In March, 2010 Molecular Ecology published a special issue on ‘Next generation molecular ecology’. The papers published in that issue covered topics ranging from high-throughput sequencing of environmental DNA to genome-wide SNP detection and analysis of alternative splicing to comparative transcriptome sequencing. Clearly new sequencing technologies will ‘result in transformation of how we think about molecular ecology as a discipline’, as Tautz et al. (2010) argued in their introduction to that special issue. We see another example in this issue, where Gompert et al. (2010) use 454 pyrosequencing to gain new insight into the complex phylogeographic history of Lycaeides butterflies.
Earlier work in Lycaeides relied either on sequence data from just a few genomic regions, e.g. SSCP analysis of 236 bp from the AT-rich region of the mitochondrial genome (Nice et al. 2005) and DNA sequence analysis of 1000 bp from COI and COII (Gompert et al. 2008a) or on a modest number of fragment-based markers (Gompert et al. 2006a, 2008b). In contrast, Gompert et al. (2010) now identify nearly 1600 contigs with greater than 10 times coverage in all of the populations they study. Since the average length of these contigs is about ∼250 bp, the results they present are based on roughly 400 kb of DNA sequence [Gompert et al. (2010) report a mean contig length of 310 bp, but only contigs <700 bp were used in population comparison to avoid repetitive regions that may belong to non-orthologous genes]—two orders of magnitude greater than was available only 2 years ago. The result is very precise estimates both of the overall amount of genetic differentiation among populations and of the pairwise divergences among the sampled populations.
Gompert et al. (2010) use ΦST (Excoffier et al. 1992) to measure genetic differentiation among populations and find that 36% of variation is associated with among-population differences (95% CI: 0.34–0.38). ΦST can also be interpreted as a measure of the extent to which isolation among populations increases the coalescence time for genes drawn randomly from different populations relative to the coalescence time for genes within a single population (Slatkin 1991; Holsinger & Weir 2009). Thus, pairwise estimates of ΦST between populations provide insight into the degree to which populations are historically connected, although they cannot reveal the extent to which such connections reflect contemporary gene flow vs. recent common ancestry of populations that are now isolated (Felsenstein 1982).
In Lycaeides, a non-metric multidimensional scaling analysis of pairwise ΦST estimates reveals three broad geographic groupings (Fig. 1): (i) a western group corresponding roughly to what has been referred to as L. idas; (ii) a central group corresponding roughly to L. melissa; and (iii) an eastern group corresponding to L. melissa samuelis (the Karner blue). Estimates of ΦST from pairwise comparisons involving the Karner blue were larger than those involving other populations, generally greater than 0.3 and greater than 0.24 in every case. In contrast, the western and central groups of populations are more weakly differentiated. Some pairs of western populations and some pairs of central populations have greater pairwise ΦSTs than do other pairs in which one population belongs to the western group and the other belongs to the central group.
The geographic groups correspond with hypothesized glacial refugia and it is tempting to interpret the smaller amount of differentiation between western and central populations as a result of gene exchange associated with recent secondary contact. Indeed, Gompert et al. (2006b, 2008b) point out that other data are consistent with this hypothesis. But central (L. melissa) and eastern (Karner blue) populations are geographically adjacent and mitochondrial introgression has been detected between the Karner blue and populations of L. melissa (Gompert et al. 2006b, 2008b). Thus, the larger pairwise differences for comparisons involving the Karner blue might simply reflect smaller population sizes in the Karner blue (Weir 1996; Hedrick 1999; Holsinger& Weir 2009). The Karner blue was listed as an endangered species under the US Endangered Species Act in 1992 and its populations are restricted to remnant savannas and barrens, primarily in Wisconsin and Michigan (Wooley 2003).
The mean estimates of population differentiation just summarized provide a great deal of insight, but they also mask many differences among loci. Using a hierarchical Bayesian model similar to the ones introduced by Beaumont & Balding (2004) and Guo et al. (2009), Gompert et al. (2010) estimate that the standard deviation of ΦST across loci was 0.40 (95% CI: 0.37–0.43), and locus-specific estimates of ΦST vary from as little as –0.5 to nearly 1.0 (Gompert et al. 2010; Fig. 3C). This variation reflects real variation in the amount of differentiation at each locus, not statistical uncertainty associated with the genome-wide estimate of ΦST. That real variation undoubtedly reflects to some degree the enormous variability inherent in the process of genetic drift, but some of it is also likely to reflect the effects of natural selection at loci subject to different patterns of natural selection. Those effects may either be associated with loci included in the sample or with loci that are closely linked. One of the advantages of the Bayesian model Gompert et al. (2010) use is that it can be extended to identify statistical ‘outliers’ where the amount of among-population differentiation may reflect the effects of natural selection (Beaumont & Balding 2004; Guo et al. 2009).
In addition to illustrating how next generation sequencing may transform studies of population genetics and phylogeography, the Lycaeides data also illustrate some of the challenges that lie ahead. Take for example the ‘simple’ question: which of the populations included in this sample is the most genetically diverse? Gompert et al. (2010) point out that the proportion of variable sites detected in contigs is positively correlated with the number of reads (r = 0.44 with indels, r = 0.48 without indels). Thus, simply calculating the number of variable sites or expected heterozygosity in the sample is not enough. Investigators wishing to compare levels of diversity among populations will either have to use rarefaction methods like those in (Mousadik & Petit 1996) or they will have to estimate θ = 4Neμ using an approach like the composite likelihood method introduced in Hellmann et al. (2008). Moreover, as Hellman et al. (2008) illustrate, with whole-genome shotgun sequencing it becomes possible to compare levels of diversity in different parts of the genome. In organisms lacking a reference genome, like Lycaeides, such intragenomic comparisons will necessarily be limited to comparing levels of diversity among isolated contigs. Nonetheless, such comparisons will provide another way in which to identify regions of the genome subject to different patterns of natural selection.
Nearly 40 years ago the field of evolutionary genetics was transformed when Harris (1966), Hubby & Lewontin (1966) and Lewontin & Hubby (1966) introduced protein electrophoresis to the field. We stand on the threshold of a similar transformation today, and studies like the analysis of Lycaeides presented by Gompert et al. (2010) give us a glimpse of the insights that are sure to follow.