The mechanisms shaping island biotas are not yet well understood mostly because of a lack of studies comparing eco-evolutionary fingerprints over entire taxonomic groups. Here, we linked community structure (richness, frequency and nestedness) and genetic differentiation (based on mitochondrial DNA) in order to compare insular butterfly communities occurring over a key intercontinental area in the Mediterranean (Italy-Sicily-Maghreb). We found that community characteristics and genetic structure were influenced by a combination of contemporary and historical factors, and among the latter, connection during the Pleistocene had an important impact. We showed that species can be divided into two groups with radically different properties: widespread taxa had high dispersal capacity, a nested pattern of occurrence, and displayed little genetic structure, while rare species were mainly characterized by low dispersal, high turnover and genetically differentiated populations. These results offer an unprecedented view of the distinctive butterfly communities and of the main processes determining them on each studied island and highlight the importance of assessing the phylogeographic value of populations for conservation.
Island communities share several features: the number of species is lower than on similarly sized mainland areas (impoverishment), they host a disproportionate fraction of non-predatory and highly dispersive species (disharmony) and they are characterized by a high fraction of endemic elements1. In the last decades it has been largely recognized that these features are shaped by colonization and extinction events but also by the long-term persistence of populations, resulting in relictuality and endemicity1,2,3. In turn, these processes depend on a large number of factors related to both species and island characteristics, as well as to stochastic events1,4. As a result, no island populations and communities are identical and they have been regarded as “individuals”5. Hence, recognizing the main drivers behind the formation of each community and developing specific conservation plans require in-depth comparative analyses linking community and genetic approaches6,7,8.
An important property of island communities is that their structure tends to be nested, with some species occurring on most islands, and others occurring on fewer islands, usually the largest and least isolated9,10. The existence of nested patterns has important implications for conservation; when communities are highly nested, conservation decisions are simplified and the usual strategy is to concentrate efforts on the most diverse communities1. After a series of studies suggested that nested structures universally occur within different taxa and island systems11, the recent introduction of strict null models revealed that significantly nested patterns are less common than previously hypothesized12. There is also a debate6,13 as to whether species occurrence in island communities is mostly determined by their frequency in neighbouring source areas, as postulated by neutral theories2,14, or whether competition and interaction between species traits and island characteristics (mostly mediated by differences in dispersal tendency among species) play a primary role3,10,15.
Genetic variation provides fundamental information to understand the historical and ecological dynamics that shaped island populations and communities6,16. Past connections or long-term isolation are well-known determinants of phylogeographic patterns, but they exert variable effects on different species, with highly migratory species expected to show the least geographic variation due to frequent gene flow16,17,18. However, the assumption that species lacking spatial genetic differentiation are the most vagile and widespread has rarely been tested6,16,19.
Following these premises, it is not surprising that, although numerous studies exposed the role of complex phenomena in producing faunistic20,21 and genetic community structures for selected insular taxa19,22, comprehensive studies aiming to disentangle large arrays of ecological-historical and deterministic-stochastic factors over large taxonomic groups are uncommon8,16,17. In this study, we examined butterfly communities occurring on the circum-Sicilian islands and compared them with populations from the southern Italian Peninsula, Sicily and north Africa. Sicily and the surrounding islands represent a biogeographic crossroad with high species richness and contrasting biodiversity23,24,25. These islands have different geological histories and locations with respect to the two main faunistic sources (southern Europe and north Africa) and possess different environmental settings, while the well-known taxonomy and distribution of the butterflies occurring in this region make them an excellent model system. However, the sparse information about their genetic structure has impeded the link between community composition and patterns of genetic differentiation. In this study we: i) model species richness over the western Mediterranean islands, ii) examine the pattern of nestedness in the study area, iii) analyse the relative importance of species dispersal tendency and frequency at source in determining their frequency on islands, iv) we sequenced the COI gene to assess the genetic differentiation patterns for populations of 29 species and test for a possible correlation between dispersal tendency and regional genetic variation, v) document the overall genetic differentiation pattern for north Africa, circum-Sicilian islands, Sicily, and the Italian Peninsula, and vi) categorize the species based on their island occupancy and genetic structure. This integrative approach aids the recognition of the multiple processes generating species assemblages for an entire and diverse superfamily and provides the information needed to prioritize conservation decisions in a key biogeographical contact zone.
Determinants for island species richness
The AIC-based Generalized Linear Model (GLM) for the richness of Western Mediterranean islands on the basis of ecological factors, returned a model with four variables: island area (IA), isolation (IS), source richness (SR) and maximum elevation (EL). Isolation represented the largest part (26.1%) of the total variance explained by the model (67.8%) (Supplementary Table S3). The Maltese islands, Lampedusa, Lipari and Vulcano were richer in species than expected (Supplementary Fig. S1a), while Pantelleria, Linosa, Stromboli and Marettimo had fewer species than expected. In the second GLM (including the Pleistocene land connections (PC) as a variable) a six variable model best fitted the data (Supplementary Table S4), adding mean island precipitation (PT) and PC to the previous model. In order to make this model directly comparable with the first one, we excluded PT (results including this variable are shown in Supplementary Table S4). This model increased the explained variance to 73.2% with PC having the lowest lmg value (Table 1). The difference in richness residuals between the model without the PC and the full model can provide an estimation of the number of species that colonized the islands during the Last Glacial Maximum (LGM), due to land-bridge connections, and survived until present (Table 2).
Various null models provided different evidence for the existence of a significantly nested pattern of the butterfly communities on the 11 studied islands. The observed nestedness metric based on overlap and decreasing fill (NODF) of the entire packed matrix (Fig. 1) was significantly higher than the mean NODF obtained with the equiprobable rows and columns (EE) and proportional rows and columns total (CE) null models (Table 3). However, the mean NODF for the fixed rows and columns (FF) null model was significantly higher than the observed value, revealing an anti-nested pattern (Table 3). After dividing the matrix into two sub-matrices corresponding to widespread and rare species (occurring in more and less than half of the islands, respectively), widespread species showed a nested pattern for the EE and CE null models, while rare species showed a significantly anti-nested pattern with the FF model (Table 3). In particular, species occurring on less than four islands showed a highly chequered distribution (Fig. 1). Accordingly, when all species were considered, nestedness and turnover components had similar contributions in determining faunistic dissimilarities with a ratio between nestedness and Sørensen (nest/sor) indexes of 0.588. When divided into sub-matrices, the widespread species showed a predominance of the nestedness component (nest/sor = 0.814), and the rare ones a predominance of species replacement (nest/sor = 0.232). A multiple regression showed that species frequency on islands was significantly associated with both frequency at source (n = 32, Est. = 0.037, t = 3.88, P < 0.001, Fig. 2a, Supplementary Fig. S2a) and with dispersal tendency (n = 32, Est. = 4.607, t = 2.84, P = 0.008, Fig. 2b, Supplementary Fig. S2b). The partitioning of variance revealed that dispersal tendency explained a lower fraction of variation than frequency at source (16.4% for dispersal tendency and 29.5% for frequency at source).
We used 1044 COI sequences, of which 878 have been specifically sequenced for this study and the rest obtained from GenBank. We provide all sequences as a fasta file in the Supplementary Information. Some species showed very little genetic diversification with only one or a few closely related haplotypes (e.g. C. croceus, Gonepteryx cleopatra, Pseudophilotes baton, Gegenes nostrodamus; Supplementary Note). Other highly mobile species were more variable, but the haplotypes did not show any geographic pattern (e.g. Pieris rapae and Vanessa cardui; Fig. 3). Several species were genetically differentiated between north Africa and Europe (examples provided in Fig. 3, the remaining species are available in the Supplementary Note). Lineages of some species such as Papilio machaon, Lycaena phlaeas, Lasiommata megera (Fig. 3), Carcharodus alceae, Aricia spp. and Polyommatus celina displayed chequered distributions, even between the two sides of the narrow Messina strait (Supplementary Note). Other species like Hipparchia spp., Maniola jurtina and Pyronia cecilia had distinct lineages that in some areas occur in sympatry (Fig. 3). Dst and Gst values for each species are reported in Supplementary Table S1. The Principal Coordinate Analysis (PCoA) based on the mean pairwise Gst values among areas showed that Europe and north Africa were genetically well-differentiated. Ustica, the Aeolian, the Aegadian and Maltese islands were genetically similar to Sicily-Italian Peninsula, while Lampedusa was more similar to north Africa. Pantelleria and Marettimo had a genetic signal intermediate between the two continents (Fig. 4a,b, Supplementary Note). When the mean genetic diversification among populations, measured as Dst, for the species occupying each area was plotted on the z-axis, islands with intermediate geographic positions were shown to harbour species with low population genetic differentiation (Fig. 4a).
Correlations between species occurrence and genetic variation
As expected, population genetic differentiation of species (measured with Dst) was significantly anti-correlated with dispersal tendency (Spearman rho = −0.409, P = 0.028, Fig. 3c). However, Dst was not significantly anti-correlated with species occurrence on islands (Spearman rho = −0.051, P = 0.791). The graph representing occurrence on islands (x-axis) and population genetic differentiation (Dst, y-axis) showed a non-random distribution of the species occurring in circum-Sicilian islands: the sector of widespread and genetically diversified species was significantly empty (Fig. 5a). When communities were examined individually, the faunas of Stromboli, Lipari, Salina, Marettimo, and Linosa showed a significant negative correlation between Dst and frequency (Supplementary Table S5). Moreover, the widespread and genetically undiversified species were always more common than expected in a random distribution. On all islands except for Lampedusa, Ustica and Vulcano there was a deficit of rare, genetically homogeneous species (Supplemetary Table S5 and Fig. 5). The Aeolian Islands, together with Levanzo and the Maltese Islands did not show a significant deficit of rare and genetically diverse species.
Differentiation of populations at an intercontinental crossroad
The integration of faunistic and genetic differentiation information ultimately allowed the recognition of the main processes shaping island communities in a key biogeographic region. Similar comprehensive assessments of island communities are scarce, especially due to the difficulty of acquiring high quality data at both faunistic and genetic levels for large groups of organisms8,22,26,27. The evaluation of the contribution of singular factors in characterizing island diversity facilitated the identification of species that deserve conservation consideration on individual islands. The composition of butterfly communities and their genetic structure were shaped by neutral (frequency at source) and non-neutral (differences in dispersal tendency among species, interactions generating chequered patterns) determinants. In particular, frequency at source had a strong contribution in determining the occurrence of species on islands, as expected according to a neutral hypothesis, but species dispersal tendency also played an important role and many sedentary species were rare on islands despite their ubiquitous presence on mainland and Sicily (M. jurtina, C. pamphilus, P. aegeria, P. cecilia and Aricia spp.
One of the main findings of this study, stemming from the community and genetic data, is that even in a relatively restricted area, island populations have very different histories and are subjected to different re-colonization probabilities following local extinctions. In contrast to very isolated oceanic islands, the Western Mediterranean islands maintained relatively strong biotic relationships with the neighbouring mainland, especially for organisms with high dispersal ability, such as butterflies24,28. Accordingly, our analyses of faunistic diversity and population genetic differentiation supported that contemporary island-source dynamics, filtered by the main ecological characteristics of islands (predominantly area and isolation), are the main determinants shaping butterfly communities in the circum-Sicilian islands. Accordingly, a direct comparison between dispersal tendency and genetic variation resulted in a significant negative correlation (Fig. 2c), and about half of the species in these communities are taxa with high dispersal ability (P. rapae, P. brassicae, C. croceus, Leptotes pirithous, Lampides boeticus, Vanessa atalanta and V. cardui)29 and/or with low genetic diversification (Fig. 5). Island populations of these species likely include both local residents and recent immigrants30. Besides these widespread species, island communities include rare species (i.e. species that occur on only few islands), most of which showed considerable population differentiation over the study area. Out of 32 species, 10 occur only on one or two islands and 18 on less than half of them. Although their overall number is similar to that of the widespread species, they represent a relatively small part of each island’s diversity (on average 27.8%). These rare species did not show a nested pattern and generated inter-island faunistic dissimilarity mostly because of turnover.
The non-nested pattern of rare species revealed that basic rules of ecological filtering and colonization-extinction dynamics were not sufficient to explain occupancy patterns and that a larger array of determinants is involved, including: i) dispersal from local source populations (e.g. P. baton to Aeolian Islands, widespread north African species to Lampedusa), ii) interaction with sister species and lineages (as revealed by mutual exclusion, see below), iii) human impact and iv) Pleistocene connections. We confirmed the existence of marked differences in terms of butterfly diversity between north Africa and southern Europe24,25,31,32, and individual islands showed different degrees of similarity to the two sources, evidently based on their relative distance and paleogeographic connections. The richness analysis attributed to Malta, Levanzo and Lampedusa a set of species that supposedly colonized them during the LGM, likely through the land-bridges that connected these islands to mainland at that moment. This hypothesis is further supported by the finding that all the rare species with regional genetic diversification occurring on these islands are genetically very similar to the populations inhabiting the areas to which these islands were connected during the LGM.
Another important finding is the pervasive occurrence of chequered distributions31,32. This is evident not only for certain pairs of cryptic species (Pontia edusa-P. daplidice and P. icarus-P. celina), but also at the intraspecific level. Many species displaying over 1% intraspecific genetic divergence (C. alceae, P. machaon, L. phlaeas, Aricia spp., L. megera, P. aegeria, C. pamphilus) show chequered distributions not only across the wide channel separating Sicily from north Africa, but also across the narrow (3 km) Messina strait between Sicily and southern Italy. Chequered distributions challenge the hypothesis of neutrality for species and lineages, but the relative importance of the potential mechanisms involved is still unknown. A combination of factors, such as reproductive interference, reduced dispersal, density-dependent phenomena and differences in climatic niches is probably at the basis of the observed patterns32.
Island communities and the need for specifically tailored conservation measures
All the islands investigated host a significantly high fraction of dispersive species having widespread distributions in the study area and displaying low levels of genetic differentiation. Their long-term presence on islands is expected because any local extinction event would soon be followed by recolonization involving a population genetically similar to the original one. This is obvious for those species that reach Europe every spring and are unable to overwinter there30 [for V. cardui], but also applies to many others with permanent populations on islands and with high dispersal capacities (e.g. P. rapae, P. brassicae, C. croceus, L. pirithous, L. boeticus, V. atalanta). Any actions aiming to preserve the local island populations of these widespread species should be cautiously considered since it could represent a waste of economic resources in detriment of other, more important, conservation endeavours. On the contrary, rare species should be carefully monitored and conservation efforts immediately directed towards declining populations33. Their non-nested distribution patterns, with a prevalence of unpredictable species replacements between islands, and their regionally structured genetic diversity, are strong indications that these island populations have unique histories1,6,12. Moreover, the rare species generated the faunistic identity and the particular genetic structure of each island community, thus providing an unbalanced contribution to diversity31.
Hipparchia leighebi is a taxon endemic to the Aeolian islands with still debated status. Our results show that it represents at least a slightly diverged (0.6%) COI lineage endemic to this group of islands, where no other lineage of Hipparchia was detected. A COI haplotype of M. jurtina was the only one detected on Vulcano and the most common on Lipari, where it coexists with typical Sicilian haplotypes, and was not found elsewhere34. Similarly, Lampedusa hosts a substantially diverged lineage (0.8%) of the north African clade of P. machaon (Fig. 3, Supplementary Note). If population declines are detected for these entities, they should be considered as priority taxa for conservation in the islands where they occur. Many single individuals with unique haplotypes on islands have also been found, but their uniqueness probably represents the effect of random sampling in species with high genetic variation. This was the case for a single specimen of L. boeticus collected on Gozo island, having a highly diverged COI sequence close to a genetic lineage previously detected in Madagascar (Supplementary Note).
Priority for conservation should also be given to populations that apparently represent glacial relicts and that, in the current ecological settings, would unlikely recolonize a specific island. In fact, these species are the most threatened on the studied islands (Supplementary Note), possibly because they lack metapopulation dynamics that maintain population numbers (rescue effect) and are subjected to inbreeding depression. The most striking example is that of the Maltese islands, where L. phlaeas and A. agestis are believed to be extinct, while M. jurtina, C. pamphilus and P. aegeria are rapidly declining due to human impact35, [Paul Sammut personal observations], therefore these populations require immediate conservation actions to preserve the uniqueness of the Maltese butterfly fauna.
Levanzo and Lampedusa also had connections with Sicily and Tunisia, respectively, during the LGM. Due to the proximity to Sicily, most butterflies on Levanzo are probably part of a metapopulation and no positive richness residuals were found for this island in the GLM including contemporary determinants of richness (Fig. 1a). An exception could be C. pamphilus, which was represented on Levanzo by three slightly differentiated (single mutation) endemic haplotypes. On Lampedusa, all the rare species are highly dispersive and widely distributed in north Africa but not in Europe, probably because of climatic restrictions or species interactions leading to mutual exclusion31,32. However, the substantially divergent haplotype of P. machaon only found on this island should be considered as a priority for local conservation actions.
Chequered distributions should also be taken into consideration for conservation decisions. The possibility that density-dependent and founder-takes-all mechanisms are at the basis of the maintenance of these patterns36,37 suggests that the populations existing in an area/island represent the main barrier to the colonization by other lineages, which would change the original genetic structure, probably established after a series of unrepeatable historical events23. For example, the fauna of Pantelleria is mostly composed of widespread and undiversified species, but three of them (P. celina, L. phlaeas, L. megera) have different lineages in Sicily and Tunisia. Interestingly, all three species are represented on Pantelleria by typical north African populations, although the island was closer to Sicily during the glaciations. The similarity to Tunisia for these three taxa is the most important characteristic of this island’s butterfly fauna, but its cause is unknown. The extinction of these populations may result in recolonization from Sicily, thus erasing a key biogeographic signal on Pantelleria.
Our approach provides an example of how a series of comprehensive analyses on a wide area and large taxonomic group can test rarely assessed biogeographic principles like the links of genetic structure with dispersal tendency and frequency on islands, or the relative effects of contemporary and historical determinants on island populations. The challenge of integrating community ecology and phylogeographic approaches can also provide the baseline information for developing conservation strategies that maximize biodiversity at both the species and intraspecific genetic levels.
Study area and data collection
We analysed the butterfly faunas of 11 circum-Sicilian islands (Lampedusa, Levanzo, Linosa, Lipari, Maltese islands, Marettimo, Pantelleria, Salina, Stromboli, Ustica, Vulcano), Sicily itself and nearby mainland locations in southern Italy (Calabria), Tunisia and Algeria. Presence data were gathered from several post 1980 literature sources and from field surveys carried out by the authors between 1999 and 2015. Specimens used for genetic analyses were collected outside protected areas and were deposited at the Institute of Evolutionary Biology (CSIC-UPF), Barcelona, Spain.
Determinants for island species richness
To evaluate the influence of different factors on species richness for the studied islands, we used Generalized Linear Models (GLM) with Akaike Information Criterion (AIC). We also assessed the relative importance of potentially correlated variables using hierarchical partitioning of variance, employing the lmg metric implemented in the “relaimpo” R Package. To place the richness of the study islands in a broader framework, we used presence data on the butterfly fauna from all the western Mediterranean islands24 (excluding Sicily, Sardinia and Corsica because their large size would provide an unbalanced contribution to the analysis). Islands were included in the study if at least four out of five migrant species (P. brassicae, P. rapae, C. croceus, V. atalanta and V. cardui) were recorded there. These species are conspicuous and widespread throughout Europe and north Africa, and their records establish a minimal surveying standard24.
In the GLM, species richness was modelled against the following biotic, geographic and climatic predictors: i) mean annual temperatures (MT), ii) annual precipitation (AP), iii) island area (IA), iv) maximum elevation of island (EL), v) isolation (IS), vi) source richness (SR) and vii) the occurrence of a Pleistocene connection (PC, factor variable). MT and AP were obtained by computing the mean values of the cells corresponding to islands in Bio1 and Bio12 layers from Bioclim (http://www.worldclim.org). For each island, the faunistic source was identified as the nearest 50×50 km area, either mainland (southern Europe or north Africa), large island (Sicily, Sardinia, Corsica), or an island at least ten times larger than the target one. We calculated SR as the number of species reported from the source area and IS as the minimum distance between the target island and its faunistic source. To linearize the relationships, we log transformed richness, area, isolation and source richness. We computed a first GLM using only contemporary variables and a second GLM in which we included the PC. We compared the AIC, explanatory power and residuals of the selected variables between the two models.
We estimated the degree of nestedness of butterfly communities in circum-Sicilian islands by applying the widely accepted NODF metric9. A recent study has shown that the detected degree of nestedness depends heavily on the selected null models due to their different tendency to preserve the features of the original matrix12. To assess the significance of the observed NODF, we used the NeD program38 and computed the z-values using 999 null matrices, built by applying a series of different models (equiprobable rows and columns, EE; proportional rows and columns total, CE; and fixed rows and columns, FF)12.
Prior studies have divided species into “core” and “satellite” species39 in which “core” species are those occurring on more than half of the islands, and “satellite” those present on fewer islands. We used the same approach and divided the 27 species occurring on the 11 studied islands into “widespread” (those occurring on six or more of the islands) and “rare” (those found on no more than five islands). We also separately analysed the degree of nestedness of the two subsets.
The overall faunistic dissimilarities among areas can be partitioned between a component generated by nestedness and one determined by species replacement (turnover)40. We calculated the relative contribution of nestedness and turnover as the mean value of the ratio between the faunistic dissimilarities obtained by nestedness and Sørensen indexes (see Supplementary Information and Supplementary Data)41. This ratio has been computed for all species, as well as for the rare and widespread species groups, separately. We tested for the effect of species dispersal tendency and their frequency at source on their occupancy on islands. Measurements of the dispersal tendency in butterflies are complex and, in previous studies, have been mostly based on the agreement among subjective evaluations made by experts, and less commonly by using objective species traits. Here we combined the indexes provided by four studies42,43,44,45 by standardizing their range between 0 (low dispersal) and 1 (high dispersal) and computed, for each species, an average dispersal tendency based on the available measurements. To estimate the frequency at source we counted the number of cells of 0.1 × 0.1 degrees between 34° and 40° latitude and 7° and 18° longitude, where each of the 32 investigated species has been reported. As standardized sources we used “CKmap2000”, an online checklist of the Italian butterfly fauna46, and the database of the Butterfly Diversity and Evolution Lab at The Institute of Evolutionary Biology (CSIC-UPF), Spain. The frequency of each species on islands was regressed against dispersal tendency and frequency at source, and the relative importance of these factors was tested by hierarchical partitioning of variance.
Genetic analyses and identification of study units
Using standard sequencing procedures (see Supplementary Information) we obtained cytochrome c oxidase subunit I (COI) sequences for 1044 specimens (Supplementary Table S2) from the study islands and from five surrounding areas: southern Italy (Calabria), eastern Sicily (>14° longitude), western Sicily (<14° longitude), Tunisia and Algeria. We considered only the islands for which we had available more than 80% of the reported fauna. This led to the exclusion of Linosa and left ten islands and a total of 15 areas to be analysed.
The butterfly species currently recognized by taxonomists show different levels of intraspecific genetic divergence and they can have an unbalanced contribution to the overall biogeographic pattern31,47. To reduce this bias, we identified as units the groups of individuals having COI p-distances less than 3%, a measure that, in Lepidoptera, was reported to separate more than 90% of recognized sister species48. By applying this threshold we identified 29 units (termed species) closely matching the taxonomy proposed by Fauna Europaea (www.faunaeur.org). The list of species is provided in Supplementary Table S1.
Overall population differentiation pattern
To examine patterns of genetic differentiation for each species in the study area we constructed haplotype networks with the TCS Network method in PopART49 (http://popart.otago.ac.nz). We calculated the genetic uncorrected p-distances among all sequenced specimens for each species, as well as two measures for population differentiation: Dst and Gst50:
where Ht represents the average intraspecific p-distances for all specimens of a given species, and Hs is the average of the intra-population p-distances. Thus, Dst represents average genetic differentiation among populations in p-distance units. The second measure (Gst) is a standardized index defined as:
representing which fraction of the total genetic differentiation is encompassed by differentiation among populations50. This index ranges from negative values to 1 (complete differentiation). Negative values (intra-area differentiation higher than inter-area differentiation) can have different subtle meanings, but they are mostly generated as a bias due to relatively small sample sizes; usually they are set to zero51 and we used this solution for two cases in our study. We also calculated pairwise Gst among pairs of populations using the following formula:
representing which fraction of the overall genetic diversity (Ht) is expressed by inter-population diversification (Dsti,j) between a given pair of areas (i and j).
By using the Gst pairwise matrices for each species, we calculated the mean of the available values of the corresponding cells to produce the final mean Gst matrix, representing the degree of genetic differentiation among areas based on all species. A PCoA was applied to this matrix to obtain the overall genetic pattern among areas. Subsequently, we aligned this configuration with the geographic location of the areas by using the “procrustes” analysis from the “vegan” R package (Supplementary Data). To visualize the pattern of similarity among islands over geographic space, we projected the final configuration of average Gst values among areas in the RGB space24,52 using the R package “recluster”. The colour resemblance of the resulting dots is directly proportional to the genetic differentiation among the communities. These dots were then plotted on a map, where we outlined the −100 m depth contour as a reliable reconstruction of land during the LGM20.
Islands located between two genetically contrasting sources can show intermediate communities if: i) islands host species characterized by genetic variation and individuals belong to different sources, or ii) islands host only a reduced fraction of species characterized by genetic differentiation, and therefore look equally similar to both sources. To visualize the pattern of genetic similarity and to compare the degree of genetic differentiation among areas we computed for each area the mean Dst as the mean of all the Dst values for the species available for each area. We then plotted the relationship between the PCoA configuration and the mean Dst of each area in 3D. If the first hypothesis is met, we expect that intermediate islands will have similar mean Dst to other islands, while if the second is true we expect that intermediate islands will have lower mean Dst values.
Analysis of genetic differentiation among populations
We tested for correlation between Dst and both dispersal tendency and island occupancy (number of studied islands occupied by each species) using the non-parametric Spearman correlation rank test. We also square root transformed the Dst values to improve normality and divided the bivariate relationship between occupancy and Dst into four quadrants, and considered the species either as ‘widespread’ or ‘rare’ and the absolute genetic variation as low (<half) or high (>half) of the maximum square root transformed Dst. The number of species falling into each quadrant was scored. Subsequently, 999 null matrices were constructed by attributing to each species random values of occupancy and Dst. For each square, we assessed the frequency for which the observed number of species was lower than in random configurations. Values <0.050 were considered as significantly empty quadrants, and values >0.950 as significantly full quadrants.
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This research was supported by the Spanish Ministerio de Economía y Competitividad (Project CGL2013-48277-P) and from the European Union’s Seventh Framework programme for research and innovation under the Marie Skłodowska-Curie grant agreement No 609402 - 2020 researchers: Train to Move (T2M) postdoctoral fellowship to R. Vodă, and by the projects “Barcoding Italian Butterflies” and “Barcoding Butterflies of the Tuscan Archipelago National Park.” V. Dincă was supported by a Marie Curie International Outgoing Fellowship within the 7th European Community Framework Programme (project no. 625997). L. Dapporto was supported by European Union’s Horizon 2020 research and innovation programme under the Marie Sklodowska-Curie grant (project no. 658844 Eco-PhyloGeo). We thank Axel Hausmann, Anthony Seguna and Michael Seizmair for providing samples and Alessandro Cini, David Baracchi and Giuseppe Mazza for their help in field collections.
The authors declare no competing financial interests.
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Vodă, R., Dapporto, L., Dincă, V. et al. Historical and contemporary factors generate unique butterfly communities on islands. Sci Rep 6, 28828 (2016). https://doi.org/10.1038/srep28828
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