Abstract

Two genetically distinct lineages of European green crabs (Carcinus maenas) were independently introduced to eastern North America, the first in the early 19th century and the second in the late 20th century. These lineages first came into secondary contact in southeastern Nova Scotia, Canada (NS), where they hybridized, producing latitudinal genetic clines. Previous studies have documented a persistent southward shift in the clines of different marker types, consistent with existing dispersal and recruitment pathways. We evaluated current clinal structure by quantifying the distribution of lineages and fine‐scale hybridization patterns across the eastern North American range (25 locations, ~39 to 49°N) using informative single nucleotide polymorphisms (SNPs; n = 96). In addition, temporal changes in the genetic clines were evaluated using mitochondrial DNA and microsatellite loci (n = 9–11) over a 15‐year period (2000–2015). Clinal structure was consistent with prior work demonstrating the existence of both northern and southern lineages with a hybrid zone occurring between southern New Brunswick (NB) and southern NS. Extensive later generation hybrids were detected in this region and in southeastern Newfoundland. Temporal genetic analysis confirmed the southward progression of clines over time; however, the rate of this progression was slower than predicted by forecasting models, and current clines for all marker types deviated significantly from these predictions. Our results suggest that neutral and selective processes contribute to cline dynamics, and ultimately, highlight how selection, hybridization, and dispersal can collectively influence invasion success.

Highlights

  • Genetic clines have been formed when invasion fronts from two separate introductions from previously allopatric lineages come into secondary contact in the invaded range, and such a scenario has occurred in the invasive European green crab (Carcinus maenas) (Darling, Tsai, Blakeslee, & Roman, 2014; Pringle et al, 2011; Roman, 2006)

  • We take advantage of the strong genetic differentiation between lineages from the past and recent introductions, and the interaction of invasion fronts, as a platform to examine dynamics in the hybrid zone and study the temporal changes in the genetic clines. Such investigations are possible because the clinal genetic structure of C. maenas in eastern North America has been well characterized in previous studies (Darling et al, 2014; Jeffery et al, 2017a; Pringle et al, 2011), allowing for a historical perspective and the ability to investigate temporal dynamics

  • We modelled the genetic clines of C. maenas over multiple time points since 2000 using the mitochondrial cytochrome c oxidase subunit I (COI) gene and microsatellite markers

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Summary

| INTRODUCTION

Marine genetic studies increasingly demonstrate patterns of population structure over much smaller scales than might be predicted by dispersal potential (Sa-­Pinto, Baird, Pinho, Alexandrino, & Branco, 2010; Selkoe, Henzler, & Gaines, 2008; Selkoe et al, 2016; Väinölä & Hvilsom, 1991), including the existence of genetic clines across tens to hundreds of kilometres (Bradbury et al, 2010; Hare & Avise, 2011; Pringle, Blakeslee, Byers, & Roman, 2011; Sotka, Wares, Barth, Grosberg, & Palumbi, 2004). We take advantage of the strong genetic differentiation between lineages from the past and recent introductions, and the interaction of invasion fronts, as a platform to examine dynamics in the hybrid zone and study the temporal changes in the genetic clines Such investigations are possible because the clinal genetic structure of C. maenas in eastern North America has been well characterized in previous studies (Darling et al, 2014; Jeffery et al, 2017a; Pringle et al, 2011), allowing for a historical perspective and the ability to investigate temporal dynamics. Our ability to determine the current distribution and movement patterns of lineages over the last decade is critical to the ongoing management and monitoring of this invasive species as lineages could have differential impacts on ecosystems given differences found in physiology, reproduction and competitive behaviour of crabs from different regions (Best, McKenzie, & Couturier, 2017; Rossong et al, 2011; Tepolt & Palumbi, 2015; Tepolt & Somero, 2014)

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CONFLICT OF INTEREST
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