Abstract

The establishment and spread of aquatic invasive species are ecologically and economically harmful and a source of conservation concern internationally. Processes of species invasion have traditionally been inferred from observational data of species presence/absence and relative abundance. However, genetic‐based approaches can provide valuable sources of inference. Restriction site‐associated DNA sequencing was used to identify and genotype single nucleotide polymorphism (SNP) loci for Round Gobies (Neogobius melanostomus) (N = 440) from 18 sampling locations in the Great Lakes and in three Michigan, USA, drainages (Flint, Au Sable, and Cheboygan River basins). Sampled rivers differed in size, accessibility, and physical characteristics including man‐made dispersal barriers. Population levels of genetic diversity and interpopulation variance in SNP allele frequency were used in coalescence‐based approximate Bayesian computation (ABC) to statistically compare models representing competing hypotheses regarding source population, postcolonization dispersal, and demographic history in the Great Lakes and inland waters. Results indicate different patterns of colonization across the three drainages. In the Flint River, models indicate a strong population bottleneck (<3% of contemporary effective population size) and a single founding event from Saginaw Bay led to the colonization of inland river segments. In the Au Sable River, analyses could not distinguish potential source populations, but supported models indicated multiple introductions from one source population. In the Cheboygan River, supported models indicated that colonization likely proceeded from east (Lake Huron source) to west among inland locales sampled in the system. Despite the recent occupancy of Great Lakes and inland habitats, large numbers of loci analyzed in an ABC framework enable statistically supported identification of source populations and reconstruction of the direction of inland spread and demographic history following establishment. Information from analyses can direct management actions to limit the spread of invasive species from identified sources and most probable vectors into additional inland aquatic habitats.

Highlights

  • The establishment and spread of invasive species have caused devastating trophic cascades (Strayer, 2010) that have reduced the abundance (Gallardo, Clavero, Sánchez, & Vilà, 2016) and diversity (Hejda, Pyšek, & Jarošík, 2009) of native species

  • Secondary inland spread dynamics into the Flint River system clearly differed from invasions into the Au Sable and Cheboygan Rivers

  • The Flint River invasion appears to have involved a more severe bottleneck associated with colonization compared to the Au Sable and Cheboygan Rivers (~7%)

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Summary

Introduction

The establishment and spread of invasive species have caused devastating trophic cascades (Strayer, 2010) that have reduced the abundance (Gallardo, Clavero, Sánchez, & Vilà, 2016) and diversity (Hejda, Pyšek, & Jarošík, 2009) of native species. Given the deleterious effects associated with biological invasions, conservation agencies have emphasized prevention of human‐assisted (Lockwood, Cassey, & Blackburn, 2005) introductions of invasive species from native sources along with efforts to limit spread of invasive species in habitats that have experienced introductions These actions are widely believed to be the most cost‐effective control strategies (Mack et al, 2000). Unambiguous identification of source populations, vectors of dispersal, and demographic changes associated with colonization are often unavailable (Sakai et al, 2001; Lee, 2002) Such information is critical for recently colonized invaders that are increasingly targeted for management actions because this information can be used to prevent future introductions and spread of invasive species

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