Bioanalyzer, and samples were grouped in equimolar concentrations for sequencing. We sequenced libraries on an Illumina sequencer (HiSeq 3000 and HiSeq 4000) generating 150 bp paired‐end reads.

DNA sequence reads were processed with Phyluce v1.6.7 (Faircloth, 2015). Raw sequence reads were first processed with illumiprocessor v2.0.9 (Faircloth, 2013), a tool that uses Trimmomatic v0.39 (Bolger et al., 2014), to remove adapter contamination and poorly sequenced base pairs. Trinity v2.0.6 (Grabherr et al., 2011) was used to assemble cleaned reads into contigs. We then aligned contigs with the hymenopteran probe set v2 to retain only sequences matching a targeted UCE. Loci were aligned with MAFFT v7.407 (Katoh & Standley, 2013), and ends with high amounts of missing data were trimmed. Ambiguously aligned sites were removed with Gblocks v0.91b (Castresana, 2000) using default settings. We then filtered the cleaned sequence loci to retain those sampled in a minimum of 70% of individuals.

We also generated a phased data set for the UCE loci following the outline of Andermann et al. (2018). Briefly, we aligned our cleaned sequence reads back to aligned loci with BWA‐MEM as implemented in bwa v0.7.17 (Li & Durbin, 2010). Data were phased using the phase command in samtools v1.9 (Li et al., 2009) resulting in two alleles per individual per locus. Phased data sets were cleaned as outlined above, and loci with a minimum of 70% of individuals were once again saved for downstream analysis.

2.2. Wasp population structure and hybridization

We used two approaches to test for species boundaries and hybridization in the fig wasps. First, we used principal components analysis (PCA) to determine species groupings. In the absence of recent hybridization and introgression, individuals are expected to form distinct clusters corresponding to species. Hybrid individuals (F1s or subsequent backcrosses), by contrast, are expected to be located equidistant between species clusters while limited introgression is expected to result in intermixed species clusters. We conducted the PCA in R v3.6.3 (R Core Team, 2018) using the dudi.pca command in adegenet v2.1.3 (Jombart, 2008). For our input data set, we subsampled a single biallelic SNP per UCE locus. Missing data were replaced with the global mean allele frequency for that SNP. Because of a high amount of missing data for one individual (FW514), this sample was excluded from the analysis. We visualized results by plotting the first two principal component axes of variation.

Second, we explicitly tested for hybridization and introgression using the population graph and admixture approach as implemented in TreeMix v1.13 (Pickrell & Pritchard, 2012). TreeMix estimates a population graph with an a priori number of migration events between lineages, here species. This method allowed us to test whether a model with migration between wasp species is a better fit to the data than a strictly bifurcating model without migration. We analyzed the data in TreeMix using zero to three interspecific migration events and used the proportion of variance explained by the model to determine the optimal number of migration events. We used the phased data set and randomly subsampled a single biallelic SNP per locus for this analysis. If hybridization and introgression are not operating within this system, we would expect negligible improvement to the model as we add migration events.

2.3. Wasp phylogenetics

To infer wasp phylogenetic relationships, we estimated a maximum likelihood (ML) phylogeny of the concatenated UCE data set in IQ‐TREE v2.1.2 (Chernomor et al., 2016; Nguyen et al., 2015). This approach allowed us to determine whether individuals sampled from the same fig host species cluster together in phylogenetic space. We partitioned the concatenated data set by UCE locus and used ModelFinder (Kalyaanamoorthy et al., 2017) with Bayesian Information Criteria (BIC) to select the substitution model of best fit for each partition. We assessed nodal support by generating 1000 bootstrap replicates with the ultrafast bootstrap approximation (Hoang et al., 2018).

2.4. Wasp mitochondrial DNA

We wanted to compare phylogenetic patterns between the nuclear (UCE) and mitochondrial genomes. If individuals belonged to different clades between the species tree (estimated with nuclear UCE data) and the mitochondrial gene tree, the cytonuclear discordance could be explained by interspecific hybridization and introgression. To generate mtDNA data from our samples, we followed the outline of Satler et al. (2022). Briefly, we used NOVOPlasty v4.3.1 (Dierckxsens et al., 2017) to identify mitochondrial reads and generated haplotypes from off‐target reads present in the UCE sequencing files. We used a COI sequence from a Tetrapus species (AY148155) as our seed sequence. After recovering mtDNA haplotypes, we aligned these data with MAFFT v7.471 and trimmed the matrix to match the length of the seed sequence to minimize missing data. We then estimated an ML gene tree with IQ‐TREE, used ModelFinder with BIC to select the substitution model of best fit, and generated 1000 bootstrap replicates with the ultrafast bootstrap approximation. Finally, we tested for cytonuclear discordance by comparing the species compositions recovered with the mitochondrial DNA with those recovered with the nuclear (UCE) DNA.

2.5. Host associations

Through the estimation of well‐supported wasp and host fig phylogenies, as well as knowledge of the fig species from which wasps were sampled, we can determine the association between pollinator and host fig species. A one‐to‐one correspondence between a wasp species and an individual host species is indicative of current host specificity. By contrast, evidence of reduced specificity is indicated when two or more host lineages share the same pollinators or when two or more wasp lineages are associated with the same host. This information can be quantified over available wasp samples to estimate the frequency with which each wasp species is associated with each fig species and to identify those wasp and fig species that have higher or lower host specialization. Lower host specificity creates greater opportunities for interspecific interactions between wasps and between figs and provides a mechanism for hybridization.

Because our approach prioritized deep genomic sampling of individuals over sampling large numbers of individuals, we supplemented our data set with additional wasp individuals to increase the sample size for assessing the host specificity of the different pollinator wasp species. Specifically, we collected COI mtDNA data from an additional 201 wasps sampled from the fig species described above (with the exception of F. tonduzii). Genomic DNA was extracted, and COI sequences were generated and aligned following the methods described in Marussich and Machado (2007). These COI mtDNA data provide sufficient information for confirming species identification and for generating host association frequencies.

This independent COI data set was generated from samples collected between February 1997 and May 2005, earlier than the samples collected here for UCE sequencing. Because of potential pollinator turnover, we needed to confirm that the wasp species sampled for the newer UCE data set and the older COI data set were the same. To confirm wasp species identity between the two data sets, we combined the older COI data set of 201 wasps with our newer COI data set recovered from NOVOPlasty, resulting in a total of 257 sequences. We realigned these data with MAFFT, then estimated an ML gene tree with IQ‐TREE (as outlined above) to test for continuity of wasp species over these two time periods. Since the two data sets resulted in congruent wasp species inference, we used this information from the combined COI gene tree to determine host–pollinator association frequencies.

2.6. Fig sampling and sequencing

We sampled 30 fig trees representing all five free‐standing fig species present in our Panamanian Ficus community and that were sampled for pollinating wasps (Table S2). This included five trees that were putatively identified as F. glabrata × maxima hybrids and one tree identified as an F. insipida × maxima hybrid. Our initial hybrid identifications were based on intermediate leaf morphology and growth form. Genomic DNA was extracted using a modified CTAB protocol (Doyle & Doyle, 1987). Extractions were sent to Floragenex Inc. for restriction site‐associated DNA (RAD) library preparation. Single‐end RAD libraries were generated with the PstI restriction enzyme following the standard protocol (Baird et al., 2008). Libraries were sequenced on an Illumina HiSeq 3000 using 100 bp single‐end sequencing.

DNA sequence reads were processed with ipyrad v0.9.62 (Eaton & Overcast, 2020). No mismatches were allowed in barcodes when demultiplexing samples, with strict filtering used for removing any adapter contamination. Up to five low‐quality base calls were allowed in a read. We used a clustering threshold of 85% sequence similarity when assembling reads into loci within species. Within individuals, we allowed up to 5% Ns and 5% heterozygous sites per locus. Alleles were clustered across individuals using an 85% sequence similarity threshold. For clustered loci, we allowed up to 20% SNPs, up to 20% heterozygous sites, and up to eight total indels. Data sets were output varying the amount of missing data depending on the downstream application.

2.7. Fig population structure and hybridization

We conducted a PCA to determine whether fig species cluster in multivariate space and to identify any potential hybrid individuals located between species clusters. To reduce the potential negative effects of missing data, we output loci sampled from at least 90% of individuals and, from these data, selected a single SNP per locus. We conducted the PCA in R as described above for the wasps and visualized the first two axes of variation.

Based on the PCA of SNP data (see ‘Section 3’), we identified six individual fig trees as putative recent hybrids between F. glabrata and F. maxima and identified one individual as a putative hybrid between F. maxima and F. yoponensis. To further evaluate hybridization, we used fastSTRUCTURE (Raj et al., 2014) to estimate population membership between pure species and potential hybrids. fastSTRUCTURE uses a variational Bayesian framework to approximate the structure (Pritchard et al., 2000) model for estimating population membership. We created two data sets for fastSTRUCTURE, one that included individuals of F. glabrata, F. maxima, and putative hybrids between the two species, and one that included individuals of F. maxima, F. yoponensis, and their putative hybrid. We ran each data set under a two‐population model (K = 2). If individuals represent hybrids, we would expect them to show population membership in both clusters in their respective analyses. For fastSTRUCTURE, we used unlinked SNPs present in at least 50% of sampled individuals. To visualize the results, we used the R package pophelper v2.3.1 (Francis, 2017).

Of the hybrid figs identified in our community, we next wanted to know whether they were first‐generation hybrids (F1) or first‐generation backcrosses (BC1) to either parental species. Individuals backcrossing to a parental species are of interest because they provide a mechanism for the introgression of genetic material between species. To address this question, we used snapclust (Beugin et al., 2018) implemented in the R package adegenet. Snapclust is a maximum likelihood approach for assigning individuals to clusters, including both pure species and hybrids. Specifically, snapclust can model F1 hybrids as well as first‐ and second‐generation backcrosses, allowing the identification of the specific generation for a sampled hybrid. We partitioned samples into the same two data sets as described for fastSTRUCTURE and used the same genomic data as described for the PCA.

2.8. Fig phylogenetics and introgression

To estimate the phylogenetic relationships among these free‐standing figs, we used the coalescent‐based approach SVDQuartets (Chifman & Kubatko, 2014) as implemented in PAUP* v4.0a168 (Swofford, 2003). SVDQuartets uses site patterns in the nucleotide data to estimate a phylogeny under the coalescent model. Because hybridization and introgression are not accounted for in this method, we removed hybrid individuals identified by the above analyses from the unlinked SNP data set. Individuals were assigned to species a priori, all quartets were evaluated, and nodal support values were generated with 100 standard bootstrap replicates. We included an individual from F. obtusifolia (Bioaccession #SAMN12175287), a species of Neotropical strangler fig (Ficus subgenus Urostigma, section Americanae), to serve as the outgroup to estimate the root position of the phylogeny.

Although SVDQuartets estimates phylogenetic relationships among species while accounting for incomplete lineage sorting (ILS), the method does not model gene flow (i.e., it explicitly considers distinct nonhybridizing species). To test whether hybridization and subsequent introgression have been processes operating among these fig species at deeper time scales, we used the maximum pseudolikelihood approach SNaQ (Sols‐Lemus & Ané, 2016) as implemented in PhyloNetworks (Solís‐Lemus et al., 2017). This approach estimates a multispecies network by modeling the processes of ILS and hybridization. Thus, we can test whether a model allowing ILS and hybridization is a better fit to the data than a model only allowing ILS.

To estimate the phylogenetic network, we first generated concordance factors from our unlinked SNP data sampled from pure species (as in SVDQuartets, hybrids were removed) as outlined in Olave and Meyer (2020). Specifically, we used the R function SNPs2CF (www.github.com/melisaolave/SNPs2CF), sampled 100 alleles per species quartet (n.quartet = 100), and generated 100 bootstrap replicates. Using these concordance factors as input to SNaQ, we estimated networks allowing a maximum (hmax) number of between zero and three hybrid edges (i.e., hybridization events), doing 10 runs per analysis. For the network analysis with zero hybrid edges, we used the SVDQuartets species tree as the starting tree. For each subsequent analysis, we used the hmax – 1 network as our starting network. Pseudolikelihoods were compared across runs with different numbers of hybrid edges to estimate the network model with the best support. We then used the best model to estimate 100 bootstrap replicates to generate support for the presence of the hybrid edge(s) indicating historical gene flow and introgression between species.

3. RESULTS

3.1. Wasp population structure and hybridization

We generated 180,616,361 raw reads for the 57 fig wasp pollinator samples representing six pollinator species (Table S3). Individuals had on average 3,168,708 (±1,603,597) raw reads. Following data processing, individuals had on average 154,359 (±74,989) contigs with an average length of 379 (±211) base pairs. We generated contig data from 2248 total UCE loci, with each individual being sequenced at 1423 (±151) loci on average (Table S3).

All six wasp species are well differentiated with little intraspecific variation in PCA space (Figure 1). PC1 and PC2 explained 44.19% and 20.11% of the variation, respectively. Because we see tight clusters of individuals within species, and no spread of individuals between species, the PCA supports the pollinators as genetically distinct species with no recent hybridization or introgression.

FIGURE 1.

FIGURE 1

Population genetic and phylogenetic results for the fig‐pollinating wasps. (a) Principal component analysis (PCA) of the Tetrapus wasps. Species are genetically distinct with little intraspecific divergence. (b) An unrooted maximum likelihood phylogeny. All interspecific nodes are strongly supported with bootstrap values of 100. Fig host species names are shown in gray.

TreeMix results indicate that a model without hybridization provides the best fit to the data (Table 1). Although we estimated models with up to three admixture edges, there was essentially no increase in the proportion of variation explained by the model with the addition of admixture edges. Thus, the PCA and TreeMix results both show the pollinator species to be genetically distinct and reproductively isolated, with no evidence of hybridization.

TABLE 1.

TreeMix results for the pollinator wasps. We compared models allowing between zero (m0) and three (m3) admixture edges. There is essentially no increase in the proportion of variation explained by the model when allowing admixture edges, suggesting a model with zero admixture edges is the best fit for the data. This is consistent with an absence of introgression among these pollinator wasp species

Model Admixture events Percent variation
m0 0 99.87%
m1 1 99.99%
m2 2 99.99%
m3 3 99.99%

3.2. Wasp phylogenetics

In agreement with the PCA and TreeMix results, a concatenated ML tree of the UCE data detected six well‐defined and reciprocally monophyletic species (Figure 1). The tree was characterized by low intraspecific divergence and high interspecific divergence. All interspecific nodes have 100 bootstrap support values.

3.3. Wasp mitochondrial DNA

We were able to generate COI data from 56 of the 57 wasp individuals. After alignment and edge trimming, our COI matrix was composed of 816 base pairs. In agreement with the nuclear UCE phylogeny, our COI gene tree recovered six clades, all supported with bootstrap values of 100 (Figure S1). Once again, these species were characterized by low intraspecific divergence and high interspecific divergence. Results recovered with mtDNA data mirrored those recovered with UCE data, showing no cytonuclear discordance among species compositions between the two data sets.

3.4. Host associations

Species compositions were identical between the UCE nuclear phylogeny and the mitochondrial gene tree. Pollinator species have also been consistent temporally in this community between the previously generated COI data and the current UCE data set. We therefore combined our current sampling with the 201 samples directly sequenced for COI to quantify associations between host figs and pollinator wasps in this community (Figure 2). Additionally, because we identified six individual figs as being recent hybrids between F. glabrata and F. maxima (see below), we grouped these individuals as a distinct host fig species (F. glabrata × maxima) for understanding host associations.

FIGURE 2.

FIGURE 2

A heatmap showing the relative frequency with which each of the six Tetrapus wasp species was sampled from the five Pharmacosycea fig species for UCE and COI sequencing. Because we identified six individual figs as recent hybrids between Ficus glabrata and Ficus maxima, we treat them here as a distinct lineage for understanding host associations (see Section 3). Wasp and fig species are ordered from having higher to lower host or pollinator specificity, respectively. Rows with multiple entries represent cases of hosts sharing pollinators, which could promote hybridization between fig species. Columns with multiple entries represent cases of pollinators sharing hosts, which could promote wasp hybridization. Values in the cells are the numbers of wasps sampled per host combined over UCE and COI sequencing data sets.

Of the 258 wasps sampled, only three (1.2%) appear to be cases in which a single individual of a given wasp species pollinated a non‐natal host species (one individual each of T. costaricanus on F. maxima, T. sp. 1 on F. glabrata × maxima, and T. sp. 3 on F. glabrata). Looking beyond these rare “mistakes” in host association, a single pollinator species is associated with each of F. insipida (T. costaricanus), F. tonduzii (T. sp. 4), and F. yoponensis (T. ecuadoranus), strongly suggesting strict host specificity in these species. By contrast, we also identified clear cases of host sharing, resulting in potential wasp species co‐occurrence in the same figs of the same host species, and pollinator sharing, resulting in potential fig species being pollinated with interspecific pollen, and therefore opportunities for hybridization for both the figs and the wasps.

Specifically, two pollinator species are regularly associated with F. glabrata: one pollinator species is host‐specific (T. sp. 1), whereas the other species (T. sp. 2) is commonly associated with F. glabrata, F. maxima, and F. glabrata × maxima hybrids (Figure 2). Additionally, one pollinator species (T. sp. 3) is primarily associated with F. maxima, but individuals were also frequently sampled from F. glabrata × maxima hybrids. We thus have two cases of host sharing: (T. sp. 1) and (T. sp. 2) associated with F. glabrata, and (T. sp. 2) and (T. sp. 3) associated with maxima and also with F. glabrata × maxima hybrids (Figure 2). Moreover, we have two cases of pollinator sharing: F. glabrata, F. maxima, and F. glabrata X maxima hybrids share a pollinator (T. sp. 2), as do F. maxima and F. glabrata × maxima hybrids (T. sp. 3), which directly affects opportunities for hybridization among fig lineages. In sum, four of the pollinator species are host species‐specific while two are associated with multiple hosts.

3.5. Fig population structure and hybridization

We generated 263,931,402 raw reads for the 30 fig tree samples representing five fig species (Table S4). Individuals had on average 8,797,713 (±7,271,731) raw reads. Following data processing, individuals had on average 76,879 (±31,497) rad clusters (Table S4).

Requiring at least 90% coverage for loci, we used 9662 unlinked SNPs for the PCA. PC1 and PC2 explained 25.09% and 22.29% of the variation, respectively. Species are recovered as distinct clusters in PCA space (Figure 3). We also recovered individuals that appear to represent genetic hybrids. For example, we recovered six individuals as a cluster (black squares) approximately equidistant between F. glabrata and F. maxima. In addition, another putative hybrid fig individual (gray triangle) is equidistant between F. maxima and F. yoponensis. The existence of multiple hybrids between F. glabrata and F. maxima is consistent with the pollinator sharing observed between these two species, and the intermediate positions of these admixed fig individuals are consistent with recent hybridization.

FIGURE 3.

FIGURE 3

Population genetic and phylogenetic results for the host figs. (a) Principal component analysis (PCA) of section Pharmacosycea figs. Squares in black represent hybrid individuals between Ficus maxima and F. glabrata, with the triangle in gray representing a hybrid individual between F. maxima and F. yoponensis. Genetic structuring plots from fastSTRUCTURE—color‐coded to match corresponding species in the PCA—show hybridization between the species, with symbols (black squares and gray triangle) corresponding to individuals in the PCA plot. (b) Phylogenetic network of the fig species. Hybrid individuals were removed from this analysis. The best model places one hybrid edge between F. glabrata and F. maxima, estimating that F. maxima inherited 33.6% of its genome from F. glabrata. All nodes and the hybrid edge are strongly supported with bootstrap values of 100. The outgroup (F. obtusifolia) was removed for visual purposes.

To further explore species affinities of the putative hybrid individuals, we analyzed subsets of the data in fastSTRUCTURE. One analysis contained samples from F. glabrata, F. maxima, and the putative hybrids of the two, while the other contained samples from F. maxima, F. yoponensis, and the putative hybrid between those two. For each analysis, the two pure species were recovered as distinct with the putative hybrid samples showing admixed ancestry consistent with recent hybridization (Figure 3). To estimate whether these recent hybrids are first‐generation hybrids (F1s) or first‐ or second‐generation backcrosses, we analyzed the two data sets in snapclust. The result for the F. glabrata and F. maxima data set estimated that five individuals are F1 hybrids and one individual is a first‐generation backcross (BC1) to F. glabrata (Figure S2). The results for the F. maxima and F. yoponensis data set estimated the putative hybrid individual to be an F1 hybrid (Figure S2). These results confirm the presence of seven recent hybrids (six F1s, one BC1) in our sampled fig community, with the remaining individuals assigned to pure species.

3.6. Fig phylogenetics and introgression

Our species tree estimated with SVDQuartets recovers the fig species in two clades: one supporting F. glabrata and F. insipida as sister species, with F. yoponensis sister to them (all nodes strongly supported with a bootstrap value of 100), and a weakly supported sister relationship (bootstrap value of 51) between F. maxima and F. tonduzii (Figure S3). Although we sampled six hybrids between F. glabrata and F. maxima, demonstrating recent hybridization, these two species were not recovered as sister species in our phylogeny. This phylogenetic pattern is also the case with F. maxima and F. yoponensis, where they have produced an F1 hybrid but were not estimated to be sister species.

Because SVDQuartets does not explicitly consider hybridization and only models the process of ILS, we used a network approach to test whether accounting for hybridization better reflects the evolutionary history of this community of fig species. Although we tested models with up to three hybrid edges, models with hmax >1 always estimated a phylogenetic network with a single hybrid edge. While there was a drastic decrease in the pseudolikelihood from a model with zero hybrid edges (−3743.91) to a model with one hybrid edge (−1154.21), there was no decrease when allowing more hybrid edges. This suggests that a phylogenetic network with one hybrid edge best fits our data. This single hybrid edge was placed between F. glabrata and F. maxima with a bootstrap value of 100, and with 33.6% of the genome of F. maxima inferred to be inherited from F. glabrata (Figure 3). The phylogenetic relationships estimated in SNaQ are all strongly supported (bootstrap values of 100) and show the same pattern as relationships estimated with SVDQuartets.

4. DISCUSSION

We collected genome‐wide sequence data from all species comprising a community of central Panamanian free‐standing fig species and their associated pollinator wasp species. We used these data to assess evidence for hybridization and introgression in both the fig and pollinator taxa. Given the observed levels of pollinator and host sharing in this system, we applied rigorous genomic tests to determine whether associations with lower species specificity have contributed to hybridization and introgression in the host figs, the pollinator wasps, or both. For the host figs, we identified several individual F1 hybrids demonstrating hybridization at shallow time scales and recovered evidence for historical introgression at deeper time scales between two species (F. glabrata and F. maxima) known to currently share pollinator species in central Panama. By contrast, we found no evidence of hybridization or introgression among any of the pollinator wasp species in either shallow or deep time scales. These results suggest that pollinator sharing has generated genetic exchange between their host figs, blurring species boundaries. Yet, despite potential interspecific interactions resulting from sharing host species, reproductive isolation has apparently only been reinforced in the fig wasps.

4.1. Pollinator sharing leads to hybridization in the figs

Pollinating fig wasps often appear to be highly species‐specific in their associations with host figs (Bronstein, 1987; Moe et al., 2011; Ramírez, 1970; Satler et al., 2022). The degree to which this is true constrains the opportunities for hybridization (and subsequent introgression) in both lineages. Strict species specificity by the pollinators necessarily limits potential interspecific pollination in their hosts. For host figs to have opportunities for hybridization, several barriers must be overcome by pollinators. A wasp bearing heterospecific pollen must disperse and recognize a species different from the one in which she developed (Compton, 1990; Nason et al., 1996). Once inside the syconium, the wasp must be able to put viable pollen grains in contact with the stigmatic surfaces of receptive flowers, so that they can potentially produce viable F1 seeds.

However, even occasional or rare opportunities can be sufficient to promote genetic exchange between either the fig or pollinator species. For example, Moe and Weiblen (2012) tested for reproductive isolation among six sympatric dioecious fig species found in New Guinea. Using microsatellite data, they found 7 of 300 individual trees sampled to be of hybrid origin, demonstrating occasional hybrid formation even though pollinators are primarily host species‐specific in the community (Moe et al., 2011). This shows that even limited opportunities for pollinator sharing and heterospecific pollen transfer can be sufficient to induce hybridization and, potentially, subsequent introgression in the host figs.

Of the six pollinator species sampled in the Panamanian community, two species are regularly associated with multiple fig species. One pollinator species (T. sp. 2) pollinates and successfully develops in F. glabrata, F. maxima, and F. glabrata X maxima hybrids, while a second (T. sp. 3) pollinates and successfully develops in F. maxima and F. glabrata X maxima hybrids. Pollinator sharing by these two wasp species predicts opportunities for hybrid formation between the host species, F. glabrata and F. maxima. This is exactly what we observe.

Of the 30 individual fig trees sampled, some appeared to be morphological intermediates, suggesting hybrid individuals. Our genetic tests confirmed this, identifying five F1s and one BC1 between F. glabrata and F. maxima. We then used a phylogenetic network approach restricting our data set to only individuals representing pure species. Using this method, the best model placed a hybrid edge indicating introgression between F. glabrata and F. maxima (Figure 3). These results demonstrate that hybridization and introgression between F. glabrata and F. maxima are both ongoing and have been operating at deeper time scales, shaping the evolution of these two fig species. Although F. glabrata and F. maxima are genetically and morphologically distinct, incomplete reproductive isolation allows for hybrid compatibility and, thus, porous species boundaries in these two species. In addition, our genetic tests identified an F1 hybrid fig between F. maxima and F. yoponensis, and morphological intermediates between F. insipida and F. yoponensis have been observed but unfortunately were not tested genetically (E. A. Herre, personal observation).

Evidence for hybridization and introgression have been detected in other sections of Ficus. In the Neotropics, Machado et al. (2005) and Jackson et al. (2008) used data from multiple loci to recover evidence supporting hybridization among several species of Panamanian strangler figs (Ficus subgenus Urostigma, section Americanae). Notably, a subset of these strangler figs in the Panamanian community is known to share pollinator species (Jackson et al., 2008; Machado et al., 2005; Molbo et al., 2003; Satler et al., 2019, 2022), providing a potential mechanism for interspecific pollination and hybridization. Sampling from a community of five dioecious fig species (Ficus subgenus Sycomorus, sections Sycomorus and Hemicardia) distributed in southeast Asia, Wang et al. (2016) found evidence of both pollinator sharing and host fig hybridization. In particular, they found that 13.15% of sampled pollinator wasps was associated with non‐natal fig host species, and 4.68% of fig individuals was of hybrid origin. In Australia, Wilde et al. (2020) found evidence of hybridization and subsequent backcrossing between two dioecious sandpaper fig species, F. aculeata and F. coronulata. Although the pollinator species is unknown for these two fig species, Wilde et al. (2020) suggest that the fig hybrids provide another example of a breakdown of the one‐to‐one fig–pollinator association.

Cytonuclear discordance also suggests historical introgression as an important process in the fig section Galoglychia (Renoult et al., 2009) and across species in even distantly‐related fig sections in general (Bruun‐Lund et al., 2017). In particular, Wang, Zhang, et al. (2021) analyzed whole‐genome sequence data (including nuclear, mitochondrial, and chloroplast genomes) from lineages representing all major fig sections and recovered an extensive history of hybridization and introgression—both within and between sections—in Ficus. Although there are several prezygotic mechanisms potentially limiting fig hybridization, including the production of host‐specific pollinator‐attracting floral volatile blends (Cornille et al., 2012; Grison‐Pigé et al., 2002; Hossaert‐McKey et al., 2010; Van Noort et al., 1989; Wang, Yang, et al., 2021; Ware et al., 1993), these barriers appear to be less restrictive in the figs than in the pollinators. Our results are consistent with previous evidence and suggest that hybridization and introgression have been processes operating in shallow and deep time scales in the evolution of the figs, but not in the evolution of their pollinator wasps. This asymmetry in the relative importance of introgression appears to be an integral characteristic of the evolutionary history of the fig and fig wasp pollinator mutualism.

4.2. Figs and their wasp pollinators differ in rates of successful hybridization

Evolutionary processes in the fig–pollinator mutualism appear to affect figs and wasps differently. While signatures of hybridization and introgression are present in host fig species (Bruun‐Lund et al., 2017; Machado et al., 2005; Renoult et al., 2009; Wang, Zhang, et al., 2021; Wilde et al., 2020), there is little evidence these processes affect fig wasp pollinators (see Molbo et al., 2003, 2004; Satler et al., 2022; Sutton et al., 2017). This suggests that the processes governing reproductive isolation operate differently within each lineage (figs–plants versus wasps–insects). Particularly when the one‐to‐one fig‐to‐wasp association is broken, many factors potentially contribute to the mechanisms allowing for hybridization and introgression within the figs, but apparently not within the pollinators.

As the pollinators of fig trees, fig wasps determine patterns of pollen gene flow between conspecific hosts, heterospecific hosts, or both. Whether a pollen‐bearing wasp emerges from a given host species and then pollinates a different host species defines the opportunities for hybridization and introgression for their hosts. Thus, the ability of a pollinator—carrying heterospecific pollen—to detect, locate, enter, and successfully pollinate a non‐natal fig species is critical for either reinforcing or blurring species boundaries. And because exceptions to the one‐to‐one fig‐to‐pollinator association are becoming more evident with increased taxon and genetic sampling (Darwell et al., 2014; Souto‐Vilarós et al., 2019; Su et al., 2022; Sutton et al., 2017; Yang et al., 2015; Yu et al., 2019), coupled with a growing appreciation of the role of host switching in these systems (Satler et al., 2019), it is probable that hybridization and introgression in the host figs are more widespread than previously realized. Indeed, an increase in genomic data sets has led to an increase in the detection of hybridization events across the tree of life (Taylor & Larson, 2019). We suggest this will also be the case for figs as more systems are explored with genome‐scale data and are explicitly tested for hybridization and introgression (Wang, Zhang, et al., 2021).

In our community of Tetrapus wasps, species are genetically distinct and are highly divergent (Figure 1). This result is consistent with genetic studies of fig wasps, where species typically show little intraspecific divergence but are deeply divergent from other species (e.g., Satler et al., 2022). The lack of hybridization and introgression in Tetrapus wasps is congruent with results from a recent study of Neotropical strangler fig pollinators. For example, Satler et al. (2022) sampled over 1000 genome‐wide UCE loci from a central Panamanian community of 19 Pegoscapus species associated with 16 strangler fig species. They recovered no signal of hybridization or introgression among these pollinators, even among pollinators known to share the same host fig species and to mate within the same fig syconia. In Australia, Sutton et al. (2017) sampled multiple pollinator species associated with the host figure F. rubiginosa. Even though 13% of figs had syconia with multiple pollinator species, they recovered no evidence of hybridization between pollinator species. Between the results presented here and others (Satler et al., 2022; Sutton et al., 2017), studies that have explicitly tested for interspecific hybridization and introgression among fig‐pollinating wasps have yet to find evidence for these evolutionary processes. Thus, on the one hand, the fig mating system fosters reproductive isolation by promoting host specificity and limiting opportunities for heterospecific pollen transfer, but pollinator sharing nonetheless occurs and leads to hybridization and introgression between numerous fig species. On the other hand, the occurrence of host sharing and host switching creates opportunities for interspecific interactions among wasp species, yet hybridization and introgression are apparently rare or absent. Similarly, in the yucca and yucca moth system, another well‐known obligate pollination mutualism, the host plants are known to share pollinators and to hybridize (Arteaga et al., 2020; Leebens‐Mack et al., 1998; Rentsch & Leebens‐Mack, 2012; Smith et al., 2008; Starr et al., 2013; Yoder et al., 2013), while the pollinators are genetically distinct and exhibit no evidence of hybridization (Leebens‐Mack et al., 1998). As in the yucca pollinators, it appears that hybridization and introgression of fig–pollinator wasps have not been processes influencing their diversification or coevolution with their host plants.

If hybridization occurs at a low rate within this fig wasp community, this should be detectable given the large number of marker loci we sampled, and yet, we may have missed sampling occasional first‐generation hybrid individuals. For example, Molbo et al. (2003, 2004) detected rare F1 hybrids between sister pollinator species in a Panamanian strangler fig community but estimated no introgression between these species. This suggests rare hybrid events may occur between closely‐related species, but F1 individuals fail to reproduce. In this study, although we were interested in detecting hybrid individuals (as we found with the figs), we specifically wanted to quantify genetic introgression between pollinator species. This is because introgression is an important evolutionary process, and while it has been detected in several fig systems, there is insufficient evidence that introgression also operates within fig–pollinator wasps. Thus, we prioritized sampling many UCE loci over many wasp individuals as sampling genome‐wide sequence data provides greater precision for estimating introgression (e.g., Hibbins & Hahn, 2022; Payseur & Rieseberg, 2016; Taylor & Larson, 2019). So, although we adopted a sampling approach that may miss rare or occasional F1 hybrid individuals, we should have good statistical power to detect any introgression having meaningful consequences for the evolution of pollinator species. Consistent with results from a different genus of Panamanian pollinator fig wasps (Pegoscapus, Satler et al., 2022), our deep genomic sampling coupled with rigorous statistical approaches failed to detect any introgression within this Tetrapus fig wasp community.

Although hybridization has long been considered to be more prevalent in plants than in animals (Stebbins, 1959), there is a growing appreciation of the role hybridization has played in the animal tree of life (Mallet et al., 2016; Taylor & Larson, 2019). This is becoming more apparent as access to genomic data sets and newly developed statistical methods have improved our ability to detect signals of hybridization and introgression in the genomes of animal lineages. While we suspect a combination of pre‐ and postzygotic mechanisms limit successful hybridization and introgression in fig wasps, it is necessary to test these hypotheses with genome‐scale data generated from communities of sympatric pollinator species. Observational experiments are also important in testing reproductive barriers between interacting species; however, successfully conducting such experiments with fig wasps requires overcoming significant challenges imposed by the closed structure of the syconium environment in which the heterospecific interactions of interest occur. Given the dearth of studies explicitly testing for hybridization and introgression in the pollinators—studies often focus on these processes in the host plants only—we hope future work will explicitly test for these processes in fig wasps. If the lack of hybridization and introgression demonstrated so far in fig wasps is the case in other fig systems, as we suspect, this will focus research on understanding the mechanisms promoting reproductive isolation in the pollinators in the face of frequent, and intimate, heterospecific interactions.

Machado et al. (2005) put forth the hypothesis that pollinator sharing and host switching have played prominent roles in generating the tremendous species diversity in the fig and wasp mutualism. In their model, genetically well‐defined pollinator species move among genetically less well‐defined fig species—either through pollinator sharing or host switching—and these opportunities for heterospecific pollination promote hybridization, introgression, and hybrid speciation between fig species. In this study, and others, F1 hybrid figs have been detected in nature. Because of the importance of fig floral volatiles for attracting host‐specific pollinators (Cornille et al., 2012; Grison‐Pigé et al., 2002; Hossaert‐McKey et al., 2010; Van Noort et al., 1989; Ware et al., 1993), if the admixed volatile phenotypes produced by F1 hybrids attract pollinators (bearing compatible pollen) that are able to enter, pollinate, and reproduce inside the syconium, then generations of advanced generation hybrids may be formed, potentially providing a mechanism for adaptive interspecific gene flow and, possibly, hybrid speciation and diversification in the figs. And if pollinator wasps become consistently attracted to the volatile blends produced by the hybrid individuals, then this provides a mechanism for pollinator sharing or host switching. In the case of a host shift, reproductive isolation and diversification would be promoted in the wasps. Given the observations made within this Panamanian free‐standing fig community, our results provide support for the Machado et al. (2005) model and suggest divergent evolutionary processes are responsible for generating diversification in the figs and their pollinator wasps.

5. CONCLUSIONS

Consistent with findings in other sections of Ficus, we demonstrate hybridization at shallow time scales between multiple fig species and introgression at deep time scales between two of the five Pharmacosycea fig species. By contrast, the six Tetrapus pollinating wasps in this community are genetically distinct, well‐defined species, and show no evidence of hybridization or introgression, consistent with findings from other fig and fig wasp systems. Although this obligate mutualism is maintained by tight ecological associations, processes affecting diversification differ between host and pollinator. Our findings are consistent with observations in other obligate pollination mutualisms and suggest that hybridization and introgression are processes affecting the evolution of the host plants, but not of their associated pollinators.

AUTHOR CONTRIBUTIONS

Jordan D. Satler: Conceptualization (equal); formal analysis (lead); investigation (lead); writing – original draft (lead); writing – review and editing (lead). Edward Allen Herre: Conceptualization (equal); funding acquisition (equal); resources (equal); writing – original draft (supporting); writing – review and editing (supporting). Tracy A. Heath: Conceptualization (equal); funding acquisition (equal); resources (equal); supervision (equal); writing – original draft (supporting). Carlos A. Machado: Conceptualization (equal); funding acquisition (supporting); resources (equal); writing – review and editing (supporting). Adalberto Gómez Zúñiga: Resources (equal). K. Charlotte Jandér: Conceptualization (equal); funding acquisition (supporting); resources (equal); writing – review and editing (supporting). Deren A. R. Eaton: Conceptualization (equal); resources (equal); writing – review and editing (supporting). John D. Nason: Conceptualization (equal); funding acquisition (equal); resources (equal); supervision (equal); writing – original draft (supporting); writing – review and editing (supporting).

FUNDING INFORMATION

This work was supported by a grant from the National Science Foundation [DEB‐1556853] to JDN, TAH, and AEH and was supported by Yale University (KCJ).

CONFLICT OF INTEREST

There is no conflict of interest to declare.

Supporting information

supplementary

ACKNOWLEDGMENTS

We thank Juan C Penagos Zuluaga, Brian Park, Finn Piatscheck, and Jose Lopez for extracting DNA from the host figs. We thank the Heath Lab for helpful comments and discussion that improved the manuscript. Computational resources were provided by ResearchIT and the College of Liberal Arts and Sciences at Iowa State University. The Smithsonian Tropical Research Institute provided the research facilities and intellectual community that helped make this study possible.

Satler, J. D. , Herre, E. A. , Heath, T. A. , Machado, C. A. , Gómez Zúñiga, A. , Jandér, K. C. , Eaton, D. A. R. , & Nason, J. D. (2023). Pollinator and host sharing lead to hybridization and introgression in Panamanian free‐standing figs, but not in their pollinator wasps. Ecology and Evolution, 13, e9673. 10.1002/ece3.9673

DATA AVAILABILITY STATEMENT

Raw sequence data are available from the NCBI Sequence Read Archive (SRA) under BioProject ID: PRJNA904825 (BioSample accessions: SAMN31644000–SAMN31644086). NCBI BioSample accession numbers are found in Table S1 for individual wasps and in Table S2 for individual figs. COI mtDNA pollinator barcode data are available at GenBank under accession numbers OP870658–OP870858. All data sets and custom scripts are available on Dryad (https://doi.org/10.5061/dryad.t1g1jwt60).

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Associated Data

This section collects any data citations, data availability statements, or supplementary materials included in this article.

Supplementary Materials

supplementary

Data Availability Statement

Raw sequence data are available from the NCBI Sequence Read Archive (SRA) under BioProject ID: PRJNA904825 (BioSample accessions: SAMN31644000–SAMN31644086). NCBI BioSample accession numbers are found in Table S1 for individual wasps and in Table S2 for individual figs. COI mtDNA pollinator barcode data are available at GenBank under accession numbers OP870658–OP870858. All data sets and custom scripts are available on Dryad (https://doi.org/10.5061/dryad.t1g1jwt60).


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